Economics for Disaster Prevention and Preparedness Investment in Disaster Risk Management in Europe Makes Economic Sense BACKGROUND REPORT © 2021 International Bank for Reconstruction and Development / The World Bank 1818 H Street NW, Washington DC 20433 Telephone: 202-473-1000; Internet: www.worldbank.org Some rights reserved 1 2 3 4 15 14 13 12 This work is the product of the staff of the World Bank with external contributions. The findings, interpretations, and conclusions expressed in this work do not necessarily reflect the views of the World Bank, its Board of Executive Directors, or the governments they represent. The World Bank does not guarantee the accuracy of the data included in this work. The boundaries, colors, denominations, and other information shown on any map in this work do not imply any judgement on the part of the World Bank concerning the legal status of any territory or the endorsement or acceptance of such boundaries. Nothing herein shall constitute or be considered to be a limitation upon or waiver of the privileges and immunities of the World Bank, all of which are specifically reserved. This publication was produced with the financial support of the European Union. Its contents do not necessarily reflect the views of the European Union. Administration Agreement between the European Commission and the International Bank for Reconstruction and Development concerning the Part II Europe 2020 Programmatic Single-Donor Trust Fund (No.TF073473) (EC Contract No. ECHOSUB/IBRD/2020/827615). Rights and Permissions This work is available under the Creative Commons Attribution 3.0 IGO license (CC BY 3.0 IGO) https://creativecommons.org/licenses/by/3.0/igo/. Under the Creative Commons Attribution license, you are free to copy, distribute, transmit, and adapt this work, including for commercial purposes, under the following conditions: Translations If you create a translation of this work, please add the following disclaimer along with the attribution: This translation is an adaptation of an original work by The World Bank and should not be considered an official World Bank translation. The World Bank shall not be liable for any content or error in this translation. Adaptation If you create an adaptation of this work, please add the following disclaimer along with the attribution: This is an adaptation of an original work by The World Bank. Views and opinions expressed in the adaptation are the sole responsibility of the authors of the adaptation and are not endorsed by The World Bank. The report was completed in April 2021. 2 ACKNOWLEDGEMENTS This report forms part of deliverables under the technical assistance Economic Analysis of Prevention and Preparedness in European Union Member States and Countries under EU Civil Protection Mechanism. This activity is funded by the European Commission’s Directorate General for European Civil Protection and Humanitarian Aid Operations (DG ECHO) through the Annual Work Program of 2020. This report corresponds to the output “Report on the retrospective analysis of the cost and benefits of selected investments aimed at building resilience in the Participating States”. This report was prepared under the guidance and supervision of Christoph Pusch (Practice Manager, Urban, Disaster Risk Management, Resilience and Land, Europe and Central Asia) and Gallina Vincelette (Country Director for the European Union Countries). The report was prepared under leadership of Alanna Simpson (Lead Disaster Risk Management Specialist), Samantha Cook (Senior Financial Sector Specialist) and Zuzana Stanton-Geddes (Disaster Risk Management Specialist). Drafting of the report was coordinated by Solene Dengler (Disaster Risk Management Analyst), and expert inputs were provided by Shaikh Eskander (Senior Environmental Economist), Stuart Fraser (Senior Disaster Risk Management Consultant), Mattia Amadio (Disaster Risk Management Consultant), Daniel Johnson (Heatwave Expert), Zahraa Saiyed (Senior Earthquake Engineer), Josh Macabuag (Senior Disaster Risk Engineer), and Maryia Markhvida (Senior Disaster Risk Management Consultant). Research and analytics support came from Tianyu Zhang (Data Analyst) and Jayne Hoagbin (Research Assistant), with modelling from Domingos Viegas (Professor and Senior Wildfire Expert, Department of Mechanical Engineering, University of Coimbra), Miguel Almeida (Wildfire Expert), the Global Earthquake Model Foundation, and JBA Risk Management. The report was edited by Anne Himmelfarb and designed by Ariane Kascha. The report benefitted from comments and guidance received from Reinhard Mechler (Acting Program Director, Risk and Resilience Department, International Institute for Applied Systems Analysis) and Adam Rose (Research Professor, University of Southern California); Justine Morven Sylvester (Land and Urban Analyst) and from peer review comments from received from Julie Rozenberg, Artessa Saldivar-Sali, and Jun Rentschler. The team would like to express its gratitude for the cooperation and guidance of the representatives of the European Commission and all the stakeholders consulted during the report’s preparation. STATEMENT ON COVID-19 PANDEMIC The COVID-19 pandemic has led to substantial restrictions on travelling and the organization of workshops and face-to face meetings. Despite these limitations, the World Bank team in collaboration with the European Commission and stakeholders has managed to effectively undertake extensive consultations online to collect data and information as a basis for this work. 3 Contents 1. About this Background Report���������������������������������������������������������������������������������������������������������������17 Applied in the Literature and This Report���������������������������������� 18 2. Overview of Methodologies  2.1. The Triple Dividend of Resilience Approach 18 2.2. Methodology applied to analyse case studies 20 2.2.1. Summary of methodological approach 20 2.3. Approach for the identification of case studies and overall analysis 21 2.3.1. Approach for the identification of case studies 21 2.3.2. Summarized results from analysis and case studies 22 3. Case StudiesResults and Analyses by Investments������������������������������������������������������������������������ 28 3.1. Flooding 29 3.1.1. Summary of findings for floods 29 3.1.2. Structural protection against floods 35 3.1.3. Nature-based solutions for flood protection 45 3.1.4. Flood early warning systems 61 3.1.5. Property-level protection (PLP) 68 3.1.6. Overview of BCA for flood risk reduction 72 3.2. Earthquakes 73 3.2.1. Summary of findings for earthquakes 73 3.2.2. Seismic strengthening of buildings and infrastructure 79 3.2.3. Earthquake Early Warning Systems 108 3.2.4. Responder capacity building 111 3.3. Extreme Heat 121 3.3.1. Summary of findings for extreme heat 121 3.3.2. UHI effects 125 3.3.3. Heat early warning systems 130 3.4. Droughts 135 3.4.1. Summary of findings for droughts 135 3.4.2. Irrigation and water provision systems against droughts 138 3.4.3. Early warning and capacity building for drought preparedness 140 3.5. Wildfires 142 3.5.1. Summary of findings for wildfires 142 3.5.2. Wildland-urban interfaces  149 3.5.3. Fuel Management for Wildfire Risk Reduction in forests 161 3.5.4. Decision support tools for climate change adaptation and alerting for wildfire risk reduction 167 3.5.5. Cross-border support, coordination mechanisms, and capacity building for wildfires 178 3.6. Mass movement / landslides 182 3.6.1. Summary of findings for mass movement (landslides) 182 3.6.2. Preventive investments in the resilience of roads 184 3.6.3. Land use planning investments 186 3.6.4. Information and cooperation systems for landslide prevention 187 3.7. Volcanic Eruption 189 3.7.1. Summary of findings for volcanoes 189 3.7.2. Decision making for evacuation in the case of eruptions 190 3.7.3. Infrastructure for evacuation and response 191 4 3.8. Epidemic and Disaster Health Preparedness 192 3.8.1. Summary of findings for epidemic/pandemic risks 192 3.8.2. Return on Investment of National Public Health Programs 194 3.8.3. Equipment for health-related disasters 199 3.9. Oil spills 202 3.9.1. Summary of findings for oil spills 202 3.9.2. Preventive investments in vessels and equipment in coastal areas 203 3.10. Nuclear 207 3.10.1. Summary of findings for nuclear risks 207 3.10.2. Security of nuclear power plants 208 3.10.3. Cleaning up uranium 209 3.11. Chemical 210 3.11.1. Summary of findings for chemical risks 210 3.11.2. Cleaning up hazardous waste 213 3.12. Multi-hazard 217 3.12.1. Summary of findings for multi-hazard risks 217 3.12.2. Rescue and emergency response equipment 218 3.12.3. Multi-hazard early warning systems 219 3.12.4. Participatory methodologies for climate change adaptation 220 3.12.5. Local multi-purpose green investments 221 4. Bibliography��������������������������������������������������������������������������������������������������������������������������������������������� 223 5. Annexes ����������������������������������������������������������������������������������������������������������������������������������������������������� 240 5.1. Annex 1: Key terms and definitions related to methodologies to the estimation of costs and benefits of DRM investments 240 5.2. Annex 2: A step-by-step practitioner report on applying the Triple Dividend BCA 241 5.3. Annex 3: Additional Information on the Methodological Approach 245 5.4. Annex 4: Background Information on case studies 248 5.5. Annex 5: Netherlands results from national assessments and BCAs over a century 254 5.6. Annex 6: Consultations table for case studies 256 5.7. Annex 7: Full overview of final case studies by hazards, sectors, countries and funding 261 5 Figures Figure 1: Triple Dividend of Resilience  20 Figure 2: Process for the selection of case studies  21 Figure 4: Economic loss (€, billions) from considered hazards and climate impact at warming levels for the EU and the United Kingdom (for macro regions)  27 Figure 5: Findings of BCA for floods (BCRs)  31 Figure 6: Findings of BCA for floods (NPVs)  31 Figure 7: Findings of BCA for floods (ERRs)  32 Figure 8: Location of case study and areas estimated to be protected by each project unit of the Machlandamm, with SoP denoted for each unit  37 Figure 9: Simulated reduction in risk per level 3 Administrative unit (AAL) due to protection by the Machlandamm flood protection  38 Figure 10: Elbe River basin districts and potentials for green infrastructures  50 Figure 11: Areas covered by FEWS in Flanders showing ‘flood-prone’ areas (red—susceptible to frequent floods) and ‘floodable’ areas (pink—at risk of less frequent floods)  62 Figure 12: Map of flood-prone areas in Flanders, Belgium in terms of frequency of occurrence  64 Figure 13: Case studies location for modelling of PLP measures: Lignano and Rimini are small towns in Italy located on the North-Adriatic coast  69 Figure 14: Findings of BCA for earthquakes (BCRs)  76 Figure 15: Findings of BCA for earthquakes (NPVs)  76 Figure 16: Findings of BCA for earthquakes (IRRs)  77 Figure 17: Number of buildings per region in Italy  86 Figure 18: Map of seismic countries in the EU by the exposed value of education facilities  92 Figure 19: Percentage reduction in average annual direct losses due to damage for the retrofitted case  93 Figure 20: Costs (investments) and benefits considered for quantitative analysis to provide the BCR. Note that additional costs/benefits are analysed both quantitatively and qualitatively and discussed in the text  112 Figure 21: Costs and benefits further broken down and ranked for each actor. Note that costs and benefits are often associated with different actors  115 Figure 22: Findings of benefit-cost analysis for extreme heat (B/C ratios)  123 Figure 23: Findings of benefit-cost analysis for extreme heat (NPVs)  124 Figure 24: Findings of BCA for extreme heat (ERRs)  124 Figure 25: Conceptual framework of the impacts of drought events and approaches to drought risk prevention  136 Figure 26: Share of drought losses by economic sector (agriculture, energy, water supply, subsidence, and transport) for EU + UK and the four IPCC AR5 European subregions in the baseline (1981–2010) and in 2100  137 Figure 27: Forest fire danger in the present, and under two climate change scenarios, according to two different climate models (1.5°C, 2 °C, and 3°C)  143 Figure 28: Findings of BCA for wildfires (BCRs)  146 Figure 29: Image of a fuel break for WUIs  149 Figure 30: Assessment of housing in Pedrógão Grande for destruction assessment and WUI distances  151 Figure 31: Variation of potential damage (%) as a function of fuel proximity to homes in Pedrógão Grande  151 Figure 32: Fuel management investments and corresponding economic losses to homes in WUI  152 Figure 33: Variation of potential damage (%) as a function of fuel proximity to industries in Oliveira do Hospital  157 6 Figure 34: Fuel management investments and corresponding economic losses to industries in Oliveira do Hospital  158 Figure 35: Fuel-reduced fringes (firebreaks and fuel breaks) provide a fixed safety distance  161 Figure 36: View of a fuel break in a pine stand in Central Portugal (photo of ADAI)  162 Figure 37: Findings CA for mass movement/landslides (BCRs)  183 Figure 38: Map showing the primary network under consideration of this project  185 Figure 39: Findings of BCA for epidemics/pandemics (BCRs)  193 Figure 40: Hospital beds per 1,000 inhabitants by region, 2018  195 Figure 41: Schematic phases of natural hazards’ effects on public health resources  196 Figure 42: Estimated direct and indirect costs related to mental health problems across the EU as a % of GDP, 2015  197 Figure 43: Findings of BCA for Oil Spills (BCR)  203 Figure 44: EMSA’s Operational Oil Spill Response Services  204 Figure 45: Findings of BCA for chemical risk (BCR)  211 Figure 46: Findings of BCA for chemical risk (NPV)  212 Figure 47: Findings of BCA for chemical risk (IRR)  212 Figure 48: Benefits of NBS in urban environments  222 Figure 49: Overall cumulative association between temperature and mortality  251 Figure 50: Flow chart showing Albania’s climate-resilient roads’ project approach for parts 1 and 2  253 Tables Table 1: Overview of Case studies Reviewed as part of Background Research23 Table 2: Overview of data and information sources for flood analysis30 Table 3: Risk reduction represented by change in AAL due to the Machlandamm flood protection at key settlements in the case study area38 Table 4: BCR for Machlandamm per dividend, assuming a 30-year period of operation39 Table 5: Detailed breakdown of benefits for Machlanddamm by dividend39 Table 6: BCR for river flood protection for Poland’s Odra river basin per dividend (all values in 2006 Euro values at the exchange rate of 1€ = 4 PLN).41 Table 7: Detailed breakdown of Odra River benefits by dividend41 Table 8: Comparison of costs for major investment projects in storm surge barriers in Europe44 Table 9: Estimated costs and benefits from the first economic appraisal of Eddleston Water NFM47 Table 10: Impact of NFM measures in the Eddleston Water catchment, on property damage in Eddleston village and Peebles town47 Table 11: Estimated benefits and costs for INTERREG project in Eddleston, Scotland per dividend, based on a 30-year timescale 48 Table 12: Estimated benefits and costs for INTERREG project in Eddleston, Scotland per dividend, based on a 100-year timescale49 Table 13: Green, Grey and Hybrid measures for flood prevention in Elbe, Germany 51 Table 14: Cost-effectiveness of infrastructure options for the Elbe: NPV of options52 Table 15: Benefits and costs from Chimney Meadows floodplain restoration over a 30 years period (2023-2052) applying a discount rate of 1.5% 54 Table 16: Overview of costs and benefits of all plan alternatives (€, millions in 2004 prices) for optimal Sigma Plan up to 210058 Table 17: People and households affected by EWS benefits (model estimates)63 Table 18: Overall risk reduction (AAL) thanks to EWS for 3 key assumptions (in millions €)63 Table 19: BCR of implementing EWS in Flanders by dividend, over 30 years (Future benefits and costs discounted by 3.5%/year)64 Table 20: Unitary costs of PLP measures as estimated for the Umbria case study. Adapted from ECHO-SUB-2014-69446970 7 Table 21: Summary of results for PLP scenario simulation compared to baseline. Both locations show a reduction in annual expected losses close to 3.5 percent for PLP measure implementation with percent uptake70 Table 22: BCR for PLP in NE Italy per dividend (30 years lifespan, benefits discount rate 3.5%)71 Table 23: Overview of data and information sources for earthquake analysis74 Table 24: Types of buildings included in Italy’s seismic retrofitting by sector84 Table 25: Methodologies of benefit estimations85 Table 26: Number of building interventions conducted by sector and type of interventions87 Table 27: Investment into public buildings87 Table 28: Investment into private mixed-use buildings89 Table 29: Number of schools and universities considered in the case study with associated national database websites 91 Table 30: Estimated retrofitting cost ratios from multiple sources93 Table 31: Key parameters of existing educational buildings94 Table 32: Energy efficiency measures description95 Table 33: Primary energy savings95 Table 34: CO2 savings96 Table 35: Energy costs and conversion factors96 Table 36: ‘Light/medium’ renovation monetary results 97 Table 37: ‘Deep’ renovation monetary results  97 Table 38: BCA for schools98 Table 39: BCA for universities100 Table 40: BCR of strengthening disaster risk management in Romania (in million €)104 Table 41: BCR of improving resilience and emergency response in Romania (in million €)104 Table 42: BCR of strengthening preparedness and critical emergency infrastructure105 Table 43: Comparison of BCA outputs for case studies in Romania105 Table 44: BCR of Turkey school infrastructure investment per dividend107 Table 45: BCR of implementing EEWS in Bucharest, Romania (in million €)110 Table 46: Detailed breakdown of implementing EEWS in Bucharest, Romania (in million €)110 Table 47: Capacity-building BCA for November 2019 Albania Earthquake116 Table 48: Detailed breakdown of BCA items for case study: November 2019 Albania Earthquake116 Table 49: Capacity-Building BCA for March 2020 Croatia Earthquake 118 Table 50: Breakdown of BCA items for the case study: March 2020 Croatia Earthquake118 Table 51: Overview of data and information sources for extreme heat analysis122 Table 52: Costs and benefits of green and white solutions to reduce UHI effect (in hundred millions €)129 Table 53: BCR for HEWS by dividends133 Table 54: Ranges of parameters used in Monte Carlo simulation following triangular distributions134 Table 55: Overview of data and information sources for droughts analysis138 Table 56: Fitted impact model to determine economic efficiency of emergency drought wells140 Table 57: Overview of data and information sources for wildfires analysis144 Table 58: CBR of WUIs in Pedrógão Grande (in million €)154 Table 59: Expanded triple dividend BCR calculation of WUIs in Pedrógão Grande (in million €)154 Table 60: Industrial facilities affected by industry156 Table 61: BCR of WUI management to industries in Oliveira do Hospital (in million €)160 Table 62: Expanded Triple Dividend Cost Benefit Ratio Calculation of WUI management to industries in Oliveira do Hospital (in million €)160 Table 63: Estimation of effectiveness of fuel breaks with regard to the hazard level and degree of effective fire suppression163 Table 64: BCR of fuel management for wildfire risk reduction in the Central Region, Portugal (in million €)166 Table 65: Expanded triple dividend BCR calculation of fuel management for wildfire risk reduction in the Central Region, Portugal (in 100000 €)166 Table 66: BCR of climate change adaptation decision support tool in Austria (in 100000 €)169 8 Table 67: Expanded triple dividend BCR calculation for the climate change adaptation decision support tool in Austria (in 100000 €)169 Table 68: Probabilities of injuries with risk reduction actions taken in moderate to extreme hazard fires172 Table 69: Probabilities of fatalities with risk reduction actions taken in moderate to extreme hazard fires172 Table 70: BCR calculation of alerting and preparedness for fires in Portugal (in million €)173 Table 71: Expanded triple dividend BCR calculation for alerting and preparedness for fires in Portugal (in million €)173 Table 72: Probabilities of injuries with risk reduction actions taken in moderate to extreme hazard fires176 Table 73: Probabilities of fatalities with risk reduction actions taken in moderate to extreme hazard fires176 Table 74: BCR calculation of alerting and preparedness for fires in Greece (in million €)177 Table 75: Expanded triple dividend BCR calculation of alerting and preparedness in Greece (in million €)177 Table 76: BCR calculation of the SPITFIRE project (in million €)180 Table 77: Expanded triple dividend BCR calculation for the SPITFIRE project (in million €)180 Table 78: Overview of data and information sources for mass movement / landslides analysis182 Table 79: BCR for landslide measures implemented by corridor186 Table 80: Overview of data and information sources for epidemics/pandemics analysis193 Table 81: Cost of PPE supplies in the United States pre-COVID19 and during COVID-19199 Table 83: Socioeconomic and Environmental Base Per-Gallon Costs for Oil Spills205 Table 84: Overview of data and information sources for chemical analysis211 Table 85: BCR of cleaning up hazardous waste in Latvia (in million €)215 Table 86: Expanded triple dividend BCR calculation for cleaning up hazardous waste in Latvia (in million €)216 Table 87: Overview of data and information sources for multi-hazard analysis217 Table 88: Value of various participatory climate adaption measures221 Table 89: Highlights of one century of BCAs for Dutch flood risk management: conclusions and applications254 Table 90: Highlights of one century of BCA’s for Dutch flood risk management: benefits and uncertainty estimations255 Boxes Box 1: Overview of other investments in structural flood protection across Europe45 Box 2: Structural protection for specific assets in the transport sector46 Box 3: Additional examples of investments in Floodplain and Wetland restoration58 Box 4: NBS for flood risk reduction in coastal and tidal areas62 Box 5: Investments in urban infrastructure to reduce flood risks63 Box 6: Varied investments in EWS and capacity building for flood response across Europe70 Box 7: Cultural heritage protection and seismic strengthening in Italy83 Box 8: Climate-proofing social housing126 Box 9: Investing in improving water security infrastructure and supply system139 Box 10: Investing in Early Warning and preparedness for Droughts141 Box 11: Investments in capacity for enhanced wildfire response across Europe181 Box 12: Cost-effectiveness of landslide prevention vs. response investments187 Box 13: Investments in information systems and cooperation mechanisms for landslide prevention188 Box 14: Investments in preparedness for volcanic eruptions191 Box 15: Evacuation routes in volcanic areas191 Box 16: Investments in the security of nuclear power plants across Europe208 Box 17: The use of digital tools in the early warning of disasters219 Box 18: Examples of investments in urban blue green infrastructure222 9 GLOSSARY OF KEY TERMS human, material, economic, or environmental effects that require immediate emergency response to satisfy adaptation: Adjustments or changes in economic, critical human needs and that may require external social, or environmental approaches in response to the support for recovery. effect of present or future climate change. disaster risk management (DRM): Processes for avoided losses (first dividend of the triple dividend designing, implementing, and evaluating strategies, approach): The short- and long-term damages and policies, and measures to improve the understanding losses prevented or reduced by a DRM investment of disaster risk, foster disaster risk reduction and when a disaster occurs. transfer, and promote continuous improvement in disaster preparedness, response, and recovery co-benefits (third dividend of the triple dividend practices, all with the explicit purpose of increasing approach): The social, environmental, and economic human security, well-being, quality of life, and benefits generated by a DRM investment, which is sustainable development. independent of the occurrence of disasters. disaster risk reduction (DRR): Both a policy goal and benefit-cost analysis (BCA): Process used to identify, the strategic and instrumental measures employed for measure, and analyse the benefits of a project, anticipating future disaster risk. DRR reduces existing programme, or decision versus the costs associated exposure, hazard, or vulnerability and improves with it. resilience. benefit-cost ratio (BCR): Ratio used in BCA to discount rate: Rate of return used to discount future summarize the relationship between overall relative cash flows back to their present value. Financial benefits and costs of a project. A BCR lower than 1 discount rates are the interest rates used to calculate means that the project’s net benefits could be negative, the present value of future cash flows from a project or i.e., benefits are lower than costs. investment. Social discount rates indicate a society’s average valuation of future versus present impacts of damage: Total or partial destruction of physical assets interventions (benefits and costs). A high discount rate existing in the affected area. Damage occurs during indicates a lower valuation of the future and a and after the disasters and is measured in physical preference for the present, which particularly in the units (that is, square meters of housing, kilometres of context of climate change also has implications for roads, and so on). intergenerational equity. direct and indirect benefits/costs: Benefits/costs early warning system (EWS): An integrated tool of either directly or indirectly associated with the impact hazard monitoring, forecasting and alert, that enables of the project/program/decision. An example of a individuals, communities, governments, businesses direct benefit is the prevention of asset losses or and others to take timely actions to reduce disaster enhancement of environmental value due to a flood risks in advance of and during hazardous events. In prevention measure; a direct cost is the cost of the terms of flood interventions, EWS refers to interventions flood prevention measure. An example of an indirect that rely on meteorological forecasts of intense or benefit is the productivity losses prevented given the sustained rainfall to identify locations with forecast flood measure, while an indirect cost is the increase in flooding. EWS comprise technical components to prices in the area leading to displacement and loss of detect rainfall in advance and estimate flood welfare/well-being of certain populations. conditions, and to disseminate warnings to affected communities, but also human/behavioural components disaster risk: The combination of the probability of an to take decisions to activate warnings and to respond event and its negative consequences. The likelihood to warnings. over a specified time period of severe alterations in the normal functioning of a community or a society due to exposure: The situation of people, infrastructure, hazardous physical events interacting with vulnerable housing, production capacities and other tangible social conditions, leading to widespread adverse human assets located in hazard-prone areas. Exposure 10 includes the number of people or types of assets in an and outflows associated with a project/program/ area. These can be combined with the specific decision, discount all these flows to the present day, vulnerability and capacity of the exposed elements to and add them together. A positive NPV means that, any particular hazard to estimate the quantitative risks after accounting for the time value of monetary flows, associated with that hazard in the area of interest. the project/program/decision could yield net benefits. green infrastructure: Sustainable, nature-based losses: Quantifiable damages of disasters that can be Infrastructure that makes use of natural processes translated into monetary terms. A distinction can be and ecosystem services for functional purposes, such made between direct disaster losses, which refer to as disaster risk reduction. Such infrastructure usually directly quantifiable losses (number of people killed, yields risk reduction benefits as well as social and damages to buildings, infrastructure or natural environmental effects. resources) and indirect losses, which refer to indirectly quantifiable losses (declines in output or revenue, grey infrastructure: Structural, human-engineered impact on wellbeing, disruptions to flow of goods and infrastructure for flood or other disaster risk services in an economy). management, which includes both static and active elements and which is usually built with materials like property level protection (PLP): A type of flood steel and concrete. intervention, which comprises protection of individual properties through small-scale interventions such as hazard: The potential occurrence of a natural or demountable flood walls and gates at doorways, raising human-induced physical event that may cause loss of the ground floor level or elevation of door thresholds. life, injury, or other health impacts, as well as damage and loss to property, infrastructure, livelihoods, service resilience: The ability of a system and its component provision, and environmental resources. parts to anticipate, absorb, accommodate, or recover from the effects of a hazardous event in a timely and moral hazard: Refers to a situation when rational efficient manner, including through ensuring the individuals have incentives to change their exposure to preservation, restoration, or improvement of its risk when they do not bear the full cost of that risk essential basic structures and functions. exposure. For example, a full health insurance coverage may discourage an individual to take care of sensitivity analysis: analysis that determines and her physical state since the monetary burden of any showcases how results change when assumptions, healthcare services will be borne by the insurance parameters, or variables of an analysis are changed. company. structural protection: A type of flood intervention, nature-based solutions (NBS) or natural floodplain which comprises engineered or ‘hard’ defences with management (NFM): A type of flood intervention, are further classified as permanent engineered which include interventions such as floodplain, dune, structures: levees, dikes, walls, dams flood gates and or wetland restoration; planting of green infrastructure, temporary or de-mountable infrastructure such as for example, hedgerows, woodlands, and natural temporary barriers. grasslands; and blue elements such as pools, ponds buffer basins or water courses. Commonly, several triple dividend benefit-cost analysis: A systematic elements are combined in a management plan and are approach that evaluate different project alternatives to often considered as blue-green infrastructure, with the determine the best option that generates the most selection determined by the local environment and welfare for the society by comparing the alternatives’ prevalent flood mechanisms. social and economic costs to the benefits, which consist of three dividends: 1) avoided losses and saved net present value (NPV): Difference between the lives, 2) unlocked economic potentials, and 3) the present value of monetary inflows and the present social, environmental, and economic co-benefits of value of cash outflows over a period time. The idea the project. behind the NPV is to project all future monetary inflows 11 unlocked economic potentials (second dividend of value of statistical life (VSL): The marginal rate of the triple dividend approach): Innovations, entre- substitution between income (wealth) and mortality preneurship, investments, and other economic risk, i.e., how much individuals are willing to pay on activities stimulated due to the reduction in background average to reduce the risk of death. It therefore risks related to disasters through DRM investments. indicates not the value of an actual life but the value of This economic development potential is independent marginal changes in the likelihood of death. of the occurrence of disasters. vulnerability: The characteristics and circumstances value of a life year: A concept derived from the of the built environment and communities that make willingness to pay for increasing life expectancy by one them susceptible to damaging impacts (or human additional year. This measure is considered more vulnerability). Vulnerability factors include building appropriate for disasters that mostly displace mortality construction type, socio-economic context, and so on. (i.e., affect certain age groups) rather than mostly causing premature deaths. Theoretically, measurements of actual changes in life expectancy would be the exact measure to consider. 12 ACRONYMS AND ABBREVIATIONS AAL Average Annual Loss ADAI Association for the Development of Industrial Aerodynamics AEP Annual Exceedance Probability AGIF Agency for the Integrated Management of Wildfires ARA Albanian Road Authority BAP Biodiversity Action Plan BASE Bottom-Up Climate Adaptation Strategies Towards a Sustainable Europe BCA Benefit-Cost Analysis BCR Benefit-Cost Ratio C3S Copernicus Climate Change Service CCDR-C Central Regional Coordination and Development Commission CFA Country Fire Authority CTCN Climate Technology Centre and Network DACC Damage Assessment Coordination Centre DACEA Danube Cross-border System for Earthquake Alerts DALY Disability-adjusted Life Year DEFRA Department for Environment, Food, and Rural Affairs DG Directorate-General DG ECHO Directorate-General for European Civil Protection and Humanitarian Aid Operations DiD Difference-in-Difference DPPI Disaster Preparedness and Prevention Initiative DRM Disaster Risk Management DRR Disaster Risk Reduction DSS Decision Support Systems EAEE European Association for Earthquake Engineering EC European Commission EDO European Drought Observatory EEA European Environment Agency EEWS Earthquake Early Warning System(s) EFAS European Flood Awareness System EFFIS European Forest Fire Information System EMS Emergency Medical Services EMSA European Maritime Safety Agency EPB earthquake-prone buildings ERCC Emergency Response Coordination Centre ERDF European Regional Development Fund 13 ESHM13 2013 European Seismic Hazard Model ESPON European Spatial Planning Observation Network EU European Union EUCPT European Union Civil Protection Team EWS Early Warning System(s) FEMA Federal Emergency Management Authority FEWS Flood Early Warning System(s) GDACS Global Disaster Alert and Coordination System GDP Gross Domestic Product GFDRR Global Facility for Disaster Reduction and Recovery GHRF Commission on a Global Health Risk Framework for the Future Commission GNI Gross National Income GPSS Global Program for Safer Schools GRP Gross Regional Product GRT Gross Register Tonnage HEWS Heat Early Warning System(s) HWWS Heatwave Warning Systems IAEA International Atomic Energy Agency ICT Information and Communication Technology IMPRESSIONS Impacts and Risks from High-End Scenarios: Strategies for Innovative Solutions IPCC Intergovernmental Panel on Climate Change IRR Internal Rate of Return ISMEP Istanbul Seismic Risk Mitigation and Emergency Preparedness JPA Joint Procurement Agreement JRC Joint Research Centre LCE Limit Condition for Emergency LSM Landslide Susceptibility Mapping MATRIX Multi-Hazard and Multi-risk Assessment Methods for Europe MCA Multi-criteria Analysis MCE Multi-criteria Evaluation MoNE Ministry of National Education MS Member State(s) MSP Multisector Partnership NBS Nature-based Solution(s) NIBS National Institute of Building Sciences NIEP National Institute for Earth Physics NPV Net Present Value 14 OCC Opportunity Cost of Capital OECD Organisation for Economic Co-operation and Development ONERC National Observatory for the Impacts of Global Warming (Observatoire National sur les Effets du Réchauffement Climatique) OSD Office of the Secretary of Defence PAD Project Appraisal Document PBCA Participatory BCA PDC Permanent Drought Commission PESETA Projection of Economic Impacts of Climate Change in Sectors of the European Union-based on Bottom-up Analysis PFAS Per- and Polyfluoroalkyl Substances PGA Peak Ground Acceleration PLP Property-level Protection PML Probable Maximum Loss PPE Personal Protective Equipment PS Participating State(s) PTSD Post-traumatic Stress Disorder PWWS Philadelphia Hot Weather-Health Watch/Warning System QALY Quality-adjusted Life Years R&D Research and Development RDNA Rapid Disaster Needs Assessment RESIN Climate Resilient Cities and Infrastructures RISE Real-time Earthquake Risk Reduction for a Resilient Europe ROI Return on Investment SDG Sustainable Development Goal SEA System of Earthquakes Alert SEAP Sustainable Energy Action Plan SEPA Scottish Environment Protection Agency SERA Seismology and Earthquake Engineering Research Infrastructure Alliance for Europe SHARE Seismic Hazard Harmonization in Europe SHOPP Society for Healthcare Organization Procurement Professionals SoP Standard of Protection SuDS Sustainable Urban Drainage System TD BCA Triple Dividend Benefit-Cost Analysis UCC USAR Coordination Cell UCPM Union Civil Protection Mechanism UHI Urban Heat Island UN United Nations  15 UNDAC UN Disaster Assessment and Coordination UNFCC United Nations Framework Convention on Climate Change USAR Urban Search and Rescue USGS United States Geological Survey VAT Value Added Tax VOLY Value of Life Year VOSOCC Virtual On-site Operations and Coordination Centre VSL Value of a Statistical Life WFD Water Framework Directive WTA Willingness to Accept WTP Willingness to Pay WUI Wildland-Urban Interface Note: Currencies have been converted throughout the document to euro values. Wherever the original values were in other currencies, this has been indicated in footnotes. The currency exchange rates used in this document come from the Eurostat database (European Union, 2021). All dollar amounts are US dollars unless otherwise indicated. As the results are based on analysis that is based on inherent uncer- tainty, results from new analysis under this study or detailed results from external case studies are presented as rounded numbers (i.e., to a maximum of two decimal places) and/or as ranges.  16 1. About this Background Report This Background Report accompanies a summary Climate Change and (b) summaries of all the case report, which forms part of the World Bank’s technical studies featured in this report. It first provides a assistance project undertaken with the European detailed description of the approaches for the selection Commission’s Directorate-General for European Civil of case studies and an overview of all the case studies Protection and Humanitarian Aid Operations (DG featured in the report, which can be categorized into ECHO) and financed under the Union Civil Protection three types based on the analysis undertaken: full Mechanism (UCPM) Annual Work Programme 2020. quantitative analysis, partial quantitative analysis This report is the output produced under Component 1 based on the literature, and qualitative analysis. “Retrospective analysis of the costs and benefits of Then it presents selected results from the analysis, selected disaster risk management (DRM) focusing on main pieces of analysis and comparing investments”, with the aim to showcase the benefits of results in light of the literature. Sections start with an investing in the prevention of disaster risks. This introduction to hazard risks worldwide in the EU, background paper covers (a) methodological include a summary of findings and then present approaches for the economic assessment of selected detailed analysis for illustration. investments for Disaster Risk Management and About this Background Report  17 2. Overview of Methodologies  Applied in the Literature and This Report This section provides an overview of the Bank and Overseas Development Institute (ODI) methodological approaches and applications to Triple Dividend of Resilience approach for DRM calculate benefits and costs of investments used in investments. An overview of important technical terms this report. The objective is to show the usefulness of is defined in Annex 1, while alternative methodologies using typical BCA procedures and applying the World that can be used is included in Annex 3. 2.1. The Triple Dividend of Resilience Approach The ‘triple dividend of resilience’ approach (Tanner, et Dividend 1, saving lives and reducing losses, relies on al., 2015) is a comprehensive methodology for quantifying the impact of resilience measures through analysing the net benefits of DRM investments. It risk analysis with and without the resilience measures identifies three types of benefits (see Figure 1): (1) (Mechler, 2016). Risk analysis provides the estimate of avoiding losses and saving lives during a disaster; (2) severity and frequency of impacts on people, unlocking economic potentials as a result of stimulated communities, and their structural and infrastructure innovations and bolstered economic activities due to assets (Ghesquiere, et al., 2006) and the reduction in the reduction in background risks related to disasters; those impacts due to a particular set of resilience and (3) generating social, environmental, and measures being implemented. Disaster risk (or economic co-benefits of DRM investments even in the catastrophe) modelling approaches estimate risk in absence of a disaster. terms of casualties and direct and indirect economic losses by modelling the interaction of hazard, exposure, World Bank-financed projects must include a BCA, and vulnerability (World Bank, GFDRR, 2014). For which includes a sensitivity analysis and calculation of example, they can be used to adjust the vulnerability of return on investments (ROIs), among others building stock to represent the impact on the risk of (Independent Evaluation Group, 2010). Due to the improved building codes or retrofit programmes. The broader benefits that the ‘triple dividend of resilience’ dividend can be estimated using scenario events or approach considers, there has been an increase in probabilistically to estimate the impact of the projects that include this methodology, such as a intervention on risk metrics such as AAL or extreme series of investment projects supported in Romania events. (World Bank, 2018a; 2019a; 2019c) and Turkey’s Disaster Risk Management in Schools Project, as a In terms of dividend 2, a number of research projects part of the Global Safe School Program (World Bank, have attempted to estimate in practice the wider 2019d), for example. economic benefits from DRM investments. Two studies (Erma, et al., 2020) showed the wider economic An advantage of the triple dividend approach is that it impacts of investments or policies in DRR from reconciles perspectives from the humanitarian, different perspectives. The first report (Madajewicz, et environmental, and economic fields. However, al., 2013) analysed a rural program to provide risk estimations of the second dividend have generally management support to farmers in Ethiopia and been complicated, due to a combination of factors showed that risk management tools such as weather- such as missing data, lack of appropriate and feasible indexed insurance increased farmers’ savings (an methodologies particularly within short analytical time important reserve in case of floods or droughts) and frames for project preparation and appraisal, and lack their investments in productive assets. These reports of expertise to undertake that part of the economic show that complementary soft investments for analysis (Mechler & Hochrainer-Stigler, 2019). preparedness alongside hard infrastructure measures can have a substantial impact on the realization of a Overview of Methodologies 18 positive second dividend. broadening the range of substitution possibilities, relocating businesses, or effecting technological Other factors are essential to consider when aiming to change. Moreover, all these resilience tactics can have measure benefits in terms of reduced flow losses. A lasting effects through learning or improvements in the significant reduction in flow losses - such as losses in functioning of businesses, households, or other GDP and employment, as opposed to property institutions to increase the capacity to cope with future damage - can be obtained after disaster strikes by disasters. All of these are short-run tactics that differ various types of resilience tactics related to coping from long-run climate adaptation. An example of the with a disruption of critical inputs such as utility difference relates to population movements with lifelines, critical materials, and workers. Rose (2007) regard to disasters and climate change: short-run refers to the use of such tactics as “resilience” to tactics include population evacuation either before or distinguish them from ex-ante risk reduction once the disaster has struck, which is typically measures, typically referred to as “mitigation”. Inherent temporary; for climate adaptation, as in the response resilience refers to the capabilities intrinsic to an to sea-level rise, the tactic would likely be permanent individual business, household, or institution, or the population migration. In short, informing economic economy as a whole; it can also refer to the build-up of actors of the risk may lead to them individually investing resilience capacity by pre-positioning this capability in enhanced preparedness, which will have additional for implementation after a disaster strikes. Examples positive economic effects regardless of whether a of intrinsic capabilities include resilience “tactics” disaster will strike. such as substitution (use of dual-fired boilers for electricity generation, the ability to substitute bottled In terms of dividend 3, a few studies attempted to or trucked water for piped water at the micro level, or quantify some environmental or ecosystem co- the workings of the price system to provide signals of benefits. Ideal methodology in such quantification changes in resource values for optimal allocation at requires adopting a production function method of the market or macroeconomic level) or the ability to valuing ecosystem good and services (Barbier, 2009). bring excess capacity online when regular capacity is (Barbier, 2007) considered three broad categories of damaged. Examples of pre-positioning include the benefits of ecosystem services: ‘goods’ (for example, purchase of portable electricity generators or products obtained from ecosystems, such as resource stockpiling of critical materials. harvests, water, and genetic material); ‘services’ (for example, recreational and tourism benefits or certain The concept of adaptive resilience (Rose, 2016) is also ecological regulatory functions, such as water essential to consider for estimating dividend 2. purification, climate regulation, and erosion control); Adaptive resilience refers to improvisations after the and cultural benefits (for example, spiritual and disaster has struck, such as identifying conservation religious and heritage). A table in Annex 3 lists opportunities not previously thought possible, potential economic benefits of ecosystem services. Overview of Methodologies 19 Figure 1: Triple Dividend of Resilience nd and 3rd Disaster risk management Avoiding damages and losses from disasters, by: Benefits when • Saving lives and reducing people affected disaster strikes (DRM) • Reducing damages to infrastructure and other assets • Reducing losses to economic flows investments Economic Potential Stimulating economic activity due to reduced disaster risk, by increasing: • Business and capital investment • Household and agricultural productivity • Land value from protective infrastructure • Fiscal stability and access to credit Benefits Regardless of disasters DRM investments can serve multiple uses which can be captured as co-benefits such as: Costs and • Eco-system services potential • Transportation uses 15 • Agricultural productivity gains adverse effects of DRM measures Source: (Tanner, et al., 2015) 2.2. Methodology applied to analyse case studies This report contains quantitative and qualitative 2.2.1. SUMMARY OF METHODOLOGICAL analyses of 74 case studies for floods, earthquakes, APPROACH wildfires, extreme heat, droughts, wildfires, landslides, volcanoes, storms, epidemics, oil spills, nuclear, The World Bank has applied the ‘triple dividend of chemical, and biological hazards. These case studies resilience’ approach while keeping a certain represent DRM efforts across 24 countries as well as flexibility. The specific methodologies and modelling regional and continent-wide efforts. Furthermore, approaches were adapted to various types of disaster these cases touch on at least one of these important risk investments and existing results of various BCAs sectors: housing, emergency response and have also been presented. equipment, early warning, health, education, transportation, agriculture and forestry, cultural Although there have been variabilities in analysis of heritage and recreation, commerce and industry investments, a similar process has generally been lifeline, and utility systems (for example, water and undertaken that has the following features: utility). With the information collected online, through phone interviews with leading experts and • Considered the risk profile across UCPM countries. practitioners as well as questionnaires sent via email, This was undertaken to better understand benefits our team applied the World Bank’s triple dividend of and costs and the limitation and comparability of resilience approach as much as possible to analyse available data. the well-rounded economic and non-economic costs and benefits of DRM investments and policy implementations. Overview of Methodologies 20 • Collected and summarized data on selected lifelines, communications, energy and water. investments. Information was collected on investments in prevention and preparedness as • Applied the triple dividend approach to well as DRR, including among others broad figures demonstrate the benefits of DRR investments. The on national funds and EU programs, intervention first dividend was estimated by conducting type and description, anticipated or actual cost, scenario impact models for cases with detailed number of beneficiaries, feasibility studies, any BCA data being available to simulate the interventions that was undertaken, and how risk is considered and their impacts. Examples where this might be (availability of data for future scenarios and so on). simulated include the construction of coastal and Further information was collected through extensive inland flood protection, relocation of assets and consultations. population, restriction of land use, and strengthening/hardening of existing buildings and • Reviewed case studies related to specific hazards infrastructure. The calculation of the second and and sectors. These encompassed hazards such as third dividend depended on the availability of data. flooding, earthquake, extreme heat, droughts, “The analysis has built on a number of parameters, wildfires, landslides, volcanoes, storms, epidemics, specific methodologies and assumptions. The oil spills, nuclear, chemical and biological as well as process of calculation of the BCAs is described in sectors such as housing, transport, education, detail in Annex 2. health, emergency response, early warning and 2.3. Approach for the identification of case studies and overall analysis 2.3.1. APPROACH FOR THE stakeholders) and methodological feasibility to IDENTIFICATION OF CASE STUDIES undertake at least a partial triple dividend BCA in a quantitative manner or qualitatively describing the The identification and selection of case studies was benefits and costs, and (c) quantitative analysis with undertaken through a three-step approach (Figure 2). risk modelling for a selected number of case studies The three steps were (a) identification of case studies and partial or qualitative analysis for the others as well for the focus of the analysis, (b) categorization of case as presenting of results from the literature and World studies based on data availability (collected through Bank projects. online research and extensive consultations with Figure 2: Process for the selection of case studies • 100 case studies General • 74 case studies Identification of case studies Final selection of case studies • 17 case studies (via online research and discussions with the Analysis with quantitative European Commission) own analysis (17), (via data research, extensive (partial) quantitative based consultations, and on the literature (13), consideration of methodologies) and qualitative analysis (44) Source: World Bank analysis Overview of Methodologies 21 Following an initial research and review of existing to be interesting investments that could be suitable for case studies, approximately 100 case studies from a further analysis. An overview of case studies with European context have been selected. These case detailed information and an illustration of coverage by studies were considered for a preliminary analysis and hazards, countries, sectors, and type of methodology presented in the inception report delivered in June is included in Annex 7. 2020. The case studies included a mix of relevant sectors (housing, education, transport, health, In a third step, analysis was undertaken for the case emergency response, early warning and lifelines, studies and relevant international best practices were communication/ICT, energy, and water) and hazards presented. A summary of results of the case studies that are either natural (floods, droughts, earthquake, and analysis is included in Part 3 of the report, wildfires, landslides, and volcanic eruptions) or according to various European Commission priorities, technological (oil spills, chemical pollution, biological, by hazards and types of investments. The international radiological, or nuclear disasters). The case studies case studies (among others New Zealand, Japan, the focused on MS/PS of the UCPM; were funded from United States, and Australia) were mostly selected as national funds, at least partly by EU funds or by per their suitability for transferability of experiences to international financial institutions; and were major the EU context and lessons learned from making the projects1 that were aimed predominantly at reducing economic case for investing in DRR. disaster risk, increasing prevention and preparedness. These case studies were categorized into thematic Determining an average value on a hazard- or sector- areas and hazards and the depth of data and specific BCA was not possible due to non-repre­ information available for BCA assessed, including sentative samples of investments and non-uniform through extensive consultations (see Annex 6). For all methods. An important consideration for the analysis case studies, background information on disaster has been the variety of methodologies and levels of vulnerability of the country or area, the project funding, modelling or risk assessments applied given the achieved or expected impacts as well as cost- multitude of hazards, sectors and information/data effectiveness, and/or triple dividend BCA were availabilities. For example, some of the case studies are presented. analysed on a scenario basis and others on the basis of AALs. For some of the case studies where a concrete In a second step, case studies were categorized and investment could not be found (that is, retrofitting of reviewed according to their suitability for further schools at European scale), a hypo­ thetical scenario analysis, and 74 were included in the final selection.2 was modelled. Moreover, an insufficient number of These case studies were reorganized by types of case studies to have a representative sample investments covering various hazards and sectors and undermined the possibility of inferring representative 17 case studies were considered for full quantitative average BCRs for investments. analysis including own risk modelling and/or assessment (3 on floods, 4 on earthquakes, 2 on 2.3.2. SUMMARIZED RESULTS FROM extreme heat, 7 on wildfires and 1 on chemical; ANALYSIS AND CASE STUDIES included in those are 3 on early warning). Another 13 case studies were presented based on at least partial A brief summary of the typology, coverage and main quantitative analysis undertaken in the literature, information on the case studies is included below including for World Bank project appraisal or (see Table 1). A considerable effort has been evaluations (5 on floods, 2 on earthquakes, 1 on undertaken to achieve a balanced coverage of hazards, droughts, 1 on landslides, 2 on epidemics, 1 on oil types of investments and countries. However, the lack spills and 1 on multi-hazard). The remaining 44 case of data and information, available methodologies to studies were described qualitatively as insufficient undertake risk assessments and BCA, or possibility to information and data were found to be able to present present qualitative information conforming to the results according to triple dividend BCA or at least Triple Dividend Framework constrained the depth and somehow quantitatively, but these were still considered breadth of coverage. This was expected, as a major 1 Major projects in the programming period 2014–2020 are defined as operations where eligible costs exceed €50 million or €75 million in the case where they contribute to the thematic objective under Article 9(7) (Article 100, Regulation 1303/2013 from the European Commission). 2 The number is higher than just based on the original list of case studies considered, as some case studies were added in the process based on further recommendations from stakeholders. Overview of Methodologies 22 focus of key EU investments in the past decade has Danube region - emergency response and been, for example, on flood risk prevention. equipment - drought - qualitative analysis. In terms of coverage of countries, a good balance has • ‘Union civil protection knowledge network in been achieved in terms of development/income earthquake’: Albania and Croatia - emergency levels3, geographical locations, and disaster risks response and equipment - earthquake - commonly faced in subregions. Figure 3 shows quantitative own analysis. countries in Europe and beyond as well as the coverage of case studies by hazards, sectors, and • ‘The case of pandemic preparedness’: Across type of analysis as well as information on countries Europe - epidemic - health - partial quantitative/ status of participation to the UCPM. Figure 4 also literature. shows that the case studies include close to all countries that are expected to suffer from high • ‘Rate of return on health investments’: Across welfare losses due to climate change (Feyen, et al., Europe - epidemic - health - partial quantitative/ 2020). literature. The following case studies are not included in the map • ‘Schools in seismic countries across Europe’: (Figure 3) because they were regional investments Across Europe - earthquake - education - across Europe or undertaken in two or more non- quantitative own analysis. neighbouring countries involved. • ‘European flood awareness system’: Across Europe • ‘Mapping landslide hazards’: Croatia/Bosnia and - flood - early warning - qualitative. Herzegovina/Montenegro - emergency response and equipment - landslide - qualitative. • ‘URBAN GreenUP’: Across Europe - all hazards - housing and public buildings; recreation - • ‘Early warning and preparedness for droughts’: qualitative. Table 1: Overview of Case studies Reviewed as part of Background Research NATURAL HAZARDS # CASE COUNTRIES (INCL. CROSS- TYPES OF HAZARD  SECTORS COVERED STUDIES BORDER AND AREAS) INVESTMENTS 28 United Kingdom, Portugal, Structural protection (8); Industry, early warning, water, Spain, Greece, Cyprus, NBS (14); early warning (5); agriculture, housing and public Poland, Netherlands, PLP (1) buildings, response and Austria, Croatia, Serbia, equipment, recreation Malta, Spain, Bulgaria, Denmark, Belgium, Germany, Italy, Europe FLOODS TOTAL VALUE OF PROJECTS FUNDING SOURCES  IMPLEMENTATION PERIOD  TYPE OF ANALYSIS  (EUR) 8.965 billion EU, World Bank, National 2006 - 2023  Quantitative, own analysis (3); Partial Quantitative / literature (5); Qualitative (20) 3 The case studies cover six upper-middle-income countries and 28 higher-income-countries according to World Bank definition as of 2021. According to the categorization of the World Bank, for FY2021, low-income economies are defined as countries with a gross national income (GNI) per capita of €925 (that is, US$1,035) or less in 2019; lower-middle-income economies are countries with a GNI per capita between €925 and €3,613 (that is, between US$1,036 and US$4,045); upper-middle-income economies are countries with a GNI per capita between €3,614 and €11,197 (US$4,046 and US$12,535); and high-income economies are countries with a GNI per capita of €11,198 (US$12,536) or more. Overview of Methodologies 23 NATURAL HAZARDS # CASE COUNTRIES (INCL. CROSS- TYPES OF HAZARD SECTORS COVERED STUDIES BORDER AND AREAS) INVESTMENTS 6 United Kingdom, France, UHI effects (2); early Housing and public buildings, Spain, Portugal, Austria warning (1); irrigation and early warning, water, agriculture water provision system (2); early warning and capacity building for droughts DROUGHTS preparedness (1) AND EXTREME TOTAL VALUE HEAT OF PROJECTS FUNDING SOURCES  IMPLEMENTATION PERIOD  TYPE OF ANALYSIS  (EUR) 100.18 million EU, National 2013 - 2022 Quantitative, own analysis (2); partial quantitative/literature (1); Qualitative (3) # CASE COUNTRIES (INCL. CROSS- HAZARD TYPES OF INVESTMENTS SECTORS COVERED STUDIES BORDER AND AREAS) 7 Italy, Romania, Turkey, Seismic retrofitting (5); Housing and public buildings, Albania, Croatia, Europe early warning (1); capacity education, health, early building (2) warning, emergency response, cultural heritage EARTH- TOTAL VALUE QUAKE OF PROJECTS FUNDING SOURCES  IMPLEMENTATION PERIOD  TYPE OF ANALYSIS  (EUR) 59.22 billion EIB, National, EU, World 2015 - 2025 Quantitative, own analysis (4); Bank partial quantitative/literature (2); Qualitative (1) # CASE COUNTRIES (INCL. CROSS- HAZARD TYPES OF INVESTMENTS SECTORS COVERED STUDIES BORDER AND AREAS) 10 Czech Republic, Poland, WUIs (2); fuel management Emergency response, early Spain, Portugal, Greece for wildfire prevention (1); warning, forestry early warning (3); cross- border support, coordination mechanisms and capacity building (4) WILDFIRES TOTAL VALUE OF PROJECTS FUNDING SOURCES  IMPLEMENTATION PERIOD  TYPE OF ANALYSIS  (EUR) 149.24 million EU, National 2013 - 2022 Quantitative, own analysis (7); Qualitative (3) Overview of Methodologies 24 NATURAL HAZARDS # CASE COUNTRIES (INCL. CROSS- HAZARD TYPES OF INVESTMENTS SECTORS COVERED STUDIES BORDER AND AREAS) 6 Switzerland, Croatia, Bosnia Information system and Agriculture, recreation, and Herzegovina, cooperation mechanism (3); Transportation, early warning Montenegro, France, Spain, resilient road (1); landslide Albania, Italy prevention and response MASS investments (2) MOVEMENT / LANDSLIDES / TOTAL VALUE AVALANCHES OF PROJECTS FUNDING SOURCES  IMPLEMENTATION PERIOD  TYPE OF ANALYSIS  (EUR) 20.60 million EU, National, World Bank 2019 - 2020 Partial Quantitative / literature (1); Qualitative (5) # CASE COUNTRIES (INCL. CROSS- HAZARD TYPES OF INVESTMENTS SECTORS COVERED STUDIES BORDER AND AREAS) 2 Italy, Spain Preventive Investment (2) Transport, early warning TOTAL VALUE VOLCANIC OF PROJECTS FUNDING SOURCES  IMPLEMENTATION PERIOD  TYPE OF ANALYSIS  (EUR) 55.00 million EU, National 2013 - 2020 Qualitative (2) TECHNOLOGICAL HAZARDS AND CROSS-CUTTING # CASE COUNTRIES (INCL. CROSS- HAZARD TYPES OF INVESTMENTS SECTORS COVERED STUDIES BORDER AND AREAS) 1 Estonia Oil spills prevention (1) Water, fishery TOTAL VALUE IMPLE-MENTATION OF PROJECTS FUNDING SOURCES  TYPE OF ANALYSIS  OIL SPILLS PERIOD  (EUR) 33.00 million EU, National 2013 Partial quantitative/literature (1) # CASE COUNTRIES (INCL. CROSS- HAZARD TYPES OF INVESTMENTS SECTORS COVERED STUDIES BORDER AND AREAS) 1 Latvia Cleaning up hazardous Water waste (1) CHEMICAL TOTAL VALUE IMPLE-MENTATION OF PROJECTS FUNDING SOURCES  TYPE OF ANALYSIS  PERIOD  (EUR) 29.00 million EU, National 2013 Quantitative, own analysis (1) Overview of Methodologies 25 TECHNOLOGICAL HAZARDS AND CROSS-CUTTING # CASE COUNTRIES (INCL. CROSS- HAZARD TYPES OF INVESTMENTS SECTORS COVERED STUDIES BORDER AND AREAS) 2 Italy, United Kingdom, Return on investment of Health Sweden, Netherlands, National Public Health Europe Program (1); equipment for health-related disasters (1) EPIDEMIC TOTAL VALUE IMPLE-MENTATION OF PROJECTS FUNDING SOURCES  TYPE OF ANALYSIS  PERIOD  (EUR) 4.50 billion EU, National 2021 Partial quantitative/literature (2) # CASE COUNTRIES (INCL. CROSS- HAZARD TYPES OF INVESTMENTS SECTORS COVERED STUDIES BORDER AND AREAS) 3 Czech Republic, France Security of nuclear power Energy, emergency response plant (2); cleaning up and equipment, water uranium (1) NUCLEAR/ RADIO- TOTAL VALUE IMPLE-MENTATION LOGICAL OF PROJECTS FUNDING SOURCES  TYPE OF ANALYSIS  PERIOD  (EUR) 24.34 billion EU, National 2018 and on-going Qualitive (3) # CASE COUNTRIES (INCL. CROSS- HAZARD TYPES OF INVESTMENTS SECTORS COVERED STUDIES BORDER AND AREAS) 8 Croatia, Serbia, Romania, Rescue and emergency Education, transport, Europe and Central Asia, response equipment (1); emergency response, early Finland, Poland, Italy, Early Warning (4); climate warning, communication/ICT, Latvia, France, Europe and change adaptation (3) recreation, houses and public Central Asia, Greece, Malta, buildings Switzerland, United ALL Kingdom, Hungary DISASTERS TOTAL VALUE IMPLE-MENTATION OF PROJECTS FUNDING SOURCES  TYPE OF ANALYSIS  PERIOD  (EUR) 730.93 World Bank, EU, National 2006 - 2020 Partial Quantitative / literature million (1); Qualitative (7) Source: World Bank analysis Overview of Methodologies 26 Figure 3: Overview of case studies analysed under this report Source: World Bank analysis Figure 4: Economic loss (€, billions) from considered hazards and climate impact at warming levels for the EU and the United Kingdom (for macro regions) Source: Szewczyk, et al. (2020) Overview of Methodologies 27 3. Case StudiesResults and Analyses by Investments This section presents selected results from the analysis, focusing on main pieces of analysis and comparing results in light of the literature. Subsections start with an introduction to hazard risks worldwide in the EU, include a summary of findings, and then present selected detailed analyses for illustration. 3.1. Flooding 3.1.1. SUMMARY OF FINDINGS FOR seen in continental and Mediterranean Europe FLOODS (Guerreiro, et al., 2017). Surface water maps, used in conjunction with existing flood data, can provide a Floods are the most frequent natural disasters and the fuller picture of these pluvial flooding risks and equip most common disaster regionally, and they can cause stakeholders with information on areas at risk beyond widespread devastation that results in loss of life and/ river floodplains. or damages to personal property and public infrastructure. More than 2 billion people worldwide A range of interventions designed to deal with were affected by floods between 1998 and 2017 inundation triggered by river flooding, flash flooding, (WHO, 2021). Floods can be classified in three broad and storm-surge coastal flooding are covered in this categories: (1) pluvial floods, which are caused by section. The understanding of hazard and risk rapid and excessive rainfall that quickly cause water to distribution is the first step in the development of an cumulate outside of water bodies; (2) river floods, appropriate defence strategy. The impacts of river which are caused when consistent rain or snow melt floods, flash floods, and coastal floods can be forces a river to exceed its capacity, causing water to addressed with different risk reduction strategies. overflow from its course; and (3) coastal floods, which are caused by extreme sea levels associated with In this section, we have demonstrated benefit-cost storm surge, strong wind, high waves, or exceptional assessments for four types of flood interventions, tides. which can be categorized as (1) structural flood protection (for example, levees and walls), (2) nature- Over the past 30 years, the number of devastating based solutions (for example, NFM and floodplain flood events in Europe has more than doubled, and restoration), (3) property-level protection (for example, there has been a proportionally higher increase in the small-scale demountable door barriers), and (4) flood frequency of flooding events caused by surface water early-warning systems. BCRs for the different types of flooding due to overwhelmed drainage systems, interventions are shown by a combination of although investments in flood protection seem to have conducting detailed case study analysis and reviewing been effective in reducing flood risk (Paprotny, et al., past BCAs, including both prospective and 2018). JBA Risk Management also cites projections, retrospective types of assessments. The flood suggesting that this trend will continue, and the effects mechanism in most case studies considered is fluvial of these flooding events will be exacerbated by climate flood originating from one or more major rivers. A few change. A study conducted by Selma Guerreiro and other examples consider coastal flood risk from co-authors in 2017 was the first attempt at continental extreme storm surge events, alone or (for delta regions) city flooding modelling of European cities, and they in combination with river floods. Pluvial flood (flash found that, generally, cities with a lower percentage of flood) is also included in some analyses presented. flooding are located in the north and west coastal Table 2 summarizes main data and information areas of Europe, while higher percentage areas are sources. Case Studies Flooding 29 Table 2: Overview of data and information sources for flood analysis INVESTMENT CASE STUDY DATA SOURCE NAME AND REFERENCE Structural Machlanddamm • Total investment information from OECD report on a draft case study of disaster protection risk prevention and mitigation policies in Austria • Residential buildings exposure data, developed under the Seismology and Earthquake Engineering Research Infrastructure Alliance for Europe (SERA) project NBS INTERREG • External economic assessment, published by Tweed Forum (Eddleston Water project Project Summary Report and Integrating natural capital into flood risk Eddleston Water management appraisal Study Report) NBS Sigma Plan • Costs, risk reduction benefits, and co-benefits obtained from ‘Sigma Plan Social- cultural Benefit-Cost Analysis, Synthesis Report (Sigmaplan Maatschappelijke Kosten-Baten Analyse)’ EWS The Flandres • FEWS anticipation capacity, warning coverage and losses reduction assumptions Flood Early based on the national report on flooding published by Flemish Environment Warning System Agency • JBA Global Flood Model and residential exposure PLP Property Level • Implement cost and the simulation of PLP effectiveness based on the ECHO Protection in study ‘Prevention and Preparedness in Civil Protection: Cost-benefit Analysis Northern Italy of Mitigation Measures to Pilot Firms/Infrastructures in Italy’ Source: World Bank analysis Flood hazard models need to be adapted to test the and exposure intersection is crucial when effect of different investment types analysed on considering the difference in BCR between case fatalities and economic losses. For the detailed case studies and is illustrated in the regional-scale PESETA studies presented, we have applied a global flood analysis, which demonstrates the different BCRs model to assess flood impact with and without possible in each country when common defence protection (as a basis to estimate dividend 1), based assumptions and costs are applied. on stochastic modelling of flood inundation intersected with buildings distribution, construction, Results of the analysis of investments are generally and replacement costs. Estimation of dividends 2 positive in terms of net benefits (BCRs higher than 1, and 3 due to flood risk reduction strategies also varies positive NPVs and IRRs higher than defined by type of investment and requires data from sources thresholds), although consistent with research other than the flood inundation model. More details findings (Dottori, et al., 2020) some hard infra­ on the methodologies, models, and types of impacts structure investments, in some contexts, tend to have considered are included in the relevant section on BCRs close or lower than 1. Complementary floods in the report. investments and comprehensive analysis to inform designs (including considering climate change BCRs for flood protection can be extremely variable, scenarios) could therefore be highly beneficial for as they depend on the scale and type of investment, investments to maximize benefits across sustaina­ the intersection of localized hazard and exposed bility goals. More details are included in Figure 5, assets, and the factors captured in the analysis. This Figure 6 and Figure 7. variability is demonstrated by the specific cases analysed here and broader regional-scale analysis Figure 5 shows the distribution of benefit-cost ratios such as conducted under PESETA IV (Dottori, et al., (BCRs) for flood investments, based on a five-number 2020). The Eddleston Water case study, as it summary: minimum (shown in orange), first quartile, includes multiple analyses with different factors, median (shown in red), third quartile, and maximum demonstrates the latter. The influence of hazard (shown in orange). Case Studies Flooding 30 Figure 5: Findings of BCA for floods (BCRs) Source: World Bank analysis; based on external data and information; presenting in part results from literature based on World Bank & external reports (1 structural protection result from World Bank (2007), 3 nature-based solution results from Spray (2016), Hölzinger & Haysom (2017) and Gauderis, et al. (2005)) Figure 6 presents boxplots that display the distribution quartile, median (shown in red), third quartile, and of NPVs (in millions of euro) for different types of maximum (shown in yellow). The outliers are shown as investments in flood prevention based on a five- dots. Extreme values are excluded from the first number summary: minimum (shown in yellow), first graph and included in the second one. Figure 6: Findings of BCA for floods (NPVs) Case Studies Flooding 31 Source: World Bank analysis; based on external data and information; presenting in part results from literature based on World Bank & external reports (1 structural protection result from World Bank (2007), 4 nature-based solution results from Spray (2016), Grossmann & Hartje (2012), Hölzinger & Haysom (2017) and Gauderis, et al. (2005)) Figure 7 below shows the distribution of ERRs for quartile, median (shown in red), third quartile, and different types of investments in flood based on a five- maximum (shown in orange). The outliers are shown number summary: minimum (shown in orange), first as dots. Figure 7: Findings of BCA for floods (ERRs) Source: World Bank analysis; based on external data and information; presenting in part results from literature based on World Bank & external reports (1 structural protection result from World Bank (2007), 3 nature-based solution results from Spray (2016), Hölzinger & Haysom (2017) and Gauderis, et al. (2005)) Case Studies Flooding 32 Overall, the results and qualitative research on low but considers only benefits of avoided damage. structural protection showed that hard infrastructure The lack of flood-related fatalities in any case in solutions are not necessarily always an option that has Austria meant they were not considered, land/ a BCR higher than 1. However, the BCR is dependent property values were not expected to be affected on the modelling assumptions and the availability of (due to additional regional development data to enable the quantification of all dividends restrictions), and dividends 2 and 3 could not be (particularly intangible impacts over health and estimated due to a lack of data on additional environment), which were not included in some case amenities and even official information on the exact study analyses. Given increasing multi-hazard risks number of protected houses. and the need for integrated investments, it is im­ perative to collect sufficient baseline information • Case study 2 (World Bank Project Appraisal across all dividends when designing investments, to Document [PAD] analysis (World Bank, 2007), ex assess hard infrastructure solutions with the Triple ante and ex post): The analysis of a major river flood Dividend Framework; this would promote designing protection project in Poland derived a high BCR investments that maximize co-benefits alongside (5.14, NPV of about €2 million, IRR/ERR of 81 reducing losses and saving lives. Evaluating the costs percent), which was mainly due to the consideration and benefits of complementary or other investments of intangible benefits (that is, reduced mental (soft investments, NBS) with the Triple Dividend health and health impacts) and the consideration of Framework when considering hard infrastructure can economic benefits from future gravel production in reveal added ecosystem benefits and any impact the reservoir area, which became available due to (positive or negative) in terms of cost or protecting the flood strategy including construction in a gravel- lives and assets. Another result emerging from rich area. The case study estimated substantial qualitative case studies is that citizen and stakeholder physical and mental health benefits from the risk engagement and extensive consultations and reduction investments. cooperation mechanisms can support an enhanced decision-making of designs informed by evaluation • NBS make use of natural processes to decrease (the Netherlands, Malta) as well as implementation flood risk while also providing ecosystem services, (Greece/Bulgaria cross-border and Greece). More they can be implemented alone or in combination details on the utilization of BCA and participatory with traditional engineering approaches. The EU decision making in the Netherlands for flood risk has been building evidence of the cost-effectiveness management are highlighted in Table 89, Table 90 of NBS through various programs. While NBS can and Table 91 in Annex 5. Moreover, prioritization be more cost-effective than structural (grey) models and methodologies such as criticality infrastructure, they can provide lower safety analysis (Vukanovic, 2018; Rozenberg, et al., 2019), benefits in some cases compared to hard can support the better targeting of specific assets infrastructure (although costs generally also and infrastructure considering the asset-specific decrease). It can be most beneficial to consider vulnerability and cost-effectiveness, which have been NBS as complementary solutions, forming hybrid applied in countries such as Serbia or Romania green-grey infrastructures, and they can maximize (European Commission, 2018). a range of benefits including improving water storage/absorption capacity, ecosystem services, • Case study 1 (new analysis under this project recreational use, protection around coastal risks, (Heidrich, 2016; JBA Risk Management, 2021), ex and so on. They can also allow for longer-term post): Analysis of Central Europe’s largest flood flexibility under projected climatic changes, control protection project, the Machlanddamm in whereas a firm standard of protection (SoP) of hard Austria, showed that the protective structures had defences may not easily be adapted to address variable effects on reducing risk in each of the more extreme risks. NBS can provide educational protected communities. On average, the reduction opportunity (Eddleston Water, United Kingdom), of risk in residential properties was 12 percent create habitat networks (Ijsselpoort, the compared to the undefended scenario. BCR of <1, Netherlands), and have co-benefits in terms of NPV of about −€146 million, and IRR/ERR of −80 climate and erosion regulation (Yorkshire, the percent was estimated, which is considered to be United Kingdom). Landscape preservation such as Case Studies Flooding 33 dunes has also been shown to support the • Case study 5 (external analysis (Hölzinger & restoration of habitats and protect from flood and Haysom, 2017) ex post): The analysis of the storm risks (Barcelona, Spain) and flood risk floodplain restoration project in Chimney Meadows, reduction in coastal/tidal areas seems to generally the United Kingdom, demonstrates the high value work well with integrated ecosystem presentation/ (BCR of 1.5–4.8, NPV €1,665–€11,528, upgrading measures (Sandwich, the United IRR/ERR 35.1–79.18 percent) that restoration Kingdom, and Alkborough, the United Kingdom). In from intensive farmland can have on flood risk as urban settings, measures combining natural well as co-benefits. The study measured many building materials and shaping park and recreation ecosystem benefits affecting the second and third areas as well as neighbourhoods with green dividend and could be improved by exploring the solutions can have positive impacts on flood risk effects on agricultural supply chains and impact on reduction and liveability of the areas (Benicassim, broader communities. Spain; Mayes Brook River, the United Kingdom; and Malmö, Sweden). Æ Nature-based coastal and tidal protection: Æ Natural Floodplain Management: • Case study 6 (external analysis by Sigma Plan contractors (Gauderis, et al., 2005), ex ante): The • Case study 3 (External analysis by Scottish analysis of the Sigma Plan, an integrated flood Environment Protection Agency [SEPA] and protection plan combining grey and green contractors (Spray, 2016), ex ante and ex post): infrastructure, yielded BCRs higher than 1 for all The analysis of the Eddleston Water project that solutions including just implementing a storm surge involved landscape restoration yielded high BCRs barrier. The BCR increases from an estimated 1.87 at economic appraisal (BCR of 9–17). A second to 4.97 (NPV until 2100 of €346–593 million, IRR/ estimation of ecosystem services, which applied a ERR of 46.57–79.89 percent), and the relative different set of services and valuations, showed that cost-effectiveness increases when integrating grey BCRs are lower and only higher than 1 when a 100- measures with NBS or using a work-with-nature year timescale is considered. Depending on the approach. Although safety benefits tend to assessment and combination of options, the BCR decrease slightly, costs also decrease while co- was estimated at 1.71-2.42 (NPV up to €9,512 and benefits (especially environmental ones) tend to IRR/ERR of 41–59 percent). This indicates that increase. these interventions tend to take longer to yield economically valuable benefits and that longer time Flood Early Warning Systems (FEWS): provide horizons for policy recommendations should be integrated hazard monitoring, forecasting, and alerts considered and even potentially lower discount that enable various stakeholders to take timely actions rates. Moreover, in such wide-ranging analyses, the to reduce disaster risks in advance and during selection and valuation of benefits can lead to hazardous events. Economic assessments of EWS different outcomes. impacts in quantitative terms are prone to several uncertainties, relying on many assumptions and • Case study 4 (external analysis (EEA, 2017; generalizations and the results should be considered Grossmann & Hartje, 2012), ex post): The analysis with caution as they may capture impacts from other of the green, hybrid, and grey infrastructure investments as well. The literature reviewed for this solutions implemented along the Elbe River in report shows that FEWS tend to have positive benefits Germany showed highest net benefits for an (for example, European Flood Awareness System integrated floodplain management investment with [EFAS] (Pappenberger, et al., 2015) and Grimma, green infrastructure compared to hybrid or grey Germany). Moreover, risk information systems related investments (NPV of €429,746 compared to to EWS can also have numerous benefits (Greece/ 196,337 and 72,707, respectively) while showing Cyprus Environmental Risk Management Information negative NPV for grey infrastructure where only Service, Poland PANDA). avoided loss benefits are included. This case study is specific as it looks at options of replacing old flood • Case study 7 (new analysis under this project, ex protection infrastructure and used a cost- post) (JBA Risk Management 2021, Perera et al., effectiveness methodology. 2019): The analysis of the advanced FEWS in Case Studies Flooding 34 Flandres, Belgium, yielded a range of BCRs for 3.1.2. STRUCTURAL PROTECTION various scenarios to test sensitivity of losses AGAINST FLOODS to uptake of the warnings issued (5 percent, 25 percent, and 50 percent assumed loss Risk reduction strategies using structural protection reduction). BCRs ranged from 0.5 to 5.2 (NPV of focus on the control of floodwaters that result from -€1.5 million to €12.5 million, IRR/ERR of −100 to intense rainfall and/or overflow of river channels. Most 80.65 percent) suggesting that the strategy requires flood risk management involved engineering measures a minimum level of uptake to provide a BCR to control flooding, avoiding as much as possible the greater than 1. Benefits may have been change of hazard where vulnerable elements are underestimated given the difficulties to capture located. These are also known as ‘grey’ or ‘hard’ dividend 2 and 3 benefits, which may include measures and can include both static elements (such actions of households after flood warning and as embankments, dams, levees, and channels) and reductions in emissions and were not quantified active elements (such as water gates, pumps, and due to unavailable data. mobile barriers). PLP involves the installation and deployment of The design of protection measures relies on the flood resistance measures (retrofitting or by design) assessment of risk probabilities to elaborate to prevent water from entering individual properties appropriate protection standards. A design flood is and resilience measures to limit the damage caused defined by its probability of occurrence, for example, once it has entered. There is limited information ‘1 percent annual exceedance probability (AEP) or 1 in available on examples of PLP being applied in EU MS, 100 return period’ defines a flood which has 1 chance but benefits can be substantial given potential in 100 of occurring in any one year. Structural increases in property values as well as energy efficiency protection measures are designed and built to meet when substantial PLP measures are implemented. A with a certain SoP. It is important to note that protection prospective analysis of PLP was conducted to explore standards need to be updated over time, in line with the levels of benefits, but there were great difficulties the changes in hazard frequency brought by climate in quantifying uptake or buy-in of PLP strategies and change. co-benefits at the individual property level. Models can account for the risk reduction due to flood • Case study 8 (new analysis under this project, ex protection by explicitly modelling protective structures ante/hypothetical): The analysis of a hypothetical of by delineating area protected by those structures. comprehensive PLP program over two towns in Site-specific models built for a particular location can Northern Italy based on previous research on PLP explicitly include the structure in the model and cost estimates (ECHO, 2014) yields BCRs of less estimate the chance of the protection being overtopped than 1, lower than examples found in the literature. or breached, resulting in a flood. Probabilistic models This can be explained by three factors: (a) the over a large area tend to assume a level of flood difficulty in estimating a realistic PLP investment in protection in terms of the return period (that is, a relation to the hazard probability and standard of defence designed to protect up to a 1-in-50-year defence; (b) the transferring of assumptions from event) and floods are assumed to not cause loss below different contexts (for example, rural settlements that return period. A hybrid approach - defining the exposed to intense river floods compared to high- areas protected, as informed by the locations of the density urban areas exposed to moderate pluvial protection system, and applying the design level of floods); and (c) the uncertainty in risk modelling for protection in only those areas - can also be applied specific locations (building level), affecting the and assumes that those protected areas only scale of risks to be taken into account and thus the experience flooding when an event is above the design- scale of costs. level return period. These approaches can be applied to a scenario-based analysis of probabilistic analysis and can simulate the benefit for a single protective structure or commonly a series or combination of multiple structures and types of structure. Case Studies Flooding 35 RIVER FLOOD PROTECTION: THE MACHLANDAMM, OBERÖSTERREICH, AUSTRIA This case study is a new ex-post analysis under this river flooding on the relevant section of the Danube project that involved modelling of hazards. without and with the effect of flood protection by the Machlandamm. The simulated difference in number of Æ Description buildings flooded and resulting economic damage, represented as AAL and return period losses, is the The Machlandamm is Central Europe’s largest flood expected benefit of protection. The analysis uses control protection project and the largest one in the exposure data. history of the Oberösterreich region. Construction began in 2008 and was completed in 2012. It consists The analysis of this case study uses a methodology of about 30 km of earth dams, 4 km of mobile flood and data consistent with the accompanying EU protection elements, and a few hundred meters of regional flood analysis. The exposure data applied are flood protection walls, in addition to pumping stations, a disaggregated version of residential buildings gate valves, and an 8.4 km flood basin running parallel data developed under the SERA project (Crowley, et to the Danube River (Heidrich, 2016). The project al., 2020). The communities in the study area are includes eight project units on the left bank of the largely residential buildings; damage to these buildings Danube and protects seven municipalities (Ecker & is modelled with a residential property and contents Hrebik, 2012). Each unit is protected by earthen dams vulnerability curve developed by JBA. The with an SoP of 1-in-100-year return period, except for accompanying project report on Component 2 one area with 1-in-30-year SoP (Weingraber, 2020), as (regional analysis) contains more details on all aspects indicated in Figure 8. The dam has been designed with of the risk analysis method. spillways such that they cannot protect against larger floods; else the flood risk of other communities would Flood protection is accounted for in the model by be increased. The total cost of the project was €182.6 identifying the communities protected by the million (€150,000 per house protected) protective structure in each of the eight project units (GOV/PGC/HLRF, 2015). The project was supported (Figure 8). Only the effect of the earth dam is included; financially by the Oberösterreich region and by other no demountable barrier defences have been modelled institutions. In 2013, a severe flood hit the region due to a lack of information on their operation and (IBS, 2013), but available estimates of impact are location. Where the return period of a simulated flood subject to significant uncertainties about what they event in the model is below the SoP, the defence is include and are only available at much broader modelled as being fully effective and no flooding geographic scales than this case study’s domain. occurs in the delineated area (JBA Risk Management , Therefore, we estimate damage to the case study 2021). Where the severity of a simulated flood event areas using a proprietary flood model. exceeds the capacity of the defence, a defence overtopping calculation is applied to reduce the impact Æ Methodology of the flooding based on the volume of water overtopping the defence. The change in flood return Dividend 1 (avoided fatalities and economic damage) period is applied to all exposure points located within a is estimated by applying the JBA probabilistic global defended area, thus reducing the risk estimate (AAL) flood model to estimate the frequency and severity of and return period losses in that area. Case Studies Flooding 36 Figure 8: Location of case study and areas estimated to be protected by each project unit of the Machlandamm, with SoP denoted for each unit Source: World Bank analysis; elaboration based on information from interview and reports In attempting to quantify the effects of protection on Æ Results of the analysis, by dividends Dividends 2 and 3 of the Triple Dividend Framework, and overall we encountered an absence of data. This prevented the quantification of some potential benefits, which for The analysis showed variable influence of the an investment of this size would be expected to include protective structures on reducing risk in the protected stimulus of the local or regional economy due to the communities. Figure 9 shows the estimated risk construction project, and change in land value or reduction (AAL in euros) per level 3 administrative property prices due to enhanced flood protection. In unit, with Grein showing the greatest potential Oberösterreich there is a law prohibiting new reduction. The risk reduction is a factor of flood development in high-risk flood zones, so we assume no inundation with and without the protection and the broad change in land value due to new development concentration and value of exposure within the potential (since none can be constructed). However, protected area. The overall reduction in risk to property values and domestic land value could be residential properties due to Machlandamm protection expected to increase due to higher level of flood is 12 percent compared to the undefended scenario. protection afforded by the dam. No analysis on this aspect had been previously conducted for the Machlandamm and the age of the project prevented thorough analysis of these aspects here. Case Studies Flooding 37 Figure 9: Simulated reduction in risk per level 3 Administrative unit (AAL) due to protection by the Machlandamm flood protection Source: World Bank analysis; elaboration based on the results from the analysis Table 3: Risk reduction represented by change in AAL due to the Machlandamm flood protection at key settlements in the case study area ADM2 ADM3 BASELINE LOSS DEFENDED LOSS REDUCTION % Perg Baumgartenberg 100,244 88,201 −12 Perg Saxen 355,017 354,445 −0 Perg Naarn im Machlande 1,385,847 1,185,831 −14 Mitterkirchen im Perg 799,441 619,618 −22 Machland Perg Mauthausen 1,757,207 1,757,110 −0 LinzLand Enns 4,707,258 4,707,247 −0 Amstetten Grein 891,294 57,187 −94 Total 9,996,308 8,769,639 −12 Risk reduction −1,226,669 (reduction in AAL) Source: World Bank analysis; based on external data and information Case Studies Flooding 38 Table 4: BCR for Machlandamm per dividend, assuming a 30-year period of operation BENEFITS (€, MILLIONS) COSTS (€, MILLIONS) Dividend 1 36.8 Dividend 2 Not quantified Dividend 3 Not quantified Total 36.8 182.6 BCR = 0.2 Source: World Bank analysis; based on external data and information Table 5: Detailed breakdown of benefits for Machlanddamm by dividend FIRST DIVIDEND BENEFIT/COST Lives saved Not quantified (no evidence of fatalities without the protection) Injuries avoided Not quantified (as above) Property damage avoided (reduction in AAL for each €36.8 M year of 30 years of the assumed operation period) Total first dividend €36.8 M SECOND DIVIDEND Change in property value €0 Value added to broader economy from construction Not quantified (lack of available evidence) sector Total second dividend €0 THIRD DIVIDEND Transportation uses Not quantified (lack of available evidence) Total third dividend n.a. Cost of construction €182.6 M Second cost item Maintenance costs Not known TOTAL DIVIDEND €36.8 M BCR 0.2 NPV −€145.8 M IRR/ERR −79.85% Source: World Bank analysis; based on external data and information Case Studies Flooding 39 Æ Challenges faced and lessons learned construction firms normally have their own workers who may not be locally hired. In addition, if there are This case study demonstrates that the impact of some any locally hired workers involved in dam construction, structural protection infrastructure can be simulated it is uncertain where they find their next employment with relatively little detailed information on the once the dam construction has been completed. structure. No official data were available to describe Consequently, local realization of economic benefits the location, length or height of the earth dam or becomes difficult to quantify. delineate the areas protected. Publicly available satellite imagery was used to digitize the dam position In fact, other studies have found positive net benefits in GIS software and to estimate the areas protected by of investments through ex ante economic analysis as each section of the dam. Official information describing well as ex post when considering increases in property the prescribed level of protection was then sufficient to values in upgraded areas, among others. Analysis has estimate the frequency of flooding, up to which the been undertaken for a major infrastructural investment dam is effective. However, uncertainty around the in Poland in the Odra river basin. Moreover, other protected area and protected number of houses may analysis showed some of the challenges for large-scale underestimate the overall reduction in AAL. structural protection programs in terms of costs incurred as well as interesting solutions that can The case study also demonstrates the need to assess support better decision-making, development, and prospective large risk reduction investments according implementation of these projects to achieve higher net to the Triple Dividend of Resilience Framework in the benefits. These include risk-based prioritization of project appraisal stage. Despite the size of investment investments such as strengthening road infra- and potential benefits under dividends 2 and 3, there structure, soft measures enhancing capacity, was little information available so long after the management of water resources and participatory investment was implemented, with which to confirm or decision making. Examples are projects implemented quantify those benefits, including after extensive in Serbia, the Netherlands, Bulgaria, Greece and Malta consultations and additional research.4 The main that provided some useful lessons learned. challenge for analysing this case study was the lack of information on the co-benefits of the dam Possible avenues for further research could be construction, primarily benefits to the construction considered. Considering some of the factors below sector and impact of increased flood protection on could potentially be expected to increase the property values in the protected areas. This has assessed net benefits of this investment: hampered the full evaluation of such a significant investment and potentially underestimates the BCR. • Benefits of reduced stress (mental health) With more comprehensive analysis, a possible distributional effect is that this structure can prevent • Reduction of traffic and economic activity disruption risk or harm to those who are near rivers, including people with low incomes or who are homeless. • Property value increases linked to the enhanced Moreover, it is uncertain who benefits from the liveability of the area increased job opportunities in the locality since large RIVER FLOOD PROTECTION ON THE ODRA RIVER BASIN, POLAND Æ Description of the case study economic analyses comprised a comparison between the incremental capital and operating costs of the Major infrastructural investments in a dam and project scenarios with the incremental economic improved conductivity of Odra river (World Bank, benefits resulting from their implementation. The 2007) in the area of Wroclaw, Poland, were undertaken parameters for the economic evaluation include a 30- in a World Bank project in 2006, which included a year period of operation and a 90 percent economic prospective economic analysis for Wroclaw. The conversion factor. The economic analysis considered 4 For example, information about prices would have been costly to retrieve as the extraction is complex and therefore undertaken by private companies. Case Studies Flooding 40 both tangible and intangible benefits, making the This is above the 10 percent opportunity cost of capital methodology closer to the triple dividend approach. (OCC); before the 2008 financial crisis 10 percent was a threshold above which projects were considered Æ Methodology worthwhile (today this threshold is lower). The BCA of this project estimated annual average Total direct flood damage was estimated €4.01 billion damages with and without flood protection, (PLN 12.035 billion), and intangible damages at €0.5 considering multiple flood probabilities and severity. billion (PLN 1.965 billion), with the project projected to Avoided damages, that is, the difference between reduce damages to 72 percent of these estimates damages with and without the project, were the main (€2,166.3 billion and €353.7 billion, or PLN 8665.2 benefits considered with the specific components of: billion and PLN 1414.8 billion, respectively). In property and contents flood damage; damage to public addition, the project was expected to generate €5 infrastructure and facilities; agricultural production million (PLN 20 million) equivalent annual extraction losses; damage to trees; and damage to environment, of gravel from the Raciborz reservoir area. Gravel stock land and livestock. Secondary benefits included the can last for a total duration of 20 years. At a discount benefits from the exploitation of gravel in the rate of 3.5 percent, present value of this 20-year Raciborz reservoir area. While many intangible benefits stream of future incomes is calculated at €73.55 were considered in the project appraisal, the ERR was million (PLN 294.2 million). based on these quantified primary and secondary benefits. The following tables list these benefits according to the triple dividend framework and results from analysis Æ Results of the analysis by Dividends (Table 6 and Table 7). Reduction in the direct flood and overall damages forms the first dividend, economic benefits of the project are included as the second dividend, and The estimated ERR for the project was 17.4 percent. finally the intangible benefits are included as the third That is, the Polish economy would realize a 17.4 dividend. percent rate of return from implementing the project. Table 6: BCR for river flood protection for Poland’s Odra river basin per dividend (all values in 2006 Euro values at the exchange rate of 1€ = 4 PLN). BCR: 5.14 BENEFITS COSTS Dividend 1 2.17 B Dividend 2 73.6 M Dividend 3 353.7 M Total 2.59 B 505 M Source: World Bank compilation based on extracted data from the World Bank documents Table 7: Detailed breakdown of Odra River benefits by dividend FIRST DIVIDEND BENEFIT / COST Lives saved Not quantified (no evidence of fatalities without the protection) Injuries avoided Not quantified (as above) Avoided direct damages €2.17 B Total first dividend €2.17 B Case Studies Flooding 41 SECOND DIVIDEND Change in property value, productivity, capital investment Not quantified Value added to broader economy from construction sector Not quantified Present value of all future gravel production, assuming €73.6 M duration of 20 years and discount rate 3.5% (EURO) Total second dividend €73.6 M THIRD DIVIDEND Transportation Uses, agricultural productivity, ecosystem Not quantified benefits Reduction in intangible losses due to project (reduced stress, €353.7 M alcoholism, suicide rates, fear of floods, loss of control over situation, loss of memorabilia, and health problems) Total third dividend €353.7 M First cost item Cost of construction €505 M Second cost item Maintenance costs Not quantified TOTAL DIVIDEND €2.59 B Total cost €505 M COST-BENEFIT RATIO (RATIO) 5.14 NPV €2.1 B IRR/ERR (%) 80.53 Source: World Bank analysis; based on results from World Bank Odra River PAD Æ Challenges faced and lessons learned In addition to quantifying many tangible benefits, this ADDITIONAL EXAMPLES OF STRUCTURAL appraisal used robust methods to quantify many PROTECTION INVESTMENTS AGAINST intangible benefits with considerable longer-term FLOOD RISK impacts. This includes increasing stress, fear of further floods, loss of control over the situation, loss of Several additional investments in structural flood memorabilia and health problems. Inclusion of these protection were found that could provide lessons additional benefits is important to justify the overall learned and inspirations. These investments cover economic viability of the project. However, several technical solutions such as barriers (dams, sluices and potential benefits and costs have not been quantified, dykes) and reclaiming land from the sea in the which would likely adjust the BCR presented above Netherlands; enhanced capacity for response across from the project documents. A distributional impact borders of Bulgaria and Greece; construction of a that we should be wary of is the ability for this network of storm water management infrastructure in development to displace local residents who may no Malta; and building of flood prevention structures in longer be able to afford living in the area. An increase Greece. Highlights and main lessons learned of these in property value could lead to real estate price investments are presented in Box 1 below. increases, and this may catalyse gentrification in the area. Case Studies Flooding 42 Box 1: Overview of other investments in structural flood protection across Europe A review of investments in structural flood protection across project is expected to reduce flood risk for residents and Europe provided several lessons learned and inspiring increase safety for business owners to locate and operate in achievements outlined below. A common theme is that a this area. combination of structural protection and soft factors such as improvements of water management or support of citizen A flash floods resilience project in Malta has achieved some engagement in the design and evaluation of programs benefits in terms of protecting residents. Between contributed to the success and net positive benefits of the September and January in Malta, severe flash floods occur projects. frequently resulting in economic loss and disruption. The €62.5 million (€44.9 million EU-funded) project “National A large-scale program implemented in the Netherlands Flood Relief Project” supported by EU funds 2007-2013 showcases some of the challenges faced with massive aimed to build an effective storm water management system projects in terms of costs, but also solutions that can be through the construction of a network of underground found in collaboration with civil society. The battle of the tunnels, canals and bridges (European Commission, Dutch in reclaiming land from the sea provides one of the 2013a). The project aimed for Malta to meet the most ambitious and successful examples of flood protection requirements of the European Floods Directive, while engineering. The Zuiderzee Works and the Delta Works are helping to reduce the negative impacts of flood on human two massive flood protection works, which required health, the environment, cultural heritage and economic consistent public investments (6–7 percent of Dutch annual activity, and improve sustainability by reusing storm water GDP at that time) and were a challenge for political decision- from both urban and rural areas. The project was expected making. After a storm in 1953 where 1836 people lost their to benefit an estimation of 165,000 Maltese residents lives, a large-scale project (“Delta works”) was implemented directly and indirectly. Subsequent EU funding (€54 million that consisted of a series of dams, sluices and dike 2013-2015) under the second River Basin Management reinforcement that was completed 1958-1997, including Plan of the country supported continued works on the storm the Maeslant storm surge barrier in the port of Rotterdam water management system and the collection and reuse of (Bos & Zwaneveld, 2017). Overall costs for the Delta works rainwater via reservoirs (European Commission, 2019). As were €5 billion and €450 million for the Maeslant barrier water management systems and impacts from floods are (Dutch Water Management, 2020)(Maeslantkering). This still massively impacting the country and criticisms were compares to around €5.5 billion investments for the Venice made for the effectiveness of the programs implemented, lagoon barrier (see Table 8 below that shows the cost of the Energy and Water Agency of Malta undertook extensive eight different storm surge barriers built in Europe since consultations and developed a menu of measures for the 1958). The final design of the Maeslant barrier was selected third RBMP (The Energy and Water Agency, 2020) based on a cost-effectiveness analysis and standards for comprehensively addressing the water sector and its flood protection according to land use and assets (Kind, management. 2014). The ex-ante cost-effectiveness analysis showed that the solution was best compared to alternatives such as In Athens, Greece, flood protection has been combined with raising dikes in the whole area of Dordrecht, representing efforts to enhance the liveability of the city while promoting savings of around 200 million EUR. economic activity (European Commission, 2013b; EPRS, 2020). The most damaging recent floods in Greece, in 1994 A cross-border program in a common area of Bulgaria and and in 2003, caused over €623 Million (US$700, 1994 Greece has achieved successes in terms of reducing ROE) and €707 Million (US$800, 2003 ROE) of damage, negative impacts of floods (Interreg Greece-Bulgaria, 2021). respectively. The €84 million project “Stopping Athens The cross-border area of Greece and Bulgaria, especially floods” (€71.4 million funded by the EU) 2007-2013 was the areas across the two international river basins of Struma/ launched to reduce the impacts of flood while encouraging Strymon and Evros/Maritsa, is highly vulnerable to floods. employment and city rejuvenation. The project invested in “Cross Border Planning and Infrastructure Measures for new flood prevention structures, which was aimed to protect Flood Protection” is an EU-financed €11.5 million (€9.8 about 116,000 residents flood. In addition, the million ERDF-funded) INTERREG project implemented from implementation of the project itself was expected to create 2017 to 2020 that protects the area from floods. The main 712 jobs and thus generate co-benefits for Greece’s objective of the project is to reduce the risk of floods by economy. Moreover, recent continued investments in the improving existing flood protection infrastructure along the region of Attica north of Athens included ambitious aims to river flow and reducing obstructions in the narrow areas of enhance the flood prevention network across municipalities the river basin. It also invests in early response equipment, where over 500,000 people live and commute every day which can reduce negative social and economic impacts on combined with a €150 million loan from the EIB for disaster the surrounding area and raise public awareness. The risk prevention and climate change adaptation programs Case Studies Flooding 43 across Greece (The National Herald, 2019). Given general specific commitments connected to procurement challenges of procurement, land management and planning (Transparency International EU, 2017). Moreover, a Horizon of such complex investments, the project was selected by 2020 program supported the engagement of citizens in Transparency International Greece and the European environmental monitoring, particularly flood and water Commission to be part of an Integrity Pact to monitor management issues (Alice Accelerate Innovation, 2018). Table 8: Comparison of costs for major investment projects in storm surge barriers in Europe NAME TYPE LOCATION COST (M €) Maeslant barrier Sector gate – y axis Hoek van Holland (NL) 450 Hollandse IJssel barrier Vertical lift gate Capelle aan den IJssel (NL) 20 Eastern Scheldt barrier Vertical lift gate Vrouwenpolder (NL) 2400 Haringvliet sluices Sector gate – x axis Hellevoetsluis (NL) 600 Ramspol barrier Inflatable tube Kampen (NL) 48 Hartel barrier Vertical lift gate Spijkenisse (NL) 98 Venice barrier Flap gate Venice (IT) 5500 Thames barrier Rotary segment and gate (x axis) London (UK) 600 Source: Noguiera & Walvaren (2018) The structural flood protection projects described above assessment. Modelling multiple individual segments as focus on protecting multiple properties/infrastructure inactive (representing a damaged or blocked segment), and areas of land from a source of flood hazard. This can the impact on disruption across the network can be explain the somewhat broad estimated number of measured to assess the criticality of each segment and to beneficiaries and is related to substantial potential measure overall redundancy in the transport network. benefits but also costs. Analysis of the vulnerability of segments against risk of damage should enable a prioritization of DRM Structural protection may also be implemented for asset- interventions including protective structures and inform specific protection, such as sections of road or railway BCA or cost-effectiveness analysis of the potential including bridges and tunnels, to improve the resilience interventions. Box 2 below outlines a few examples of of the transport infrastructure. A method used to prioritize projects implemented for protecting specific assets the protection of transport infrastructure is criticality mainly in the transport sector. Box 2: Structural protection for specific assets in the transport sector Two projects have showcased theoretically and in practice more proactive and resilient investments in Serbia. the application of cost-effectiveness analysis for the The CFR-SA railway project at Simeria, Romania, is one EC- prioritization of targeted structural protection interventions. funded project that focused on specific assets. Costing €2 Undertaken by the World Bank, a modelling exercise ranked billion and financed through the Large Infrastructure roads in different countries including Serbia according to Operational Programme (LIOP) 2014-2020, the project their criticality (Vukanovic, 2018; Rozenberg, et al., 2019). comprises rehabilitation and modernization works to The criticality was assessed based on vulnerability (therefore develop a high-speed rail link at the town and railway priority for intervention) and the cost-effectiveness of junction of Simeria. Crucially, the project considered climate interventions based on the impact costs avoided and change adaptations and protection of the rail and bridge implementation costs. Though based on limited information, infrastructure due to extreme flows and extreme storms. It the model undertook an economic analysis that examined also developed structures to protect the infrastructure from the cost-effectiveness of the roads, which can help to inform rockfalls (European Commission, 2018). Case Studies Flooding 44 3.1.3. NATURE-BASED SOLUTIONS FOR flooding to a particular level, yet they can reduce flood FLOOD PROTECTION risk potential to a large degree. The EEA (2017) analysed the cost-effectiveness of green and grey The concept of ‘nature-based solutions’, ‘ecosystem- infrastructure investments for flood protection in based adaptation’, ‘eco-DRR’, or ‘green infrastructure’ Germany, finding that the green measures can be has emerged as a good alternative or complement to superior to grey solutions and cost-efficient even when traditional engineering approaches. NBS make use of their indirect benefits were not considered. natural processes and ecosystem services for functional purposes, such as decreasing flood risk. While green infrastructure can take various forms and, These interventions can be implemented alone or in in principle, can be applied to address fluvial, pluvial, combination with “hard” engineering approaches and coastal flood in isolation or in combination, the (grey infrastructure). They can help mitigate flood and local environment and risk context dictates which decrease vulnerability to climate change while also solutions are applicable. For instance, floodplain creating multiple other benefits to the environment restoration can only occur where there is a fluvial and local communities. These include sustaining floodplain, not in steep-sided catchments, and dune livelihoods, improving food production and in turn restoration/stabilization is only possible in coastal food security, sequestering carbon, and providing areas with sand dunes. The following sections all recreation.5 Such solutions can be applied to river present short examples of NBS risk-reduction basins (for example, reforestation and natural flood initiatives. Due to the multi-faceted approaches typical control areas), coastal zones (dunes and wetlands), of NBS, some components of these cases are and cities (urban parks). applicable to more than a single section, but they are broadly presented here according to their primary NBS for risk management were supported by the EU focus. Smart green solutions can be particularly agenda first by FP7 projects and more recently by the important in urban contexts, as shown for investments H2020 programme and several Interreg projects, in Spain, the UK or Sweden to reduce flood risks and aimed at providing evidence of NBS cost-effectiveness, maximize co-benefits. covering risk reduction benefits as well as social and environmental effects. As with conventional 3.1.3.1. Natural floodplain management engineering solutions, the effective application of NBS requires a comprehensive risk assessment comparing This section highlights cases which aim to improve the the risk under baseline and defended scenario. condition of the floodplain to enhance ecosystem services and reduce flood risk by increasing capacity Although traditional risk assessment methods can be of the floodplain or wetland areas to retain runoff and applied to evaluate NBS, they hardly incorporate the reduce peak flows in the river. We present BCA full range of benefits generated by nature-based performed in NFM projects in the catchment of projects (European Union, 2019). NBS are emerging Eddleston Water, Scotland, which demonstrate the approaches that still need to develop standards and myriad ecosystem services benefits of NBS. Further guidance to facilitate a common understanding of examples such as a comparison of green versus grey their effectiveness and the risk reduction outcomes. It versus hybrid solutions for flood protection on the Elbe is also difficult to apply the concept of ‘protection River, Germany, and other investments from England standard’ to NBS, because they do not protect from and the Netherlands. 5 For ecosystem services associated with floodplains, see EEA (2019) Case Studies Flooding 45 INTERREG PROJECT EDDLESTON WATER (SCOTLAND) This case study is an external analysis that was from previous reports and adds the actual outturn cost undertaken with ex-ante and ex-post analysis that data for the implementation of NFM in the Eddleston involved partially modelling of hazards. catchment. Benefits in terms of avoided flood damage are compared for the NFM already implemented Æ Description (Tweed Forum, 2020) additional NFM investment (increasing the area changed from improved The Eddleston Water project, ongoing since 2009, grassland to native woodland and wet reed beds, and aims to reduce flood risk and restore the Eddleston increasing the number of flow restrictors and ponds), Water for the benefit of the local community and and traditional in-town engineered flood defences wildlife. It is funded by the Scottish government, (Burgess-Gamble, et al., 2018) and PLP. In addition, it Interreg, and the SEPA. The project involves river re- estimates the impact of a range of hybrid options. meandering, the planting of over 200,000 trees and Four options for in-town defences and three sub- the creation of new wetlands within the catchment (70 options for different levels of NFM were tested; for km2). This should slow the speed and impact of clarity here the report presents only two options: floodwaters affecting the village of Eddleston current NFM measures and the application of two (population 550) and town of Peebles (about 8,400) as different in-town standards of protection. The report well as creating new wildlife habitat, such as improved used updated definition of costs and took flood and ES spawning for salmon. The project partnership, led by benefits from analysis. The breadth of components the Tweed Forum, is closely monitoring the project included in the study was made possible by the results, including any reduction in flood risk for availability of GIS data on the location and downstream communities. The study was undertaken characteristics of the different interventions, project by the project consortium (see below) rather than in reporting of cost data, detailed simulation of avoided this project; it is included here as it is a rare case that damages from traditional structural protection in the demonstrates the high level of detail considered in a settlements and for NFM measures. The reduction in study of costs and benefits of NBS over several years. flood peak by slowing the catchment response is demonstrated, although it is noted that the potential Æ Methodology impacts of climate change by 2050 would more than counteract the considerable improvement. Spray (2016) analysed the Eddleston project including flood regulation to assess wider ecosystem benefits as Æ Results of the analysis, by dividends well as costs of afforestation and riparian woodland and overall planting. By far the greatest benefit of afforestation was in climate regulation—using a value transfer The impact of re-meandering, creation of ponds, approach this yielded up to four times the cost of introduction of woody flow restrictors and forest planting afforestation. Flood regulation in the catchment each have shown flood reduction and ecological contributed a minor proportion of the benefits, as did benefits, according to the SEPA study. The study biodiversity, education, aesthetics, water quality, and focused on the benefits delivered from planting riparian recreation. woodland, which returns a positive NPV and average BCR of 12.5 across low, central and high scenarios Another study (MacDonald, 2020) of this catchment (Table 9) - primarily from improvements to ecosystems tested the application of combining avoided damages in this catchment, with benefits of flood regulation in and natural capital in an economic appraisal of options, Eddleston village still positive under most current floods using the B£ST model (Horton, et al., 2019), which and under all climate scenarios. Benefit transfer values was selected after a review of available models in the for ecosystem studies were applied from other studies. same study. This study uses a slightly different benefit estimation framework and returns different results compared to the previous BCA. It considers the results Case Studies Flooding 46 Table 9: Estimated costs and benefits from the first economic appraisal of Eddleston Water NFM (lower and upper bound results in parenthesis) ALL VALUES GIVEN IN 2012 2016 2040 2080 THOUSAND EURO PER YEAR Total cost 7.81 7.81 7.81 (6.36 –9) (6.36 –9) (6.36 –9) Total benefits (flood 110.37 106.9 106.82 reduction and ecosystem (60.94–157.96) (58.32–156.35) (58.03–158.15) benefits) Net benefits (total benefits 102.56 99.1 99.01 minus total cost) (54.58–148.94) (51.96–147.32) (51.66–149.13) BCR 14.1 (9.6–17.5) 13.7 (9.2–17.3) 13.7 (9.1–17.5) Source: Spray (2016); Original values in pound converted using 2012 currency rate £1 =€1.26 According to the analysis, the total NPV of ecosystem contribution of NFM not associated activities), the benefits scaled over 100 years was reported at €1.25 triple dividend BCR is presented in Table 11. The million (with lower and upper bounds of €1 million original project reports provide longer timescales and and €1.3 million). This is additional to the benefit of value ranges. The reduction in property damage in avoided property damages of €680,000. The Eddleston and Peebles is shown in Table 10, with the summary of total costs and benefits in the Triple annual reduction in damage estimated at €35,473, Dividend Framework, based on central estimates for a equating to the NPV of €680,000 over 30 years.6 30-year timescale (and accounting only for the Table 10: Impact of NFM measures in the Eddleston Water catchment, on property damage in Eddleston village and Peebles town RETURN PRE-NFM POST-NFM AVOIDED PRE-NFM NO. POST-NFM NO. SPARED PERIOD DAMAGES DAMAGES DAMAGE OF HOUSES OF HOUSES HOUSES AFFECTED AFFECTED (€, thousands) AAL 1.05 1.01 35 n.a. n.a. n.a. 10 2.96 2.88 87 75 73 2 50 3.4 3.2 207 98 86 12 100 3.7 3.48 228 109 100 9 200 4.06 3.79 267 115 109 6 Note: MacDonald (2020); Original values in pound converted using 2020 currency rate £1 = €1.12. The Mott Macdonald study assessed 12 options for with 75-year return period SoP versus defences with managing flood risk in Eddleston Water catchment to 200–year return period SoP versus PLP) over an assess value for money and BCR of each – this is a appraisal period of 100 years. The flood damages combination of retrospective and prospective analysis avoided and ecosystem benefits of NFM already using the B£ST model. A matrix of costs and benefits implemented and additional NFM are shown in was created showing the variation in BCR of three NFM Table 12. options (no catchment NFM versus NFM already implemented versus additional NFM) and four in-town Comparing the in-town defence options also showed protection options (legal minimum versus defences the various BCRs of changing the SoP of defences, and 6 Converted from Pounds using £1 = €1.12 (2020). Case Studies Flooding 47 applying PLP. The baseline of NFM and no change to and PLP to €6,124,000. However, the BCR remained in-town defences yielded damages avoided of at 0.48 for 75-year defences, 0.45 for 200-year SoP €1,064,000 at a BCR of 0.45, when ecosystem services defences, and only increased significantly for PLP, are not considered. The addition of 75-year SoP returning a BCR of 1.34. Corresponding estimates defences increased the damages avoided to were also developed in that study for a case with no €5,497,000, 200-year SoP defences to €6,485,000 NFM, and with the additional NFM options. Table 11: Estimated benefits and costs for INTERREG project in Eddleston, Scotland per dividend, based on a 30-year timescale (€, THOUSANDS AT PRESENT VALUE) FIRST DIVIDEND Property damage avoided 680 Total first dividend 680 SECOND DIVIDEND Total second dividend 0 THIRD DIVIDEND Recreational benefits 391.2 Carbon benefits 897.9 Non-use biodiversity benefits 71.7 Benefits to anglers (NFM contribution), assuming ecological condition change ‘bad’ to 45.7 ‘moderate’ (change to ‘good’ may result in three times this value) Ecological status change (NFM contribution; ‘bad’ to ‘moderate’ (change to ‘good’ may 0.7–1.9 result in two to four times this value) Timber 452.8 Agricultural income foregone (lost income) −340.5 Health benefits 95.1 Education 160 Total third dividend (central estimate, for NFM contribution only) 1,253.3 Costs - NFM Enabling costs 779 Capital costs 1,072 Operation and maintenance costs 831 Other costs 13 TOTAL DIVIDEND Total benefits 1,933.3 Total cost 2,694 BCR 0.7 IRR/ERR (%) −39.35 Source: World Bank compilation; based on extracted data from the sources mentioned above; Original values in pounds and converted using 2020 currency rate £1 = €1.12. Case Studies Flooding 48 Table 12: Estimated benefits and costs for INTERREG project in Eddleston, Scotland per dividend, based on a 100-year timescale NFM ALREADY IMPLEMENTED ADDITIONAL NFM (€, THOUSANDS (€, THOUSANDS AT PRESENT VALUE) AT PRESENT VALUE) FIRST DIVIDEND Property damage avoided 1.1 3.2 Total first dividend 1.1 3.2 SECOND DIVIDEND Total second dividend 0 0 THIRD DIVIDEND Amenity Carbon benefits 1.67 8.65 Non-use biodiversity benefits 0.8 5.44 Education 0.7 5.15 Flows in watercourse 0.43 0.43 Water quality and pollution 0.41 3 Agricultural income foregone (lost Not assessed Not assessed income) Timber production Not assessed Not assessed Total third dividend (central estimate, 4.7 19.78 for NFM contribution only) Costs - NFM Total cost 2.34 13.46 TOTAL DIVIDEND Total benefits 5.77 22.97 Total cost 2.34 13.46 BCR 2.42 1.71 NPV 3.38 9.51 IRR/ERR (%) 58.62% 41.41% Source: Macdonald (2020) assessment of current NFM measures and prospective analysis of additional measures; original values in pounds and converted using 2020 currency rate £1 = €1.12 Æ Challenges faced and lessons learned differences include addition/omission of amenity, timber, and agricultural production foregone). This case study demonstrates the value in undertaking Potential distributional effects could include a multi-year study of benefits from flood interventions, maintaining the area’s biodiversity, preventing damage being able to incorporate ecosystem benefits that and injury to households living along the river, and are realized over time. This particularly concerns ensuring that the river continues to be a source for ecological responses to modifying the channel and clean water for the rest of the community. habitat (Spray, 2016), which can result in multiple ecosystem services benefits from water quality to Other studies have shown the comparative benefits of amenity value. It also demonstrates the different BCRs NFM. Green infrastructure solutions appear to have that are possible when ecosystem services are valued the highest net benefits and be most cost-efficient differently, or different services are included (here when these are compared to structural protection Case Studies Flooding 49 measures such as on the Elbe River in Germany, even the potential range and magnitude of benefits of NFM without consideration of indirect benefits. Moreover, investments but that prospective appraisals can indirect benefits can be substantial, as shown in the demonstrate optimal additions to NFM options. Here, Chimney Meadows or other case studies in the United with a fourfold increase in benefit but over 5.5 times Kingdom and the Netherlands. It would therefore be the original cost, the BCR reduces with the potential interesting to undertake more such multiyear case addition of NFM measures. The analysis also studies with high-quality, site-specific information, to demonstrated the multidimensional appraisal required compare various infrastructure solutions to analyse to consider the optimal in-town structural defences the advantages of combining grey and green and optimal level of NFM in the catchment, but note infrastructure. that the negative impact of structural options on some ecosystem services such as amenity benefits are not The various analyses on this NFM project demonstrate included here. GREEN, HYBRID, AND GREY INFRASTRUCTURE SOLUTIONS ON THE ELBE RIVER, GERMANY This case study is an external analysis that was Elde is in the middle of the Elbe river basin region and undertaken with ex-post analysis. Introduction is at high risk of flooding. Magdeburg is the most and background vulnerable region and was frequently hit by floods in 2002, 2003, 2006, and 2013. In order to reduce flood Æ Introduction and background risk for the region, dikes were built in the 19th and 20th centuries, which effectively protect about 85 A high-probability flood scenario in the Mittlere Elbe/ percent of the floodplains and decrease losses due to Elde region of Germany on the Elbe River would be flooding. In recent years, proposals that suggest a shift expected to impact 3,500 residents and four industrial from traditional grey infrastructures to nature-based facilities in the region, while an extreme catastrophe green measures have been made, as the green would affect 210,000 residents and up to 289 industrial measures are expected to be more adaptable to facilities (EEA, 2017). Starting in the Czech Republic, climate changes, support ecosystems and unlock the Elbe is a 1,100 km waterway that crosses 10 states social and environmental benefits beyond flood risk and many important cities in Germany ,Mittlere Elbe/ reduction (see Figure 10). Figure 10: Elbe River basin districts and potentials for green infrastructures Source: EEA (2017) Case Studies Flooding 50 Æ Description solution, several grey solutions, and a mix of the two (see Table 13). The green solution refers to the In order to examine the effectiveness and efficiency of restoration and preservation of floodplain wetland, grey and green solutions and find the optimal solution, while the traditional grey solution aims at the relocation seven approaches are considered, including a green or enclosure of dikes and dam. Table 13: Green, Grey and Hybrid measures for flood prevention in Elbe, Germany TYPE NAME OF MEASURES SHORT DESCRIPTION Green Controlled retention polders with Restoring a wetland in a floodplain (3.2 K ha) and preserving it. ecological flooding This will increase the area for the river to flood. Hybrid Combination of polders with Restoring a wetland in a floodplain (4.1 K ha), preserve it and ecological flooding and dike relocate a dike (3.4 K ha). relocation Grey Large scale dike relocation Relocate a dike in large parts of the river (35 K ha) Small scale dike relocation Relocate a dike in chosen parts of the river (9.4 K ha) Large scale controlled retention Enclose areas (25.6 K ha) with a dike and a dam, flooding during polder overcharge. Small scale controlled retention Enclose areas (3.2 K ha) with a dike and a dam, flooding during polder overcharge. Combination of polders and dike Enclose an area (4.1 K ha) and relocate a dike (3.4 K ha). relocation Source: World Bank compilation; based on information extracted from external documents, notably Grossmann & Hartje (2012) Æ Methodology Æ Results of the analysis by Dividends and overall Grossman & Hartje (2012) calculated the BCA and notably the NPVs of the seven measures and The study finds that the green infrastructure solution determined the effectiveness of the solutions based provides the highest net benefit and is the most cost- on the expected lifetime of a dike of 100 years and a efficient measure, even without the consideration of social discount rate of 3 percent. The costs of the the indirect benefits. The NPV of the green solution is measures included construction and maintenance around €108 thousand per ha in the scenario when costs as well as the economic losses from activities in only taking into consideration flood risk management agriculture and forestry due to wetland restoration or benefits. If the indirect benefits are included, the dike enclosure. The benefits are considered under two number will rise to around €430 thousand per ha, scenarios: the first scenario only considers the direct which is significantly higher than the NPVs of the benefit of flood risk reduction, while the second alternative solutions (see Table 14). This indicates that scenario includes indirect benefits from nutrition green solution yields substantial co-benefits in terms retention and biodiversity conservation. of nutrition and biodiversity preservation. Case Studies Flooding 51 Table 14: Cost-effectiveness of infrastructure options for the Elbe: NPV of options DIRECT INDIRECT NPV EFFECTS EFFECTS (IN 2012 PRICES) Flood-risk Nutrient Biodiversity Only flood risk Integrated reduction retention conservation management floodplain Benefits — Scenario 1 management [ EUR/ha/y] — Scenario 2 Green Controlled retention polders with 4.12 +++ +++ 108.26 429.75 ecologicalFlooding Hybrid Combination of polders with 1.83 ++ ++ 43.23 196.34 ecological flooding and dike relocation Grey Large scale dike 0.165 + + -3.71 72.71 relocation Small scale dike 0.07 + + -7.37 155.34 relocation Large scale controlled retention 1.02 13.84 13.84 polder Small scale controlled retention 4.12 101.99 101.99 polder Combination of polders and dike 1.83 + + 43.23 182.2 relocation Source: Grossmann & Hartje (2012) Æ Challenges faced and lessons learned 85 percent) by green protections, we should only be accounting for environmental/ecological benefits. It This is an example of replacing old flood protection could benefit from providing an analysis of different infrastructures. Alternatives considered include both alternatives. By investing in green infrastructure traditional and eco-friendly options, with the green or options for integrated floodplain management, the eco-friendly restoration producing the highest net communities near the Elbe can used the saved money benefits allowing for environmental/ecological to invest in other climate-resilient projects. Moreover, sustainability. While this is not a conventional case of members of local communities will also be able to building new flood protection infrastructures, wider increase their private allocations on other important range of alternatives made this case study an things. For example, reduced private burden of flood interesting one for future references – both in the due to public investment in DRM projects will allow cases of restoration or new constructions. them to invest more on their children’s human capital development. Such longer term indirect benefits may This study had to use a cost-effectiveness methodology be regressive to income, that is, poorer households as it was aimed to assess the replacing of traditional may benefit more through their increased allocations protections (that were reducing the flood damages by to daily essentials. Case Studies Flooding 52 CHIMNEY MEADOWS, OXFORD, ENGLAND, FLOODPLAIN RESTORATION This case study is an external analysis that was food production based on agricultural statistics and undertaken with ex-post analysis. previous yield records; and flood regulation based on avoided damages. Æ Description of the case study Æ Results of the analysis by Dividends The Chimney Meadows case study demonstrates the and overall effect that restoration of floodplains from intensive farmland can have on flood risk. Chimney Meadows is a A BCR greater than 1 was determined under both a 260-hectare farm with 50 hectares protected as natural business-as-usual scenario (BCR 1.5; total net benefits reserve to 2003, and the rest as farmland in intensive of €1.7 million) and an aspirational scenario (BCR 4.8; management. In 2003 the land was purchased by a total net benefits of €11.5 million) over a 30-year period wildlife trust, with the goal to covert the agricultural Table 15 below. If we interpreted the results in terms of production land into nature reserves so that the entire Triple Dividend, we could notice the following benefits: land is protected. The goal was achieved by extending the area of floodplain hay meadows and reinstating • Dividend 1: Avoided losses through conversion of wetland features, which not only protect wading birds, agricultural land into wetlands reducing flood but also reduce the danger of flooding. potential; the resulting reduction in food production due to land reversion is reflected in the aspirational Æ Methodology assessment. Social benefits for flood regulation were estimated under the project to be €3.2 million An ecosystem services assessment (Hölzinger & compared to €1.2 million in the ‘business as usual’ Haysom, 2017) for the site lists benefits as flood (BAU) scenario (although food production private protection, food, health (walking), recreation and value decreased by half). aesthetics, water quality regulation, and wild species diversity. The assessment considered a business-as- • Dividend 2: The health benefits (walking) as well as usual scenario (intensive farming continues) and recreation & aesthetics have substantial economic aspirational scenario which comprises the ’reversion benefits in terms of attracting tourism. Recreation & of arable land to species-rich grassland, restoration of aesthetics alone was estimated to increase from a wet grassland and swamp, extension of woodland and social value of around €134 thousand to €1.9 million planting and restoration of hedgerows’. Benefits of and health (walking) benefits from around €192 ecosystem services and costs of site maintenance thousand to €987 thousand. were quantified as far as possible to a monetary benefit using the benefit transfer approach, over a 30-year • Dividend 3: The wild species diversity, water quality timescale and discount rate of 1.5 percent, though regulation and global climate regulation can be limitations on scientific evidence prevented full considered as co-benefits as they would occur quantification of all services. Outside of the change in regardless of the disaster occurring (or not influenced land management, all other conditions are assumed to by reduced perceptions of risks). The global climate remain unchanged over the 30-year period. and water quality regulation are major benefits items, as they respectively increase the social value from 0 to The assessment report details the approach to €2.8 million and from €15 thousand to €1.5 million. quantify each benefit; in summary health benefits are Wild species diversity also increases from €1.9 million estimated using the WHO Health Economic to €3.4 million of social value. Assessment Tool (HEAT) for cycling and walking; Global Climate Regulation benefits by estimating the • The costs only increase slightly, as the capital and change in greenhouse gas emissions due to land use equipment costs are considerably reduced and change; wild species benefits using the WTP method; labour or site management costs increase slightly. Case Studies Flooding 53 Table 15: Benefits and costs from Chimney Meadows floodplain restoration over a 30 years period (2023-2052) applying a discount rate of 1.5% TOTAL CAPITALISED VALUE BENEFIT SPLIT (PRIVATE VS SOCIAL) BAU -THOUSAND € 2015 ASPIRATIONAL (ASP) -THOUSAND € (THOUSAND £ 2015) 2015 (THOUSAND £ 2015) FIRST DIVIDEND Flood Regulation 100% social 1.18 (0.84) 3.23 (2.29) Food 100% private 1.16 (0.82) 0.63 (0.45) SECOND DIVIDEND Global Climate 100% social 2.84 (2.02) Regulation (only AMB) Health (Walking) 100% social 0.19 (0.14) 0.99 (0.7) Recreation & BAU: 47% private, 53% Aesthetics social 0.25 (0.18) 1.94 (1.38) Aspirational: 1% private, 99% social Water Quality 100% social 0.015 (0.010) 1,477 (1,049) Regulation Wild Species Diversity 100% social 1.94 (1.38) 3.44 (2.44) Total Benefits 4.74 (3.37) 14.56 (10.34) COSTS Capital & Equipment 100% private 1.59 (1.13) 1.04 (0.74) Labour 100% social 1.39 (0.99) 1.54 (1.09) Site & Livestock 100% social 0.097 (0.069) 0.46 (0.32) Management TOTAL DIVIDEND Total Costs 3.08 (2.19) 3.03 (2.15) Total Net Benefits 1.67 (1.18) 11.53 (8.18) BCR 1.5 (RATIO) 4.8 (RATIO) NPV 1.67 (1.18) 11.53 (8.18) IRR/ERR 35.10% 79.18% Source: Hölzinger & Haysom (2017). Original values in GBP shown in brackets, converted using the currency rate 2015: £1 = €1.41 Æ Challenges faced and lessons learned assessment would require collecting and analysing primary data, which is not possible in this study. Given Full valuation of the ecosystem services is presented in the opportunity for further analysis, exploring the effects the assessment report, but these depend on the site’s on agricultural supply chains could help to quantify the environment and climate, so while assessments such as impact to food supply for the broader community to this one can be taken as a guide, specific assessments account for distributional effects. must be conducted for each project. Such a dedicated Case Studies Flooding 54 ADDITIONAL EXAMPLES OF INVESTMENTS IN FLOODPLAIN AND WETLAND RESTORATION FOR FLOOD RISK REDUCTION Additional investments in floodplain and wetland river systems, a floodplain development and habitat restoration have been made in Europe, which provide restoration project in the Netherlands, and the effective ways to reduce flood risk while unlocking establishment of woody barriers and woodlands in ecological and environmental benefits. Such Yorkshire, UK. Outcomes and main lessons learned of investments include two British flood prevention these investments are presented in Box 3 below. schemes that created new wetland habitats or natural Box 3: Additional examples of investments in Floodplain and Wetland restoration A review of investments in floodplain and wetland restoration and generates aesthetic value. The benefit-cost ratio for the across Europe provided inspiring outcomes and lessons project is 18. learned outlined below. A common theme is that these investments reduce the negative impact of floods and The floodplain development project of the Ijsselpoort area, climate change and also generate substantial benefits in Netherlands supported the enhancing of the habitats for terms of ecosystem and biodiversity conservation. species, reduced flood risks and water storage capacity (Natuurmonumenten, 2020). Formed by the upper The village of Tattenhall in Yorkshire, UK is a community at floodplains of the river Ijssel, the Ijsselpoort area is included flood risk with 14 properties flooded during the 2000 in the Natura 2000 network of protected sites due to the flooding season (JBA, 2013). In this context, the Mill Brook presence of large areas of threatened habitats and Scheme (RRC, 2013) was established, which aims at endangered species. The LIFE Floodplain development reducing flood risk for the village through creation of wetland project was launched to tackle the negative impacts of habitats. When the project was completed in 2016, 1.5ha of climate change on the safety of the river and its surrounding reedbed and wet grassland habitats were created, which area, including increasing the floodplain water storage increase floodwater storage and reduces flood peaks. It is capacity to reduce flood risk. estimated that the project will benefit a main road and 22 properties in terms of flood risk reduction. The benefit of the Investment in constructing woody barriers and land creation of the habitat outweighs the project’s overall cost management for flood risk reduction in Pickering, Yorkshire, of €19 thousand, with an outcome Measure of 4a: UK, aimed to reduce flood risk for the town. The project €21 thousand per ha. (Revell, 2018). In addition, the habitat (Nisbet, 2018) was established in 2009 by the Forest also generates environmental benefits by reducing Research and the Environment Agency with a total funding agricultural pollution, improving water quality, and of €4.5 million. The goal was accomplished through the enhancing biodiversity and wildlife protection. construction of low-level bunds and woody dams and the planting of 29 ha of riparian and 15 ha of farm woodlands. As part of the Warrington Flood Risk Management Scheme, The project is effective in terms of flood protection as it the Padgate Brook River Restoration project (McIlwrath, reduces the chance of flooding in a year from 25 percent to 2018) reduces flood risks through the creation of a natural 4 percent for the town of Pickering. During the 2015 Boxing river system and the restoration of a 5 ha reedbed. Aiming at Day storm event, the project protected properties in the sustainability and climate change adaptation, the project local community from being impacted by the flood through was completed without using heavy engineering and a 15-20 percent reduction in the flood peak. At the same provides access to a green space. The project was completed time, it also yields benefits in terms of climate and erosion in 2015 with a total cost of £0.25 million, and it includes a regulation. The benefit-cost ratio for the project ranges from self-cleansing channel that hugely decreases its 5.6 (for the woodland measures), 3.8 (for the combination maintenance costs. The project is expected to protect 226 of woodland, moorland and farm measures), to 1.5 (for the properties from flood during its design life of 100 years. At combination measures plus the large flood storage bund). the same time, it also increases water quality and quantity Case Studies Flooding 55 3.1.3.2. Nature-based coastal and tidal protection dikes show high spatial variability between different coastal locations, but overall, benefits exceed costs Considering sea level rise projections, extreme sea for about 20 percent of the European coastline levels in Europe could rise by as much as 1 m or more segments under a moderate-mitigation and high- by the end of this century. According to the last emission scenario, respectively. Thus, the present PESETA IV report (Vousdoukas, et al., 2020), around natural or hard shoreline protection is economically one-third of the EU population lives within 50 km of optimal for about 80 percent of the European the coast. In the absence of further investments in coastline, under a moderate-mitigation and high- coastal adaptation, annual coastal flood losses for emission scenario, respectively. In urbanized and the EU and UK are projected to grow from €1.4 billion economically important areas, the benefits tend to per year (0.01 percent EU + UK GDP) to €10.9 billion surpass the costs several times. (0.05 percent EU + UK GDP of 2050) and €14.1 billion (0.06 percent GDP) by mid-century for a The examples below showcase several BCAs moderate-mitigation and high-emission scenario, including combinations of grey and green respectively. In the second half of this century, the infrastructure to protect against coastal floods in rise in coastal flood risk further accelerates and by isolation at the coast, and combined risk of coastal 2100 annual coastal flood losses are projected to and fluvial flood in the tidal reaches of rivers. In the reach €110.6 billion (0.24 percent EU + UK GDP in absence of ecosystems such as mangroves and coral 2100) and €239.4 billion (0.52 percent GDP), reefs in Europe, restoration and stabilization of dune respectively. The total number of people exposed to systems represent the main option for nature-based coastal flooding in Europe is projected to rise from coastal risk reduction at European shorelines. €0.1 million to €0.47 million and €0.58 per year by However, coastal protection also considers the effect 2050 under a moderate-mitigation and high-emission of extreme water levels from high tides or storm scenario, respectively, which further climbs to 1.4 surges on the tidal zone or in estuaries where coastal and 2.2 million people per year by the end of the waters can interact with high fluvial flows from inland; century. in such cases restoration of wetlands and the floodplain can also be applied. The section comprises Around 95 percent of these impacts could be a detailed case study from Belgium and other avoided through moderate mitigation and by raising examples from England or Spain (see Box 4). The dikes where human settlements and economically examples also show that coastal measures can in important areas exist along the coastline. The report some cases apply to major urban areas, as well as rural includes a BCA. The costs and benefits of raising coastal settings. SIGMA PLAN - COASTAL PROTECTION OF THE SCHELDT ESTUARY, BELGIUM This case study is an external analysis that was protection, the plan combines engineered or ‘grey’ undertaken with ex-ante analysis that involved infrastructure measures (mainly strengthened dike modelling of hazards and consideration of climate protection and a storm surge barrier) and ‘green’ change scenarios. measures in the form of a network of controlled flood areas (Sigmaplan.be, 2021). The Sigma Plan has not Æ Description been fully implemented yet and some components remain to be realized. In 2015, 1,200 ha of controlled The Sigma Plan is an integrated flood protection plan flood areas were operational and ongoing work was that was first established in 1977 after a major storm expected to continue this area. In a recent report, the surge in the previous year. The Sigma Plan (inspired by alternatives for the update of the Sigma Plan from the the Dutch Delta Plan) offers protection against coastal current situation have been compared through BCA - storm surges as well as floods caused by excessive providing a case of retrospective analysis of an rainfall, protecting 20,000 ha of land bordering the existing project while also being a prospective analysis Scheldt River and its tributaries such as the Rupel, the for changes to that project. The baseline alternative is Nete, and the Durme Rivers. To achieve adequate represented by the measures already implemented Case Studies Flooding 56 plus the completion of the original Sigma Plan, except businesses, infrastructure, and agricultural land. In for the storm surge barriers. In the plan alternatives, a addition to economic damage, the number of higher safety level (lower flood risk) is aimed for by victims is also estimated and valued. implementing additional measures: storm surge barriers at Oosterweel and in the Rupel basin, dike • Effects for agriculture. In some cases, agricultural raising, flood control areas and a retention basin. activities may remain in the flood zone but are subject to restrictions and damage when used as Æ Methodology flood control areas; in other cases, they are not compatible with the function of the inundation area All proposed protection measures are evaluated with and thus are permanently lost. ex ante BCA including discount rates and climate change scenarios up to 2100 (Gauderis, et al., 2005) • Costs for forestry. The potential flooding areas Complete ex-post evaluation is done on those areas contain more than 2,000 ha of poplar forests. If where measures are already completed. Simulations these areas are designed as flood control areas, of hazard scenarios were produced in 2005. The BCA there is no significant impact. Poplars like wet soils is carried out in two phases. First, 10 basic alternatives and can withstand occasional flooding. are evaluated and compared with each other. They include all types of possible measures (storm surge • Costs for shipping. Possible nuisance to shipping barrier, dike raising, room for the river), including can be expected during the construction of a storm plausible combinations of different solution types in surge barrier at Oosterweel. The effects of the small relation to a range of security levels achieved. The storm surge barriers on the Rupel, Nete, and Dijle solution with the best BCR represents the best basic are smaller and not accounted. alternative. A sensitivity analysis is also carried out. In the second phase, the best solution direction is • Ecosystem benefits. NBS generate natural optimized by fine-tuning all the variables within that benefits, split as effects on uses (production solution. The study area is subdivided into five zones functions, regulation functions, and recreation) and and an optimal solution is sought for each zone. The non-use value (including option value, inheritance optimal Sigma Plan is equal to the combination of value, and existence value). optimal solutions of the five separate zones. Costs and benefits accounted in the analysis include the • Recreational value estimated on the basis of an following: estimate of the number of expected holiday-makers on the dikes and their experiential value. • Implementation costs of initial investments plus the maintenance and management costs. A • Visual nuisance for local residents estimated on surcharge of 15 percent was charged for the basis of a key figure for the potential loss of ‘unforeseen’ costs. Value added tax (VAT) is not value of houses and included as a one-off cost in the included. It assumes an annual investment amount construction of the flood zone. of €50 million starting in 2010. Costs for land expropriation are accounted separately (see The alternatives are compared according to three agriculture). evaluation criteria: the net current benefits in the base scenario, the payback period in the baseline scenario, • Risk reduction benefits that consist of avoided and the payback period in the ‘worst case’ scenario. risks and avoided costs. The avoided risks are the The base scenario assumes a discount rate of 4 difference in damage during flooding between the percent and a sea level rise of 60 cm over the next plant alternative and the zero alternative. Customary 100 years. In the worst-case scenario, future benefits hydraulic modelling approach is used to estimate are discounted more strongly and therefore less valued flood areas with a certain probability of occurrence. (discount rate of 7 percent) and the expected sea level Both overtopping and dike breach scenarios are rise is 30 cm. In this scenario, the benefits of the Sigma accounted. The damage for all these floods is Plan will be lower. In both scenarios, average economic estimated as function of the flood extent and depth growth is assumed. over the total number of flooded houses, Case Studies Flooding 57 Æ Results of the analysis by dividends sensitivity analyses. and overall The optimal Sigma Plan consists of a combination of The analysis includes a set of measures for the short flooding areas and local dike elevations. The solution term (always profitable in the short term) as well as found to have the highest NPV and the shortest additional measures for the longer term (will likely payback period consists of a combination of flooding become profitable by 2050). The measures that best areas and local dike elevations (‘Optimal A’, see meet the various criteria discussed above were Table 16). In ‘Optimal B’, those flooding areas are set included in the definition of an optimal Sigma Plan up as ‘controlled reduced tidal areas’, rather than with measures for both the short term (construction simple flood control zones, while ‘Optimal C’ includes 2010) and longer term (for example, 2050). From four additional measures to be built in 2050, including possible plans meeting the criteria, one was selected various configurations of additional flood areas. Full as the optimal solution, subjected to a more detailed engineering details of each solution are given in the full analysis, such as the evaluation of design variants, the report (Gauderis, et al., 2005). search for additional measures for the long term and Table 16: Overview of costs and benefits of all plan alternatives (€, millions in 2004 prices) for optimal Sigma Plan up to 2100 STORM SURGE BARRIER OPTIMAL A OPTIMAL B OPTIMAL C FIRST DIVIDEND Risk reduction benefits until 2100 (€, millions) 748 737 730 752 SECOND DIVIDEND Net benefits until 2100 −5 −8 33 −11 (agriculture, forestry, shipping, ecosystem services, recreational) (€, millions) Costs Implementation costs (€, millions) 397 132 139 149 TOTAL DIVIDEND Total dividend (€, millions) 743 729 763 741 NPV until 2100 (€, millions) 346 596 622 593 BCR 1.87 5.52 5.49 4.97 Payback period baseline (years) 40 16 13 16/51 Payback period worst case (years) No payback 45 33 N.A. IRR/ERR (%) 46.57 81.89 81.78 79.89 Source: World Bank compilation; based on data and information from external sources mentioned above; Baseline scenario: discount rate of 4%, average economic growth, sea level rises 60 cm in 100 years. Worst case: discount rate of 7%, average economic growth, sea level rises 30 cm in 100 years. Compared to the Oosterweel storm surge barrier possible, instead of structural ones. It has slightly higher alternative (complemented with control flooding areas), costs but also generates additional natural benefits, so Optimal A has lower safety benefit; however, the storm the NPV is higher and the payback period is lower. Sub- surge barrier has also much higher implementation alternative C accounts for additional flood control areas costs, realisation time, and no effect on risk upstream. built in 2050 and shows better BCR than the storm The NPV until 2100 is therefore much lower. Sub- surge barrier. The investments in the first period pay for alternative B is similar to A but emphasises the use of themselves in 16 years, and the investments in the natural measures to create flood control areas where second period in 51 years. Case Studies Flooding 58 Æ Challenges faced and lessons learned through the analysis, the Sigma Plan project symbolizes the future of integrating green and grey solutions to The analysis shows that a combination of grey and create environmentally conscious infrastructure and green measures represents the optimal alternative in therefore enhance conditions for future generations. terms of realisation costs over avoided flood damage Considering maintenance or improvement costs can and natural ecosystem services benefits. This is be important as well as to carefully consider options to especially true when considering the costs of updating enhance co-benefits, as shown in other cases in the the defence solutions to cope with the effects of United Kingdom or Spain. climate change in the long-term. As exemplified ADDITIONAL EXAMPLES OF NBS FOR COASTAL AND TIDAL PROTECTION Additional investments were made in the coastal and Plan (BAP) habitat in Alkborough, UK; and construction tidal areas of Europe to reduce flood risk. These of dunes that protected the beaches and coastline of investments include improvement of tidal river defences Barcelona, Spain. Highlights of the investments and the and creation of tidal flood relief area in Sandwich, UK; main lessons learned are showcased in Box 4 below. creation of flood storage area and Biodiversity Action Box 4: NBS for flood risk reduction in coastal and tidal areas A review of NBS that reduce risks in coastal or tidal flooding agriculture and wildfire, Alkborough Flats and the area provides insightful results outline below. A common theme surrounding it often face flood under high tides, with is that the investments all include maintenance or increasing intensity due to sea level rise and sediment improvements over the existing measures and yield movements. In this context, a massive flood storage area substantial co-benefits in recreational value and ecosystem was constructed, which reduced tidal flooding risk for over preservation. 600 properties. It is estimated that without the Alkborough Flats Scheme, the volume of the flood would be 7 percent Located on the right bank of the River Stour, Sandwich is a more during the 2013 tidal surge. The scheme also created historical town with upstream urban areas vulnerable to 370 ha of a BAP habitat, which provides various ecosystem extensive flooding. To reduce flood risk for the local services benefits. The total cost of the project is €16.3 community, the Sandwich Tidal Defence Scheme (Bishop & million (£11.1 million), while its benefits in flood defence Burgess-Gamble, 2018) was established in 2015, with the and ecosystem protection is estimated to be €34.6 million goal to improve the existing tidal river defences and create a (£23.6 million). The BCR of the project is 2.72. 240ha tidal flood relief area. It is estimated that 486 residential and 94 commercial properties are protected by In Barcelona, Spain, coastal dunes are disappearing due to the scheme, with a sea level rise of 50 years included in the erosion and rapid urbanization, which increases the design. At the same time, the scheme also yields social and beaches’ vulnerability to storms, tidal floods, and sea level ecological benefits, as 20 ha of new wetland habitats were rise. The five-year EU project OPERAs (OPERAs, 2020) created for recreational uses and bird protection. With a addresses the issue by constructing and maintaining semi- total cost of 21.7 million pounds, the scheme yields a BCR fixed dunes along Barcelona’s coastline. The project of 10.5. enhances the coastal area’s resilience to storms and floods, which reduce the hazards’ negative economic impacts on The Alkborough Flats Managed Realignment scheme the real-estate and tourism. The construction of the dunes (Manson, 2018) is one of the largest managed realignment is also crucial in terms of preserving the beach and the sites and flood storage scheme in Europe, completed in coast’s ecosystem, which yields substantial ecological co- 2006. Though greatly valued for commerce, industry, benefits. Case Studies Flooding 59 3.1.3.3. NBS for urban flood risk reduction The European Commission has made investments to reduce flood risks in the urban environment In Europe, many cities are vulnerable to flood risks as a through the use of NBS. These investments include result of rapidly growing urbanization and land enhancements to buildings (for example, green roofs consumption, and increasingly variable hydro- and rainwater harvesting), diverting run-off to meteorological extremes. Urban areas located in bioswales or planter boxes, and increasing the area of floodplains along rivers have a higher risk of exposing permeable surfaces through green parking and assets and properties to river floods (EEA, 2017). In permeable pavements (EPA, 2020; Soz, et al., 2016). addition, sudden increase in the volume of water Some examples of investments are highlighted caused by heavy precipitation can lead to overflow in in Box 5 below. the urban drainage system, causing flash floods (Climate Change Post, 2021). Box 5: Investments in urban infrastructure to reduce flood risks Investments in green infrastructures have made storage improvements. The project presents how a public achievements in reducing flood risks in the urban areas and greenspace can help reduce the negative effect of climate provided inspirations. The investments showcased below change for the local community. Modelling shows that the include investments in green infrastructure to reduce project reduces flood risks within the park and in the surface water flooding in Spain and a climate change park in neighbouring residential areas. In addition, the park also the United Kingdom. generates recreational value and enhances wildlife protection, which increases the project’s social and In the municipality of Benicassim in Spain, green environmental benefits. It was estimated that the project infrastructure helped to reduce surface water flooding and yields a total benefit of £27 million, which produces a BCR yielded a number of co-benefits. Supported by the EU, LIFE of 7 comparing to its total cost of £3.8 million (Burgess- CERSUDS (Climate-ADAPT, 2018) is a €1.8 million Gamble, et al., 2018). (€0.99 million EU-funded) project with the goal to promote the use of green infrastructure in urban planning to manage An example presented by World Bank (Soz, et al., 2016) surface water flooding and also improve the resilience of the highlights the experience of Malmö, Sweden, where since Spanish city of Benicassim (European Commission, 2021). 1998 the Augustenborg District underwent an urban The project developed a low-carbon Sustainable Urban renovation program (‘Ekostaden’, or econeighborhood), Drainage System (SuDS), comprising an innovative which transform it into an ecologically, socially, and permeable ceramic tiled pavement surface with a low cost economically sustainable city district. While developing new and a small impact on the environment. The surface reduces community spaces, green roofs were developed to reduce diffuse pollution by preventing water reaching the sewage flood risk. They have been highly effective in capturing system and delays run-off by 45 minutes - reducing peak runoff, and on average intercept half of the annual total flow downstream by at least 72 percent. Co-benefits include runoff from a 9,000 m2 botanical roof garden in the the reduction of manufacturing/installation emissions industrial area. An evaluation (Kibirige & Tan, 2013) through the use of ceramic tiles and improving the quality of concluded that the “open stormwater system in the rainwater stored, but further quantified results are not Augustenborg is well suited to handle current climatic yet available. conditions and a 10 year extreme event. The 100 year extreme event posed the most risk to the area and flooding Completed in 2012, the Mayes Brook River Restoration was evident” (iv). The project has reduced runoff, created project (Restorerivers.eu, 2014) in east London was the first energy savings for residents, improved biodiversity in the climate change park in the UK that reduces flood risks region, and led to socioeconomic benefits such as a drop in through the restoration of a 1.6 km river and flood plain the unemployment rate. Case Studies Flooding 60 3.1.4. FLOOD EARLY WARNING SYSTEMS terms is prone to many uncertainties—the few studies which include a quantitative assessment of EWS An EWS is an integrated tool of hazard monitoring, benefits necessarily rely on assumptions and forecasting, and alert that enables individuals, generalisations due to scarcity of observations. Further, communities, governments, businesses, and others to assessments may take place over different scales— take timely actions to reduce disaster risks in advance from a single urban area to national scope (for example, of and during hazardous events. An FEWS requires (Priest, et al., 2011)). Schroter et al. (2008) estimate hydrometeorological observations and forecasts, the effectiveness of EWS as a function of warning lead monitoring of hazard and risk indicators in relation to time (which however is not the only factor in EWS predefined thresholds, effective channels to effectiveness). Pappenberger et al (2015) estimates disseminate the warning signals, and predesigned the potential monetary benefits of early flood warnings response measures by institutions and communities. based on the continental-scale forecasts produced by Accessibility to remote sensing and local meteoro- EFAS using existing flood damage cost information logical data is key to producing the relevant information, and calculations of potential avoided flood damages. and cooperation among institutions is a critical part of The evaluation is at the EU scale and it is based on the process. theoretical assumptions and global disaster datasets (EM-DAT). The results suggest that there is likely a The engagement of local communities also plays an substantial monetary benefit in this cross-border essential role during the design and operational phases continental-scale flood EWS—about €400 for every of an EWS. Most EU countries have some form of €1 invested. Another study from the International national EWS linked to disaster management Commission for the Protection of the Rhine (2002) operations. At the level of country or region, there are estimates that flood warnings can help businesses both dedicated local systems, such as the advanced avoid 50–75 percent of flood losses. Damage Flandres waterinfo service (run by VMM Belgium), and reduction factors for different response actions were cross-national services, such as the EFAS, launched in estimated from another study (Parker, et al., 2007; 2003. EFAS produces alerts bulletin for all member Parker, et al., 2008), ranging from 6 percent by countries, providing complementary pan-European evacuating property content up to 30 percent medium-range streamflow forecasts and early flood reduction obtained by operating (flexible) flood warning information in direct support to the national defences. At the European level, the factor is estimated forecasting services, with a focus on large transnational around 25 percent, saving an estimated €30 billion river basins. over the next 20 years. In comparison, results from local studies such as the case of Grimma in Germany Assessing EWS costs and benefits in quantitative (described later) show much smaller benefits. THE FLANDRES FEWS (VMM BELGIUM) This case study is a new ex-post analysis under this can identify extreme river flood events with 32-26 project that involved modelling of hazards. hours lead time, though a warning is only released after two runs of the model confirm that the threshold Æ Description for issuing a warning will be surpassed (12 h). This means, in practice, that the effective minimum lead The FEWS of Flandres represents the advanced time is around 20-14 hours. The EWS warning is issued integrated systems running on real-time observations if the flood intensity is expected to exceed the flood (Perera, et al., 2019). The service produces forecasts depth of a 1-in-5-year event. Information from the every 6 hours for the five provinces of West and East service is published through the website waterinfo.be. Flandres, Antwerp, Flemish Brabant and Limburg, The system is not able to forecast pluvial flash floods, shown as green-shaded area in Figure 11 (Brussels is which can develop in just 2 hours. The error on water not included). Red and pink areas on the map are level forecast is 0.3 m on average but can grow to 0.6 susceptible to flooding (more details on flood prone m in some locations; an expert validation is always areas also included in Figure 12). The EWS forecast required before releasing the warning. Case Studies Flooding 61 Figure 11: Areas covered by FEWS in Flanders showing ‘flood-prone’ areas (red—susceptible to frequent floods) and ‘floodable’ areas (pink—at risk of less frequent floods) Source: World Bank analysis; based on flood-prone extents from waterinfo.be There is no official estimate of economic risk of river consistently with the approach described by Priest, flood to Flanders, and no BCA has been produced for Parker, and Tapsel (2011). Hazard forecasting capacity the warning system, though insurance statistics includes monitoring of meteorological variables, suggest €50-€60 million of damage annually due to modelling rainfall runoff, identifying hazard thresholds floods in this region, increasing to €100 million for and evaluation of risk; it can be measured in terms of catastrophic events. For events of higher frequency anticipation and reliability (confidence level (return period of 5–10 years), the combination of EWS, approaching the event). Warning broadcasting refers public communication, and training, including to to the communication between institutional actors conduct maintenance of flood control reservoirs, and dissemination media and is measured in terms of gates, and other infrastructure ahead of flooding, coverage (exposed area or population). Emergency could reduce risk. For larger events, it is less easy to response includes the actions taken by institutions reduce damage. The cost of deploying the service is and communities to reduce or avoid the damage in about €0.3-€0.5 million per year for each province, but exposed areas, such as setting mobile barriers and these estimates are a bit outdated (2010). There are relocating properties, and is measured in terms of many other factors affecting the final price, such as avoided damage. costs IT (website maintenance), therefore it is difficult to give one final measure. As a reference, insurance Assumptions on FEWS anticipation capacity, warning costs consider each house worth €50 thousand in coverage, and loss reduction are developed on the damage. base of evidence from the location of study. According to the national report on flooding (VMM, 2011) people Æ Methodology located within flood-prone areas tend to be more responsive to EWS and to take measures to mitigate To estimate the effect of the EWS on flood risk we the impacts. To reflect this, areas at risk of flooding are apply the JBA Global Flood Model and residential classified with different warning uptake/risk reduction exposure, per the analysis of structural defences, with classes according to the flood probability. In areas the potential damage reduction due to EWS exposed to frequent floods (here termed ’flood-prone’), services estimated using assumptions based on the we assume 90 percent of households act on a information provided by the service providers (VMM), warning received. In areas affected less often (here, literature review and empirical information from real ’floodable’), we assume a 30 percent of households cases. The effectiveness of FEWS implementation act. The specific households modelled as acting on relies on the combination of hazard forecasting, the warning (therefore subject to reduced risk) is warning broadcasting, and emergency response, applied using a stochastic approach, being selected Case Studies Flooding 62 at random. The estimate of total loss for the baseline modelled scenario are consistent with the losses recorded after Based on these assumptions, the benefits are the event of November 2010, before the EWS was measured as reduction in direct losses to assets set up, which caused a loss of approximately €120 compared to the baseline flood risk, where no EWS is million. Based on the above rates of expected action, implemented. A damage reduction factor is applied to it is expected that of 617,314 households the loss model for the properties expected to act, by (approximately 1.4 million people) in Flanders, 7 reducing the maximum possible damage sustained. percent would act on receiving a warning (Table 17). An equal reduction is applied to all properties acting, This leads to an expected loss reduction of between but due to the uncertainty in levels of damage reduction €1.5 million (1 percent of the baseline loss) and €15 due to EWS three options are considered, namely 5 million (10 percent), depending on the assumption of percent, 25 percent, and 50 percent for the reduction damage reduction rate (Table 18). The avoided in maximum damage. damages supply the Dividend 1 estimate; we do not quantify fatalities avoided because the rate of Æ Results of the analysis by Dividends flood fatalities in Belgium is less than 1 per million and overall (EEA, 2020) regardless of EWS. Overall results are presented in Table 19. Table 17: People and households affected by EWS benefits (model estimates) PEOPLE PER NO. OF TOTAL NO. OF TOTAL NO. OF NO. OF PEOPLE PROPORTION HOUSEHOLD HOUSEHOLDS HOUSEHOLDS PEOPLE BENEFITTING BENEFITTING ASSUMPTION BENEFITTING 617,314 1,481,554 2.4 40,592 97,426 7% Source: World Bank analysis; based on external data Table 18: Overall risk reduction (AAL) thanks to EWS for 3 key assumptions (in millions €) EWS SCENARIO, EWS SCENARIO, 25% EWS SCENARIO, 50% BASELINE SCENARIO 5% LOSS REDUCTION LOSS REDUCTION LOSS REDUCTION Total loss, € 161.16 159.6 153.4 145.64 Change, € — −1.55 −7.76 −15.51 % change — −1 −5 −10 Source: World Bank analysis; based on external data Case Studies Flooding 63 Figure 12: Map of flood-prone areas in Flanders, Belgium in terms of frequency of occurrence Source: World Bank analysis; elaboration based on results from the analysis Dividends 2 and 3 for many soft investments such as and storms, indirect benefits of such programs are not EWS are difficult to quantify. While the socioeconomic well documented, and may not be possible to quantify benefits of reduced damage from using EWS are multi- without investigation involving primary data. faceted, such investments are often part of larger DRM projects. Therefore, it becomes difficult to Costs are calculated as annual costs of €0.5 million identify specific benefits that can be unambiguously per province plus an additional €0.5 million estimated attributed to EWS only. Moreover, as has been for the maintenance of the EWS. In total, the total discussed by Tanner, et al. (2015) for Bangladesh, annual cost of service implementation and operation variability in direct benefits (that is, dividend 1) for the five provinces is estimated at around from cyclone EWS comes from timing – maximum €3 million. Compared to the cost of implementing the reduction in damage can be possible if the citizens EWS, the benefits are likely much higher (€1.5-€15.5 receive sufficient time to evacuate and relocate million). themselves and their properties. Especially for floods Table 19: BCR of implementing EWS in Flanders by dividend, over 30 years (Future benefits and costs discounted by 3.5%/year) EWS SCENARIO, EWS SCENARIO, EWS SCENARIO, 5% LOSS REDUCTION 25% LOSS REDUCTION 50% LOSS REDUCTION FIRST DIVIDEND Fatalities avoided Negligible Negligible Negligible Annual average property damage avoided €1.5 million €7.8 million €15.5 million (€, millions) Total first dividend (30 years) (€, millions) €29.1 million €151.3 million €300.6 million COSTS (€, millions) First time capital cost of €2.5 million €2.5 million €2.5 million sensors and monitoring system Maintenance cost €0.5 million €0.5 million €0.5 million Total costs (30 years) €58.2 million €58.2 million €58.2 million BCR 0.5 2.6 5.2 NPV (€, millions) -€29.1 million €93.1 million €42.4 million IRR/ERR -100.0 61.54 80.65 Source: World Bank analysis; based on external data and information Case Studies Flooding 64 Æ Challenges faced and lessons learned investments may lead to wrong estimates of benefits in the absence of data and information. We therefore Many benefits, especially under dividends 2 and 3, have not calculated such benefits for this case study. were not quantified due to the unavailability of data. Moreover, the distributional impacts are unclear and Capturing more details on the proportion of households would be interesting to analyse in terms for example of taking different actions in response to a flood warning last mile communication to ensure reaching most and the effect of those actions and households’ private vulnerable people in remote areas. adaptation investments requires further research to make a more complete triple dividend analysis. The There are interesting studies considering additional sensitivity testing undertaken shows that there is likely aspects to improve the analysis of FEWS. These include to be a minimum uptake required for EWS to show a the implementation and maintenance costs for the BCR greater than 1, especially in areas of Europe investment in FEWS in Grimma, Germany, perfor­ where avoided fatalities are not included due to low mance of the forecast system, and uncertainties in rates of flood-related deaths, and where other damage data for the EFAS. Nevertheless, all analysis dividends cannot be quantified. show substantial benefits of FEWS under different specifications, with various methodologies and for There are additional benefits from EWS that may different types of investments, with considerable belong to dividends 2 and 3. However, calculating benefits found for cross-border floods early warning. those indirect and/or co-benefits to society can be Moreover, complementary investments in public complex and requires sufficient data in a classic DiD awareness or last-mile communication and education framework. For example, there can be social benefits are essential to ensure that benefits from EWS can from reductions in emissions. However, there are many arise and investments in this sense have been confounding factors that contribute towards emissions undertaken, for example, in Poland or as a collaboration reduction and separating the contributions of EWS of Greece and Cyprus. EARLY WARNING SYSTEMS IN THE TOWN OF GRIMMA, SAXONY, GERMANY This case study is an external ex-ante analysis that Æ Methodology involved modelling of hazards. The study of EWS in the town of Grimma, Saxony Æ Description of the case study (Priest, et al., 2011; Meyer, et al., 2012) offers an interesting example of BCA with clear implementation Grimma is a small town of 28,000 people located on and maintenance costs in addition to estimating the the Mulde river, a tributary of the Elbe. In August 2002 benefits of the system. Quantification of EWS costs regionally severe flooding occurred on the Elbe and and benefits is complex, due to the value chain and Danube Rivers, estimated to be at least a 1-in-200- often-shared costs of establishing or improving an year event. Grimma suffered significant damages of EWS, but in this case the scale of the system has €220 million from flooding as deep as 4m as existing enabled this. The system cost €148,000 (one-off) for dike protection was insufficient for this event. Soon setting the EWS and €4,200 (annual) to run the after the experience of 2002, the town council decided service. Assuming a lifetime of 100 years and using a to install an autonomous local warning system, in discount rate of 3 percent, the present value of costs is addition to the Saxon regional one, consisting of many €291,000. Assuming a lifetime of 100 years and using components including: a central flood announcement a discount rate of 3 percent, the present value of costs system including sirens, autonomous SMS information is €291,000. network and 24-h flood information to the television media. From 2010, structural protection with a design The model used to estimate the benefits is a specific level of 1-in-100-years were also installed. A study one developed for the study and considers eight from 2012 compares costs and benefits for both parallel response actions to characterize the measures, individually and combined (Meyer, et al., theoretical range of damage-reducing responses to 2012). We are in the following analysis focusing on the flood warnings. Two of these actions relate to human EWS measure alone. elements (search and rescue, evacuation of people), Case Studies Flooding 65 not evaluated in economic terms. The other six are thousand). related to reduction in flood economic damages and producing flood warning benefits: Æ Results of the analysis by Dividends and overall • Flood Defence Operation: integrity of flood defences are monitored and maintained The FEWS is estimated to reduce the total 100-year event damage only between 2.1 percent and 19.5 • Community-based measures: water prevented from percent, but its cost efficiency in terms of NPV is most reaching buildings where effective likely positive in the long run. Total annual expected damage saved of €408,585 are estimated, which is 73 • Contingent resilience measures: water prevented percent of the estimated total average annual damage from reaching buildings where effective potential (without any flood damage reduction measures). The majority of this (€386,000, 69 percent • Relocation or evacuation of belongings: property of total) are generated by the operation of flood moved away from flood waters defences, and the remaining €22,585 contributed by a combination of business continuity planning, • Watercourse capacity maintenance: freer from evacuation of house contents, contingent resilience debris, less change of flooding measures, community-based operations, and maintenance of watercourse capacity. These measures • Business continuity plan: minimises business however become less effective for more severe floods. interruption losses Æ Challenges faced and lessons learned An estimate of €0.56 million annual average damages has been used as a basis for the application of the The results of this study are valuable as an example of model for Grimma, based on a previous meso-scale a well quantified implementation of EWS integrated flood damage estimation when there were no structural with structural protection. This is in part made possible defences. This total EAD has been calculated for return by the small scale of the system and target area – periods greater than 1 in 50 years as for events below which in turn provides a challenge in scaling the this level no properties are affected, and damage is findings to larger areas and other locations. Potential assumed to be zero. Following the construction of distribution effects of this EWS with integrated structural protection infrastructure, the mean EAD for structural protection include a reduction in damages the town are estimated to be reduced by about 69 to homes and settlements near the river, which can percent to approximately €0.174 million. On average, include people with lower incomes or who are 35 percent is suffered by residential properties (€60.9 experiencing homelessness. EUROPEAN FLOOD AWARENESS SYSTEM This case study is an external ex-ante analysis Æ Methodology that involved modelling of hazards Pappenberger, et al. (2015) performed sensitivity Æ Description of the case study assessments of the potential monetary benefits of EFAS early warnings, considering the avoided damage EFAS was launched in 2003 and produces alerts factors, the performance of the forecast system, the bulletins for all EU member countries, providing discount factors and the uncertainties in the damage complementary pan-European medium-range data. Avoided damage due to early warning is set at forecasts and early flood warning information in direct 32.85 percent when flood defence operation, support to the national forecasting services, with a watercourse capacity maintenance and community- focus on large transnational river basins. The reported based operations are considered together. This cost to establish four EFAS operational centres was increases to a total of 36.68 percent damages avoided €21.8 million, with additional development costs over when temporary resistance measured are 10 years of €20 million (Emerton, et al., 2016). implemented and contents are moved. The study tests Case Studies Flooding 66 warning system performance improvements of 10 property contents. JRC (Thielen Del Pozo, 2015) percent, 20 percent, and 30 percent while assuming averages the damage reduction factor of EFAS at the the forecast model skill remains stationary over the EU level (around 25 percent) over the next 20 years. 20-year period. An EU wide discount factor of 5 percent Indirect losses avoided, counting towards Dividend 1, is applied, with some variation for UK (3.5 percent) and Dividend 2 and 3 benefits were not included in and France (4 percent). An uplift factor of 2.54 and JRC’s analysis of EFAS due to difficulties quantifying 1.75 were applied to account for indirect costs, applied indirect losses avoided and the potential provision of as an uplift to EUSF and EM-DAT reported direct costs earlier aid to at risk people. to estimate event damages. Æ Challenges faced and lessons learned Benefits of EFAS warnings are estimated by: 1) calculating correctly warned events and missed events This example highlights the challenges in estimating against an EU flood damage map, and 2) against EUSF the costs and benefits of EWS, which derive from and EM-DAT damage estimates. These benefits were several complex factors - especially in this large-scale compared against the installation and running costs of case. These include whether a forecasting system the EFAS system. No assessment of a single event is already existed and in what form, the scale of carried out by Pappenberger et al. (2015). forecasting region, temporal lead time required and enabled, in addition to human and resource factors Æ Results of the analysis by Dividends which, in an event, can limit the efficacy of response and overall actions even in cases of effective warnings being issued. The sensitivity study of Pappenberger et al. The results show that there is likely a substantial (2015) shows the significant uncertainty associated monetary benefit in this cross-border continental- with assessing benefits and costs of FEWS – scale flood EWS. The conservative base scenario uncertainty in the percentage of damages avoided due applied suggests that a BCR of 159 is generated after to actions following a warning can change the relative 20 years of operating EFAS. With improvements in monetary benefit of EFAS by over 100 percent, forecast performance this ratio could reach 202, and assumptions on forecast performance by up to around even up to 400 (400 Euro return for every 1 Euro 70 percent, and uncertainty in estimated event invested). The analysis suggests that 37 percent of damage by over 150 percent. Moreover, the damages could be avoided due to the operation of the distributional impacts are unclear and would be EWS, resulting mainly from a 32 percent reduction interesting to analyse in terms for example of last mile thanks to avoided damages by warning dependent communication to ensure reaching most vulnerable flood defences, and 5.7 percent reduction thanks to people in remote areas. residual damages avoided by moving and evacuating ADDITIONAL EXAMPLES OF EWS BUILDING AND TRAINING FOR IMPROVED FLOOD RESPONSE A number of additional investments sought to improve warning systems. Projects include investments in a awareness and capacity for preparedness that could cross-border EWS system in Greece-Cyprus with provide lessons learned and inspirations. In fact, educational tools and a comprehensive mapping building risk awareness and capacity of governments, system PANDA in Poland. Highlights and main emergency services and the public to respond to lessons learned of these investments are presented floods is an important component of increasing in Box 6 below. resilience and support the operation of effective Box 6: Varied investments in EWS and capacity building for flood response across Europe A review of investments in EWS and capacity building for reach the last mile can be very beneficial for disaster risk flood response across Europe provided a number of lessons prevention and preparedness. learned and inspiring achievements outlined below. A A Greece-Cyprus Interreg-funded project implemented common theme is that individualized early warnings to 2017-2020 aimed to bridge the gap between scientific Case Studies Flooding 67 knowledge and public action (European Commission, 2020; online, digital and comprehensive rainfall mapping system World Bank, 2021). It developed an online Environmental in Poland. It is designed to help develop urban stormwater Risk Management Information Service that provides tools and drainage systems that better protect Polish towns, and information on flooding to business owners, policy and cities and their residents against the effects of heavy rainfall. scientific communities, and the general public. By offering Based on three decades of data, the project developed an EWS, crowdsource photos, flood-risk maps, entertaining online rainfall intensity calculator, making it easier to assess videos and education games for families, the project enables potential threats in any area of the country. The data is the public to have access to scientific information on natural accessible through a personal PANDA account, which any disasters and thus increase their chances of survival when a interested party can open online. The data allows local disaster strikes. governments and companies to plan preventive actions and better equip infrastructure works and buildings against The Polish Atlas of Rains Intensities (PANDA) is the first heavy rainfall or flooding. 3.1.5. PROPERTY-LEVEL PROTECTION (PLP) coordinated effort to mitigate flood risk at the property Property-level flood protection is the installation and level over many properties and to represent the deployment of flood resistance measures to prevent potential impact of such a large-scale investment in water from entering individual properties and resilience PLP measures. measures to limit the damage caused once it has entered (White, et al., 2018). Resistance or dry proofing PLP measures were implemented from 2008 to 2011 measures include door barriers, nonreturn valves, and under a government grant scheme in England to airbrick covers, while resilience or wet proofing evaluate the effectiveness of PLP (Peter, et al., 2014). measures include waterproof plaster. Pumps can also Total funding of £5.2 million (€6.55 million in 2008 be considered to remove water from properties to prices) was awarded to 63 individual PLP schemes, reduce the amount of time they are flooded, which in offering practical flood protection solutions to 1,100 turn reduces the amount of drying time and overall properties. Based on a sample of 115 properties which damage. Other retrofit actions include moving ground had deployed their measures since installation, PLP floors electrical circuits higher to avoid damage at low measures had a positive impact (prevented ingress or flood levels, or changing floors and wall coverings to be allowed only limited ingress of water) at 79 percent more resilient when submerged. properties while 21 percent experienced no positive impact. Potential co-benefits of PLP can include There is limited information available on examples of increased property value for those properties with PLP being applied in EU MS. To present the potential improved defences, the potential to increase energy costs and benefits of another form of flood risk efficiency, but these are more likely when more reduction and compare the BCR, the decision was substantial PLP or retrofit works are implemented (for taken to simulate the hypothetical application of PLP example, relocating electrics circuits above the in a prospective analysis. This is applied to a selected potential flood level, water-resistant plastering, and flood-prone urban area, which would represent a flooring, or perimeter protection). THE SIMULATED EFFECT OF PLP IN NORTHERN ITALY This case study is a new ex-ante / hypothetical is often prone to both surface floods and river floods. analysis under this project that involved modelling We chose two locations on the Adriatic coast where of hazards. recent flash flood events caused severe impacts: Lignano Sabbiadoro and Rimini (two seaside towns Æ Description with strong touristic vocation). Lignano Sabbiadoro was hit in September 2017 by a severe urban flooding North-Eastern Italy consist of a large floodplain limited caused by two intense rainstorms that produced a by the Adriatic Sea. It is a heavily urbanised area, cumulative rainfall depth of 280 mm, estimated to showing some of the highest rates of soil sealing, and it correspond to a return period of 50–100 years. The Case Studies Flooding 68 rainstorms caused the flooding of large portions of the would be required to reduce the change of hazard urbanized area (Samela, et al., 2020). Rimini was hit in occurring in this context. While there are ongoing June 2013 by intense precipitation (148 mm in 4 efforts in this direction, PLP could be the most easily hours), generating torrential floods on urban roads and quickly implemented risk reduction measure in which caused 2 deaths and widespread economic some locations (see case studies location for modelling damage. Major structural and infrastructural changes PLP measures in Figure 13). Figure 13: Case studies location for modelling of PLP measures: Lignano and Rimini are small towns in Italy located on the North-Adriatic coast Source: World Bank analysis; based on OpenStreetMaptopographic map Æ Methodology would encompass floodproofing components such as raising electrical sockets and installing waterproof A study was conducted by ECHO (2014), with support doors/barriers and boards to deploy in advance of a from Politecnico di Milano about the cost-effectiveness flood. Above 1.67 m, there is no adjustment to the of PLP in Italy to prevent pluvial flood damage, curve. No adjustment was made to the frequency or accounting for different types of measures (flood severity of flooding for the study area, as no change in proofing of components, flood walls, and relocation) large-scale flood protection (for example, flood banks over three classes of buildings. We use the results from or barriers) was included. We consider a period of 30 this study in a simulation of PLP effectiveness in the years to sum up the total benefits of PLP context of selected flood locations. The same global implementation. flood model as applied for previous flood case study analyses was applied. To represent the impact on AAL The total cost of PLP measure implementation is and the exceedance probability curve, property calculated based on the unitary prices estimated for vulnerability curves were adjusted to represent the Italy by the study mentioned, expressed as euro per higher level of flood required before inundation would m2 per year (see Table 20).The annual cost of each occur. measure is obtained by dividing the one-off cost by the expected lifespan of the intervention. The unitary It is expected that PLP measures are effective at lower costs are first multiplied by the number of years (30) flood depths and less effective as flood depth increases. chosen to compare the benefits. Then they are It was assumed that measures where flooding is less multiplied by the total exposed area, identified as the than around 1 m would encompass floodproofing sum of buildings’ footprint areas. Only residential components such as raising electrical sockets and buildings are accounted. Rimini has about 1 km2 of installing waterproof doors/barriers and boards to built-up area located in areas prone to flood depth deploy in advance of a flood. It was assumed that between 0.5 and 1 m, while Lignano has 0.33 km2 measures where flooding is less than around 1 m (see Table 21). Case Studies Flooding 69 Table 20: Unitary costs of PLP measures as estimated for the Umbria case study. Adapted from ECHO-SUB-2014-694469 UNIT COST OF MEASURES (€/M2) OVER 30 YEARS BUILDING CLASS FLOOD PROOFING TO FLOOD WALL MEASURE RELOCATION OF BUILDINGS COMPONENTS Class ‘A’ 75 112 5,401 Class ‘B’ 1163 909 47,240 Class ‘C’ 525 398 17,458 Source: World Bank analysis; Adapted from ECHO 2014 TYPE OF MEASURE (CONDOMINIUM APARTMENT) COST (30-YEAR LIFE SPAN) (€/M2/YEAR) Electrical measure 8.57 Interior plaster measure 16.5 Plumbing/sanitary measure 6.5 Floor measure 3.47 Source: ECHO (2014) Æ Results of the analysis, by dividends reduction, though the relationship is not linear given and overall differences in flood depth at individual properties. The lower value is compatible with the percentage Dividend 1 comprised avoided damages, calculated reduction estimated in a detailed analysis by property according to the reduction in vulnerability applied type in the Umbria example Politecnico di Milano across all property types with an assumption of 100 study, which estimates an average damage reduction percent uptake of measures at properties affected by as 1.3–3.4 percent for ‘flood proofing to components’ flood. Across all Admin 3 sub-district boundaries of and 2.9–4.6 percent where ‘flood walls’ were included. Rimini and Lignano, the damage reduction was Fatalities are not quantified due to the low rate of flood approximately 7.2 percent. Assuming 50 percent fatalities regardless of PLP. uptake, this might be closer to 3.6 percent risk Table 21: Summary of results for PLP scenario simulation compared to baseline. Both locations show a reduction in annual expected losses close to 3.5 percent for PLP measure implementation with percent uptake LOCATION (MUNICIPALITY) RIMINI LIGNANO Residential buildings footprint area (km ) 2 1.00 0.33 Baseline damage (€, millions) 10.30 0.62 Damage with PLP if 100% uptake (€, millions) 9.60 0.58 Difference with 100% uptake (€, millions) 0.76 0.035 Source: World Bank analysis; based on external data and information Case Studies Flooding 70 Dividends 2 and 3 for PLP measures may include the not able to calculate dividends 2 and 3. However, benefit of reduced displacement of residents from under certain assumptions, we can reflect on the affected households (therefore reduced cost of potential sources of those dividends. For example, shelter) and reduced business interruption to there can be lower displacement which can be a commercial properties (due to services being able to source of benefits. Appropriate interventions can restart earlier after a flood than would be possible reduce their stay in temporary shelters and this without PLP). There may also be a reduced volume of dividend arises from their shorter stay in shelters bulky waste due to reduced damage and replacement (that is, the difference in the durations of shelter stay of contents and decoration/furnishings (though this is without and with interventions). While this structure quite a micro impact, likely not quantifiable) and follows the classical DiD framework, its calculation is reduced displacement of homeowners (in terms of heavily contingent on the availability of data or both number of people and duration of being appropriate proxies, absence of which restricted our displaced). Due to lack of available data and calculation of such benefits. Overall results are information on indirect and/or co-benefits, we were presented in Table 22. Table 22: BCR for PLP in NE Italy per dividend (30 years lifespan, benefits discount rate 3.5%) RIMINI LIGNANO 100% UPTAKE 100% UPTAKE FIRST DIVIDEND Fatalities avoided Negligible Negligible Annual average property damage avoided 0.7 0.035 (€, millions) Total first dividend over 30 years (€, millions) 21 1.0 First cost item Annual cost of PLP measures (€, millions) 12.9 4.0 Total dividend over 30 years (NPV) (€, millions) 13.4 0.7 Total cost over 30 years (€, millions) 387 120 BCR 0.035 0.006 Source: World Bank analysis, based on external data Æ Challenges faced and lessons learned specific range of hazard intensities. Moreover, both case study areas have a relatively high density of units The BCR from this case study is smaller than expected in exposed areas, which means the total floodproofing and overall discouraging the implementation of PLP costs are much larger compared to small-density for flood loss mitigation in the two case study areas. settlements along the river network. These observations Interestingly, the BCR for individual PLP measures was highlight the need for caution when transferring the estimated as always greater than 1 in the reference results of BCA from one specific measure and location study; however, those estimates are produced to different contexts. Investing in PLP for flood loss accounting for river floods and dam failure scenarios mitigation is important because it provides a sense of that would generate higher hazard intensities and thus financial security for these densely populated areas in larger amounts of losses, compared to pluvial floods. In a disaster. Such private initiatives can enhance the our assessment, we account for damage triggered by property value and reduce the regular maintenance pluvial floods only, because the two locations do not costs of the properties with such protections. present significant river flood hazard, and only for a Case Studies Flooding 71 3.1.6. OVERVIEW OF BCA FOR FLOOD RISK dividends are recognised and described in the text, REDUCTION the generalisations and assumptions that would be required in the absence of data resulted in a decision This section has demonstrated the variety of flood to not quantify those. However, additional examples protection investments and introduced several from the literature where detailed prospective or examples of BCA. The BCAs have been presented for retrospective economic analyses have been structural and nature-based risk reduction measures, undertaken are used to demonstrate the additional EWS, and catchment scale to property level. benefits of these dividends in the context of flood risk reduction. Quantified benefits of structural schemes focus on avoided property damage (dividend 1), though The range of BCRs presented for the included studies additional dividend 2 benefits may comprise stimulus strongly demonstrates the range of possible estimates of local/regional economy and supply of materials (for between different types of flood risk reduction and example, gravel production in the Odra River example). within the same type as well as the strong influence on The examples of NBS demonstrate the broad range of BCRs of the assumptions and values applied to benefits including impact on carbon storage, amenity, develop costs and benefit value estimates and the and recreation value and therefore health benefits, variable inclusion of individual benefits. The structural water quality, and timber production, though defence cases here provide a range of BCRs <1–5, conversion of grassland to other habitats can also though the lower estimates are subject to a lack of result in a negative benefit of lost agricultural dividend 2 and 3 information. The NBS examples, with production. The NBS examples also tend to include their quantification of myriad additional ecosystem assessment of multiple options for the NBS component benefits provide estimates of BCR generally <1–5, as well as combination with structural options, resulting but in one case up to 10. The examples of FEWS in comparison of NPVs for those different options. provide BCR ranging from <1 to 15 depending on the estimated proportion of people acting upon Unfortunately, in the examples identified for detailed receiving a warning, but due to the large component assessment of avoided damages in this study of human behaviour in reacting to a warning and (Machlandamm, Flandres FEWS, and PLP in NE Italy), the various actions people might take, there is there was insufficient information to support significant uncertainty around these estimates. quantification of dividends 2 and 3. While the potential Case Studies Flooding 72 3.2. Earthquakes 3.2.1. SUMMARY OF FINDINGS FOR There are several options for governments to effectively EARTHQUAKES reduce earthquake risk and enhance their earthquake resilience. These include targeted investments into buildings and infrastructure strengthening, Earthquakes are extremely common across the globe. development of EEWS, and improvement of emergency The National Earthquake Information Centre of the response capacity and recovery efforts, among others. United States Geological Survey (USGS) locates about The European Commission has made investments that 20,000 earthquakes each year, which is equivalent to aim at reducing human and economic losses caused roughly 55 earthquakes recorded per day (USGS, by earthquakes. The European Association for 2021). In many locations, seismic hazards pose serious Earthquake Engineering (EAEE) was established to intermediate-term risks to a society’s health, safety, promote cooperation between regions in the field of and economic viability. For example, structural earthquake engineering, which serves a crucial role in damage to buildings, fires, damage to bridges and mitigating the impacts of earthquakes in Europe highways, initiation of slope factors, liquefaction, and (European Union, 2021). Financed by the Horizon tsunami are common impacts caused by an 2020 programme of the European Commission, the earthquake. In 2011, FEMA initiated a four-phase Real-time earthquake rIsk reduction for a reSilient study (FEMA, 2020), which was aimed at informing Europe (RISE) project is a three-year program with the community officials and the public about the value of objective to enhance the scientific understanding of adopting the International Codes (I-Codes) to increase earthquakes and Europe’s capabilities in future resilience against natural hazard events. To simulate earthquake prevention (RISE, 2021). the losses avoided due to prevention of physical damage to buildings and contents, the Building Codes Several different economic approaches have been Save Study comprehensively examined records of used to quantify the social and economic losses buildings constructed from 2000 to 2016, including caused by earthquakes and the benefits of earthquake the business parcels, mapped hazard exposure, and risk reduction investment, yet the infrequent building code histories nationwide, notwithstanding occurrence of earthquakes requires careful data limitations. Results from the study show that total interpretation of the results of an earthquake-related losses avoided amounted to an average of €439 BCA. A recent report by NIBS (2019) showcases a million7 (US$484 million) for floods, €54.2 million comprehensive BCA of natural hazard mitigation in the (US$60 million) for earthquakes, and €1 billion United States and included BCRs of retrofit measures, (US$1.1 billion) per year for the whole country. which varied widely depending on the measure and Reduction in property losses associated with use of hazard level but averaged between 2 and 24. Some modern building codes for 2000–2040 was estimated studies (Pohoryles, et al., 2020) have shown that to be around €119 billion (US$132 billion). combined energy and seismic retrofit investment is economically efficient, as the combined method will 7 Original values were in US dollar. Case studies Earthquakes 73 result in a significant reduction in the payback periods In this section, we demonstrate benefit-cost in moderate to high seismicity region compare to assessments for seismic retrofitting, EEWS, and separate investments. Investments in Earthquake increased responder capacity. BCRs for the different Early Warning System have also proven to be types of interventions are shown by a combination of economically beneficial, yet for systems that depends detailed case study analysis and review of past BCA, on eyewitness accounts of earthquake shaking, including both prospective and retrospective types of socioeconomic and literacy factors can have a strong assessments. Table 23 summarizes main data and influence on the effectiveness and accuracy of the information sources. system (Seismological Society of America, 2021). Table 23: Overview of data and information sources for earthquake analysis INVESTMENT CASE STUDY DATA SOURCE NAME AND REFERENCE Seismic Seismic risk • Hazard model based on ESHM13 strengthening prevention in • Exposure and vulnerability models based on GEM Foundation’s 2018 Global Risk of buildings Italy Model and • Information on the intervention type obtained from the report ‘The Italian National infrastructure Seismic Prevention Program’ • Data provided by the Civil Protection Department Seismic Improvement • Hazard model based on ESHM13 strengthening of education • Aggregated national counts and occupants based on Global Program for Safer of buildings facilities in Schools (GPSS) GLOSI statistics and Europe • Average area and replacement value of buildings obtained from the construction infrastructure costs from the SERA project • Risk analyses for the baseline and retrofitting case performed with the OpenQuake engine • Primary energy consumption based on the comprehensive study of building energy renovation activities and the uptake prepared for the European Commission • Data for educational facilities obtained from the European Commission -Energy: Long-term renovation strategies • National and European emission factors for consumed electricity and fuels for heating and hot water taken from Covenant of Mayors Technical annex to the Sustainable Energy Action Plan (SEAP) template instructions document • Data from EU buildings database, EU countries’ 2013 cost-optimal reports, and EU countries’ 2018 cost-optimal reports - Energy, obtained from the European Commission - EWS Earthquake • Total investment information from the ‘Danube Cross Border System’ project for early warning EEWS cost, half of which is assumed to be applied to Bucharest in Bucharest • Data from the United States (Strauss and Allen methodology) for cost of one train car and cost of maintenance of EEWS, adjusted to Romanian consumer price indexes • Eurostat symmetric input-output tables for construction sector macroeconomic benefits. The EU estimation for construction sector input of every €1 yields €0.47 of value added to other industries. This is an indirect and direct economic value added from the construction or installation of sensors and other infrastructure for EEWS Case studies Earthquakes 74 Responder Benefits of • Modex and European Union Civil Protection Team (EUCPT) training costs, capacity knowledge supplied by DG ECHO and course organisers building network • Post-disaster needs assessment (PDNA)/rapid disaster needs assessment investments (RDNA): reports and interviews with PDNA leaders during • Further data requested of Albania and Croatia governments but not received. earthquake Uncertainty on certain assumptions can be further reduced with this information (Albania and Croatia) • Interviews with Croatia civil protection personnel and the Zagreb damage assessment leads • EUCPT final reports for Albania deployments (September and Novovember 2019). Obtainable, as the author of this section was deployed as an EUCPT member on both deployments (Josh Macabuag) • Further references  GRADE reports (Global Rapid post-disaster Damage Estimates, World Bank Group internal documents) for both case study events.  CSES (Centre for Strategy & Evaluation Services), Resilience Advisors Network, Evaluation Study of Definitions, Gaps, and Costs of Response Capacities for the Union Civil Protection Mechanism.  Goretti A., Molina Hutt C., Hedelund L., 2017. “Post-earthquake Safety Evaluation of Buildings in Portoviejo, Manabí Province Following the Mw7.8 Ecuador Earthquake of April 16, 2016.” International Journal for Disaster Risk Reduction March 2017.  Woo, G. 2019. “Downward Counterfactual Search for Extreme Events.” Frontiers in Earth Science December 2019.  Other references for specific figures assumptions, as provided in the calculation spreadsheet Source: World Bank analysis; based on external information Most models can be used to assess infrastructure considers all possible earthquake but often ’averages investments. The common platform that is used to out’ extreme consequences caused by rare events. evaluate earthquake hazard and earthquake risk in Europe is OpenQuake—Global Earthquake Model’s Earthquakes can cause widespread societal and computational engine. Other analysis frameworks that economic losses in a single event, but their infrequent are used to quantify earthquake consequences to occurrence poses challenges when conducting BCA building stock and infrastructure are HAZUS (Kircher, and interpreting the results. There are several different et al., 2006) and FEMA P-58 (Hamburger, et al., 2012). approaches that have been used to quantify the For the Italy and schools across Europe analysis, the benefits of earthquake risk reduction investment and OpenQuake platform and ESHM138 were used. care must be taken when selecting and interpreting Moreover, the European Commission has purposed a the results of an earthquake-related BCA. A recent methodology (European Commission, 2020d) to report by the NIBS (2019) showcases a comprehensive evaluate the combined approach of both seismic BCA of natural hazard mitigation in the United States improvement and energy efficiency of a building. The and included BCRs of retrofit measures, which varied common metrics used for quantification of benefits widely depending on the measure and hazard level but are the decrease in losses for a particular earthquake averaged between 2 and 24. Some studies have shown scenario and decrease in AALs, that is, reduction in that combined energy and seismic retrofit investment losses from all possible earthquakes that can occur in is economically efficient, as the combined method will a given year weighted by their probability of occurrence. result in a significant reduction in the payback periods While the first approach illustrates benefits for one in moderate to high seismicity region compare to plausible earthquake scenario without accounting for separate investments. its probability of occurrence, the second approach 8 While the ESHM13 model was used for this analysis, it is not consistent with the procedures and the criteria used by the Italian seismic prevention program to identify the areas where the program is applicable, define the initial and the final safety conditions, and so on. The prevention program used the official 2004 seismic hazard model since 2004. Case studies Earthquakes 75 BCA generally yields net benefits, although this varies in Figure 14, Figure 15, and Figure 16. based on various considerations. In fact, a lack of quantitative data to calculate dividends 2 and 3 as Figure 14 shows the distribution of benefit-cost ratios well as lack of prioritized assets to consider may lead (BCRs) for earthquake investments, based on a five- to some results where BCRs are smaller than 1. A number summary: minimum (shown in orange), first general message is that detailed risk assessments and quartile, median (shown in red), third quartile, and consideration of different types of assets are essential maximum (shown in orange). The outliers are shown to consider in the analysis. More details are included as dots. Figure 14: Findings of BCA for earthquakes (BCRs) Source: World Bank analysis; based on external data and information; presenting in part results from literature based on external and World Bank reports (2 Seismic strengthening results from World Bank (2018a; 2019c; 2019a; 2019d)) Figure 15 presents boxplots that display the distribution median (shown in red), third quartile, and maximum of NPVs (in millions of euros) for different types of (shown in orange). Extreme values are excluded from investments in earthquake based on a five-number the top graph and included in the bottom one. summary: minimum (shown in orange), first quartile, Figure 15: Findings of BCA for earthquakes (NPVs) Case studies Earthquakes 76 Source: World Bank analysis based; on external data and information; presenting in part results from literature based on external and World Bank reports (2 Seismic strengthening results from World Bank (2018a; 2019c; 2019a; 2019d)) Figure 16 presents boxplots that display the minimum (shown in orange), first quartile, median distribution of ERRs for different types of investments (shown in red), third quartile, and maximum (shown in earthquake based on a five-number summary: in orange). The outliers are shown as dots. Figure 16: Findings of BCA for earthquakes (IRRs) Source: World Bank analysis based on external data and information; presenting in part results from literature based on external and World Bank reports (2 Seismic strengthening results from World Bank (2018a; 2019c; 2019a; 2019d)) Seismic strengthening of buildings and infrastructure usually require large capital investments and are is intended to improve the safety of buildings (or therefore generally undertaken only when there are infrastructure) and its occupants in an earthquake. legal obligations or allocated funds. This is the case Physical earthquake risk reduction can vary in scale particularly for cultural buildings and governments in and cost, from small works such as securing certain countries such as Italy that have implemented bookshelves and equipment against improving the large programs for retrofitting of infrastructure and structural safety of the entire building by retrofitting safeguarding cultural heritage. structural or non-structural elements. Major retrofits Case studies Earthquakes 77 • Case study 9 (new analysis under this project, ex • Case study 11 (new analysis under this project, ex post (Dolce, 2012; JBA Risk Management, 2021)): ante9): The analysis of hypothetical investments The analysis of the National Plan for Seismic Risk into seismic strengthening and energy efficiency in Prevention implemented by the Government of education facilities in European earthquake-prone Italy 2010–2016, focusing on investments countries shows mixed results. However, the strengthening private residential and mixed-use analysis overall supports the message like on the buildings and retrofitting of public buildings, analysis for Italy that investments become zyielded mixed results. The analysis considering particularly economically viable when considering AALs found BCR > 1 for local strengthening the potential impact of rare events (that is, PML interventions and BCRs less than 1 for other versus AAL), that investments in school buildings intervention types, while the probable maximum should be prioritized based on spatial vulnerability, loss (PML) analysis (475-year return period, rare and that energy efficiency measures combined with event) found BCRs higher than 1 for all inter- earthquake risk reduction can allow for substantially vention types for public buildings (BCRs of 1.65, higher net benefits than when investments are 1.66, and 3.5 for, respectively, seismic upgrading, undertaken separately (BCRs range of 0.93–1.46 demolition and reconstruction, and local depending on countries and type of analysis, strengthening; NPVs of €268.6 million, €13 million, NPVs of −€63.3 to €422 million, IRR/ERR of −7.19 and €65 million, respectively; IRR/ERR of 64.68, percent to 46.11 percent). For certain countries 65.66, and 250 percent, respectively). Results such as Greece, Romania, Bulgaria, and Slovenia, differed between interventions considered and the investments would be economically viable between public and private buildings. Overall, the based on PML and AAL analyses. Interestingly, analysis shows that (1) policy objective (rare event interventions are economically beneficial across versus average building lifetime) and related the board, with only some exceptions, for methodology affect possible results, (2) comprehensive investments in universities. Given interventions focusing on certain types of buildings the nature of the results from the regional and choice of certain interventions (considering analysis, it is recommended that future BCAs are broader economic benefits) can yield higher net conducted at an asset level to more precisely benefits, and (3) interventions in private buildings identify education facilities that are economically were mostly found to be economically viable. viable to retrofit. • Case study 10 (World Bank PAD analysis (World • Case study 12 (World Bank PAD analysis (World Bank, 2018a; 2019a; 2019c), ex ante): The Bank, 2019d), ex ante): The analysis of the World analysis of three projects in Romania, financed by Bank project in Turkey focusing on the the World Bank, focus on the upgrade of critical reconstructionand retrofitting of around 350 disaster and emergency response buildings yielded schools yielded a BCR of 1.53 (NPV €120.4 variable net benefits given different interventions million). The calculations of energy efficiency and projects and varied among earthquake benefits could be quite specific given recent scenarios (BCRs in the range of 1–2; NPVs from benchmark data on characteristics of buildings that negative to €27 million, IRR/ERR from negative to the analysis could base itself on. 73 percent), with a likely underestimation due to the lack of quantitative measurement of second EEWS consist of physical infrastructure and software and third dividends (energy audits would be that can alert stakeholders about an incoming necessary to have quantitative assessments of the earthquake seconds to minutes before they latter). These second and third dividends would experience the resulting strong shaking, which allows comprise, for example, wider benefits in terms of for actions (moving to a safer location, shutting off gas economic activity due to adapted investments from pipelines, switching signals to avoid entering a risky the private sector linked to expectations of better area, and so on) to decrease detrimental impacts from emergency response buildings and capacity or shaking. The Euro-Mediterranean area has a strong energy efficiency and linked climate benefits of need for effective EWS: only a few countries have improved buildings, among others. operational systems in place (Romania and Turkey) 9 Data on schools and modelling across Europe, GEM 2021. Case studies Earthquakes 78 and one study found that only 44 percent of examined softer investments. Although the case studies had to target sites (Cremen, et al., 2020) benefit from warning make a number of assumptions, overall, the intellectual times long enough to accommodate effective actions thinking on how to account for the various potential from stakeholders. This is being addressed by projects dividends of softer investments is a great contribution such as Horizon 2020 TURNkey10 but country-specific to the literature. actions would likely have to be highly beneficial to find adapted measures. • Case study 14 (new analysis under this project, ex post (Perry, 2004)): The analysis of investments in • Case study 13 (new analysis under this project, ex training for emergency responders and response post (European Union, 2020)): The analysis of the coordination through the UCPM Knowledge Network, EEWS in Bucharest as part of the DACEA program with focus on two disaster interventions during disaster partially funded by the EU aims at providing events (Albania November 2019, Croatia March 2020) warning to authorities to shut down critical showed net benefits of impact realized on the ground infrastructure (nuclear power plants, trains, and and additional softer benefits. The events were so on). Due to the lack of data for critical different in magnitude, assets, and lives lost, as well as infrastructure, the analysis for the EEWS investigates international assistance (in Albania damage incremental and conservative losses avoided. assessments were supported and UCPM-trained These include the value of one life loss avoided due rescuers helped on the ground whereas in Croatia to appropriate warning and the cost avoided of one there were no international rescuers, but local staff train being derailed. In addition, the value of had been trained under the UCPM). However, in both construction to the broader economy is included as cases, the BCRs are greater than 1 (1.9 in Albania, 1.1 an additional benefit. This conservative analysis of in Croatia) as well as NPVs (€5 million and €0.3 million) the existing EEWS yielded a BCR greater than 1. and ERRs/IRRs (88.33 percent and 8.82 percent). All It has to be noted, however, that few methodologies three dividends have been considered and it has to be exist for economic valuation of EEWS and therefore noted that in the case of Albania the first dividend was this study should be considered as exploratory highest given the benefits that could be reaped owing research. With the conservative assumptions, to rapid damage assessments (such as saved costs of the study found a BCR in the range of 3.4–11.1 temporary shelter/accommodations) and in the case (NPV of around €19 million linked to BCR of 7, of Croatia where such benefits could not be linked to IRR/ERR of 617 percent). Although the benefits international assistance, the third dividend was found are likely to be underestimated given the lack of to be highest (job security and salary increases for information/data, the issues of needed com­ qualified staff). plementary investments and therefore potential double counting still remain in general 3.2.2. SEISMIC STRENGTHENING OF for EWS investments. BUILDINGS AND INFRASTRUCTURE Responder capacity building affects the effectiveness Seismic strengthening of vulnerable buildings and of disaster response, as the latter is directly associated infrastructure is one of the main ways to reduce with the skills of the responders at a disaster site, as existing earthquake risk. Seismic strengthening is well as their effective coordination with other resources intended to improve the safety of buildings (or deployed (Sinclair, et al., 2012). It is therefore essential infrastructure) and its occupants in an earthquake. for authorities to establish emergency management Physical earthquake risk reduction can vary in scale training and live exercise programs to build capacity of and cost, from small works such as securing responders and response coordinators. DG ECHO bookshelves and equipment against falling to funds capacity building through the Union Civil improving the structural safety of the entire building by Protection Knowledge Network. No methodologies retrofitting structural elements (for example, have been developed, so this represents an exploratory foundation, structural walls, beams, and columns) and systematic attempt at measuring the benefits of these non-structural elements (for example, partition walls, 10 TURNkey = Towards more Earthquake-resilient urban Societies through a Multi-sensor-based Information System enabling Earthquake Forecasting, Early Warning and Rapid Response actions. Case studies Earthquakes 79 staircases, facades, and HVAC elements). Seismic To quantify earthquake consequences with and strengthening can range from local strengthening of without strengthening interventions, analysis select vulnerable elements to more major retrofits frameworks such as HAZUS (Kircher, et al., 2006) and involving the entire structure. In some cases, buildings FEMA P-58 (Hamburger, et al., 2012) are commonly can be deemed not cost-effective to retrofit where too used. In addition to direct property damage, large of an investment is required and buildings need frameworks like HAZUS provide a methodology for to be demolished and reconstructed. Given the large calculating reduction in direct business interruption capital investments required for seismic strengthening, loss (for example, factory shutdown from direct they are seldom undertaken on a voluntary basis by damage or lifeline interruption), indirect business owners, where strengthening is more commonly interruption loss (for example, ordinary economic carried out when required by the building code or an ‘ripple’ effects), societal losses (deaths, injuries, and ordinance, is triggered by a change of use, or is part of homelessness), emergency response services (for a seismic risk reduction investment program. example, ambulance service, fire protection), and other non-market damages (for example, historic Seismic strengthening programs at scale require large sites). A study which evaluated BCRs of the US Federal capital investments, risk assessment, and planning. Emergency Management Agency’s mitigation grants While large-scale seismic strengthening programs are used an adaptation of the HAZUS methodology to not widespread in EU MS, there are several examples show that the average BCR of earthquake mitigation of successful programs. Seismic strengthening grants involving physical strengthening works was 1.4 programs are typically designed to prioritize vulnerable (Rose, et al., 2007). The study concluded that buildings and infrastructure that are at high risk, are considering the reduction in property loss reduction critical, or are of strategic importance. Therefore, risk alone was not sufficient for the average BCR from assessment and BCA are key tools in helping prioritize mitigation measures to exceed 1.0, and the largest and plan for seismic risk reduction investments. component of benefits (62 percent) came from the reduction of casualties. The benefits of seismic strengthening are commonly determined by considering the difference in social and A recent report by (NIBS, 2019) showcases a economic losses caused by earthquake damage with comprehensive BCA of natural hazard mitigation in the and without the intervention (Cardone, et al., 2019; United States, considering riverine floods, hurricane Liel & Deierlein, 2013; Yi, et al., 2020). This is done by surge, wind, earthquake, and WUI fire. The mitigation conducting risk analysis, simulating damage to measures that were evaluated ranged from adaptation buildings and infrastructure, which in turn is used to and exceedance of up-to-date building codes to quantify losses. Seismic retrofit BCAs commonly retrofit of existing buildings and utility and analyse the effect of several retrofit solutions on a transportation infrastructure. In terms of seismic specific type of building (for example, unreinforced strengthening strategies, the study examined BCRs for masonry, reinforced concrete frames, and soft-story seven earthquake retrofit measures: strengthening wood structures), where probabilistic earthquake the first story of soft-story dwellings, adding engineered engineering analysis is used to quantify the reduction tie-down systems to manufactured homes that are not in post-earthquake repair costs - the main considered anchored to the ground, strapping water heaters to the benefits. Studies point out that considering reduction building frame, adding child safety latches to kitchen in repair cost as the sole benefit does not typically cabinets, securing tall bookcases to the wall, strapping result in a positive return rate of a retrofit investment computer monitors and televisions to desks or shelves, (Liel & Deierlein, 2013). For this reason, other benefits and securing fragile objects to their shelves with commonly considered in seismic BCAs are reduction museum putty. The BCRs of retrofit measures varied in fatalities (Yi, et al., 2020) and injuries (Cardone, et widely depending on the measure and hazard level but al., 2019). Similar approaches are used to assess the averaged between 2 and 24. The two most cost- benefits of investment in infrastructure such as effective measures across geographies were soft-story bridges, where a study that used risk-based seismic retrofit and strapping water heaters to the building life-cycle BCA found that depending on the location, frame. However, the building codes have the potential type of bridge, and type of retrofit, the BCRs range to reduce the most overall damage. from less than 1.0 (not cost-effective) to 9.8. Case studies Earthquakes 80 SEISMIC STRENGTHENING IN THE CONTEXT OF TRIPLE DIVIDEND BCA The following is a brief description of the same time, the EU’s Energy Efficiency Directive also seismic strengthening benefits considering set a target of reaching 20 percent energy efficiency the triple dividend framework: by 2020 (European Commission, 2021). Retrofitting existing buildings so that they are both seismically • Dividend 1: The benefits related to reduced resistant and energy efficient usually requires high earthquake consequences include, but are not costs (European Commission, 2019). These conditions limited to, reduction in losses related to direct and lead to a growing need for combined retrofitting and indirect asset damages (caused by secondary energy efficiency, and this is reflected in the EU’s focus hazards), direct and indirect business and service on integrating energy efficiency and seismic upgrading interruption losses, social losses including into one agency (European Commission, 2020d). casualties and psychological trauma, natural capital losses, historical asset damages, and emergency In this context, the European Commission has response costs. purposed a methodology (European Commission, 2020d) to evaluate the combined approach of both • Dividend 2: Investment into earthquake risk seismic improvement and energy efficiency of a reduction contributes to economic stability and building. The methodology suggests three important reduced uncertainty. In terms of benefits, these can aspects that needed to be considered: (1) reduction of translate into improved government/business CO2 emissions, (2) energy efficiency of the building, image and credit rating associated with business and (3) the building‘s resilience to natural hazards. continuity (Rose, 2016). Strengthened assets and However, there are limits and barriers to the infrastructure can provide better access to combination of seismic safety and energy efficiency insurance markets and reduced insurance retrofits, which include technical difficulties for seismic premiums. Investment into seismic strengthening retrofits, owners’ insufficient awareness of the seismic can also support engineering innovation and vulnerability and energy performance of their building, technology development. and bureaucratic obstacles (Sigmund, 2019). As a result, many of the evaluations of European buildings • Dividend 3: The third dividend relates to co-benefits only consider the reduction of CO2 emissions and of DRM investment. Seismic strengthening that energy efficiency as important criteria and hardly involves significant capital works is often address the buildings’ vulnerability to natural disasters accompanied by renovation and functional and hazards (European Commission, 2020d). improvements, which can result in improved working/living conditions, higher asset valuation, Therefore, it is essential to include benefits from co- and increased revenue in case of commercial real investments in the integration of energy efficiency and estate. seismic retrofitting of buildings into the BCAs so that such investments can be further promoted. A study Co-investment into seismic strengthening and energy has shown that combined energy and seismic retrofit efficiency improvements can be a significant co- investment is economically efficient, as the combined benefit for EU countries. A large portion of European method will result in a significant reduction in the cities comprise aging building stock, which often payback periods in moderate to high seismicity region present high social, financial, recreational, and cultural compared to separate investments. The study also values. Currently, 80 percent of the existing EU suggests a 3 percent renovation rate for buildings, buildings were built before the 1990s, of which 40 which will lead to a 30 percent reduction in CO2 percent were built before the 1960s (European emissions across all cities by 2030s. An energy retrofit Commission, 2019). These structures tend to be more and seismic upgrading project for a school building in susceptible to seismically induced damage and are Italy has proved such a benefit. An analysis (Mora, et candidates for seismic retrofitting, as many of them al., 2018) of the project addresses the efficacy and need to be maintained as cultural heritages. At the cost of the project and the results suggest that by Case studies Earthquakes 81 combining energy and seismic retrofit, there is a 53 which may not occur in the investment lifetime. This percent in cost saving and a 96 percent reduction in analysis is often used when the beneficiary is energy consumption. Therefore, it is concluded that concerned with managing the adverse consequences the combined intervention is economically preferable of rare event and wants results that are easy to and generates less cost compared to the cost of two communicate. In such cases, there needs to be different interventions. acknowledgement that the benefits might not realize during the investment time. BCA MODELLING CHOICES AND IMPLICATIONS ON THE RESULTS The second approach that is commonly adopted in earthquake investment BCAs is based on assessing all Earthquakes can cause widespread societal and possible damaging events considering their probability economic losses in a single event, but their infrequent of occurrence. For example, seismic strengthening occurrence poses challenges when conducting BCA can lead to significant benefits in a large earthquake, and interpreting the results. Several different but the low probability of that will result in a ‘lower’ approaches have been used to quantify the benefits of weight compared to a more frequent/less damaging earthquake risk reduction investment and care must event. A common metric that is used in such an be taken when selecting and interpreting the results of analysis is the reduction in AALs, that is, reduction in an earthquake-related BCA. losses from all damaging earthquakes that can occur in a given year weighted by the probability of Dividend 1 benefits are only realized when an earthquakes’ occurrence. The BCRs are then earthquake occurs, whose timing and magnitude are calculated by dividing the NPV of the benefits characterized by large uncertainty. The impacts of (considering the design life of the asset) by the cost of earthquakes are nonlinear; small and frequent seismic strengthening. Another metric that is earthquakes may produce little to no damage, where sometimes considered is the payback period of the earthquakes with shaking above a certain threshold investment (Cardone, et al., 2019; Yi, et al., 2020), can cause buildings to suddenly collapse. There are which indicates how many years on average it will take two common approaches to conducting a seismic to pay back the investment. The advantage of using strengthening BCA: single-scenario assessment and this type of analysis is that it considers the likelihood of stochastic-event assessment (often referred to as earthquake events; the downside is that it often results probabilistic seismic risk assessment). in lower BCRs since extreme consequences are ‘averaged out’. Therefore, it might not be a suitable In the first approach, a single earthquake scenario of a analysis method if the beneficiary is concerned with specified magnitude is chosen and the consequences the consequences of infrequent, large-consequence with and without strengthening are evaluated. The events which pose a large risk to society. One option to earthquake scenario is typically chosen based on a account for infrequent losses is to consider benefits significant historic earthquake or a large potential associated with a lower probability of occurrence— earthquake based on seismologic studies. This another by-product of the probabilistic seismic risk approach can be thought of as a ‘what if’ analysis analysis. As an example, benefits associated with a 10 that does not explicitly consider the likelihood of percent probability of exceedance in 50 years can be occurrence of that event. Given that the chosen considered, which is similar to the philosophy of scenario is typically a large earthquake, the potentially earthquake-resistant design which is based on ‘rare’ realized benefits from strengthening are often earthquake shaking with 10 percent probability of significant and result in relatively large BCRs. They, exceedance in 50 years (or 475-year return period). however, do not reflect the likelihood of this scenarios Case studies Earthquakes 82 EVALUATING THE BENEFITS OF SELECTED INVESTMENTS OF THE 2010-2016 NATIONAL PLAN FOR SEISMIC RISK PREVENTION IN ITALY This case study is a new ex post analysis under this This case study aims to evaluate the benefits of the project that involved modelling of hazards. investments made by the Government of Italy under the 2010–2016 National Plan for Seismic Risk Æ Description Prevention (more details on programs for cultural heritage protection are included in Box 7 below). Box 7: Cultural heritage protection and seismic strengthening in Italy Due to Italy’s geodynamics, developmental dynamics, and squads” to retrieve, categorize, store, and restore cultural architecture and wealth of cultural heritage, the country is assets in case of an emergency. more susceptible to earthquake devastation than other European countries. In 2016, a 6.2 magnitude earthquake Moreover, several projects have specifically supported the (Povoledo, 2016) in Central Italy killed 296 people and reconstruction or rebuilding of specific buildings. The severely damaged over 50 historic sites in seismically Basilica of St. Benedict in Norcia, for example, is an active areas. Moreover, €541 million out of €23,53 billion important religious emblem of European monasticism that in earthquake-induced damages that same year were was heavily destroyed in the earthquake of 30 October caused by direct seismic impacts on cultural heritage 2016. With a €10 million budget, of which half is financed sites. Despite Italy’s progressive approach to improving by the EU, the Basilica will be rebuilt using an earthquake- earthquake resilience, reversible intervention techniques resistant structure, energy-saving air conditioning and are greatly preferred for cultural sites due to the deeply felt lighting, and a continuous data-acquiring remote historical connections to assets. As a result, the Italian monitoring system between 2017 and 2023 (European government has been an involved partner in the ResCult Commission, 2019c). Despite these upgrades, the platform (“Increasing Resilience of Cultural Heritage”) structure’s reconstruction is aimed at ultimately restoring (ResCult, 2021). Italy has also developed a risk map using the Basilica’s historic, cultural, and social role of fostering comprehensive alphanumeric and cartographic database social and economic activity for the local community. of cultural assets throughout the country and trained “art Italy is exposed to high seismic hazard, where in the Plan for Seismic Risk Prevention allocated financial last two decades it saw numerous damaging resources to higher-risk municipalities, whose 475- earthquakes throughout its territory. Following the year return period peak ground acceleration12 on stiff 2009 Abruzzo (L’Aquila) earthquake, under this soil exceeds 0.125 g. The program’s activities focused program, €963.5 million (Dolce, 2012) was allocated on three main areas (Dolce, et al., 2019): to various activities, which were implemented by the Civil Protection Department over seven years. The 1. Seismic microzonation studies and analysis of program’s primary objective was to reduce the human the Limit Condition for Emergency (LCE), to losses during earthquakes and incentivize private support territorial governance and emergency owners and administrators to take actions to reduce planning seismic risk. This includes building an understanding on the vulnerability of buildings, the importance of 2. Seismic retrofit and reconstruction of public local amplification, and the use of microzonation11 buildings and infrastructure of strategic interest studies (Dolce, et al., 2019a; Moscatelli, et al., 2020) or infrastructure critical for the consequence of to improve urban and emergency planning, as well as their collapse ensuring correct implementation of civil protection plans considering the vulnerability of the strategic 3. Seismic upgrading and reconstruction of private elements and the interconnection routes. The National buildings. 11 Microzonation studies are aimed at understanding the geological, geotechnical, geophysical, and geometrical characteristics of areas to provide reliable maps of seismic ground shaking parameters and induced hazards, such as liquefaction and landslides. 12 PGA is the largest ground acceleration recorded during an earthquake event. Case studies Earthquakes 83 This case study evaluates the efficiency of selected a subset of buildings from the overall investment were investments under the National Plan for Seismic Risk considered for the BCA. Prevention using a Triple Dividend BCA Framework. In particular, it focuses on select assets under the Investments and prioritization of public buildings were following two investment streams: (a) strengthening of made based on the potentially devastating private residential and mixed-use buildings and (b) consequences in case of collapse and strategic retrofitting of public buildings. Given the data importance of facilities for civil protection purposes. availability, the BCA focuses on evaluation of dividend The following categories of buildings were included in 1, or avoided disaster losses, by using probabilistic the analysed investments as outlined in Table 24. earthquake risk modelling. It should be noted that only Table 24: Types of buildings included in Italy’s seismic retrofitting by sector SECTOR TYPES OF BUILDINGS Public administration buildings Administrative buildings, city hall, post office, and so on Civil protection headquarters Municipal civil protection centres, regional civil protection headquarters, and so on Health care facilities Hospitals, health care facilities, nursing homes Military and firefighting facilities Carabinieri and public security, firefighters, state forestry corps Places of social or sporting activity Gymnasiums, stadiums, paces of social or sporting activity Education facilities Schools Source: Dolce (2012) Given that the number of private buildings that require quantified the decrease in losses associated with asset seismic strengthening far exceeds the available damage, fatalities, injuries, and the number of days the resources, the investments were prioritized in building function is interrupted. It should be noted that municipalities with the highest seismic hazard in the the estimation on the number of interruption days is a region, where the buildings were assigned a score conservative estimate where certain functions can (Dolce, 2012) based on the year of construction and continue through temporary arrangements or in other the construction material. For private buildings, buildings. The benefits were evaluated based on two government investment was intended to be an analyses: (1) a decrease in AALs (that is , annual loss incentive rather than a total refund of the expenses, averaged over a very large number of years) assuming where co-financing by private owners was expected a 50-year building design working life following the and the government refunded only the costs of the investment and (2) a decrease in losses from an structural intervention up to a certain maximum. infrequent large event corresponding to a 475-year Information of private owners’ co-financing amounts return period, hereinafter referred to as PML analysis. was not available. While the 50-year design life period is chosen in line with the Eurocode, in reality many buildings may Æ Methodology function beyond that time frame, which would further increase the benefits of the seismic strengthening. The benefits derived from the investment were The earthquake risk model that was used to evaluate evaluated by modelling the consequences of numerous the losses consisted of three major components of earthquake scenarios with and without earthquake earthquake risk analysis: hazard, exposure, and strengthening interventions. The results of the model vulnerability. Case studies Earthquakes 84 Hazard model: ESHM1313, also known as the ‘Seismic GEM taxonomy (Brzev, et al., 2013), and therefore a Hazard Harmonization in Europe’ (SHARE) project, mapping scheme between the provided exposure data was used to conduct the risk analysis (Woessner, et al., and the GEM taxonomy building classes was required. 2015). ESHM13 provides a consistent seismic hazard As part of the ongoing European Seismic Risk Model model for all of Europe, whose creation involved several 2020 (ESRM20) study, Crowley et. al. (2020) reviewed institutions and experts throughout the region, and it the seismic design regulations throughout Europe and was built upon several national and regional seismic proposed a mapping between design year and code hazard models. Within the SHARE project, three quality. These benchmark code years (that is, no code alternate seismic source models were developed using before 1908, low code before 1996, moderate code historical and instrumental earthquake catalogues, a before 2010, and high code afterwards for the case of database of seismic faults, and tectonic regionalization Italy) were used to infer a mapping between the design with associated ground motion models. The seismic year provided and their associated ductility levels source models and associated ground motion models (indicative of seismic vulnerability)14, which are a were used to perform an event-based risk analysis, fundamental component of the GEM taxonomy. which considered all plausible damaging earthquakes Information regarding the intervention type (for and their probability of occurrence. In this process, a example, local strengthening) was also used to infer a stochastic event set is generated, which is indicative of code or ductility level and construction type for both the seismicity of the region over a given period. Each of the baseline and retrofitted case, based on background these rupture events produces a ground-shaking field, information of the retrofit program provided by Dolce which is then used to estimate associated impacts and (2012) . For example, any intervention type would lead losses from the modelled exposure. to an increase in code quality or ductility, but only demolition and reconstruction would ensure high code Exposure and vulnerability models: To estimate the quality or ductility (whereas the lesser intervention risk, information regarding the exposure (for example, types might lead to only a moderate code quality or location, building typology, and value) and vulnerability ductility). Additionally, buildings that only required (for example, damageability) is required. The provided local strengthening were assumed to overall be less exposure data from the 2010–2016 National Plan for vulnerable compared with buildings that required Seismic Risk Prevention in Italy denote the location, seismic upgrading or demolition and reconstruction, size, use category, material type, design year for public as there were specific criteria to ensure that those buildings or construction period for private ones, buildings did not have notable seismic deficiencies, intervention type, and cost of intervention. The damage, or irregularities. vulnerability models associated with GEM Foundation’s 2018 Global Risk Model (as documented in Martins Benefit estimation: Given the data availability, the and Silva 2020) have been used as a starting point to BCA explicitly quantified the benefits associated with relate the ground shaking (for example, peak group dividend 1: reduction of losses associated with avoided acceleration) to a damage level (for example, slight) injuries, avoided fatalities, reduced damage, and and loss (for example, repair cost, fatalities, and reduced disruption associated with building closure. disruption time). These vulnerability models follow the Each of the benefits was quantified as per Table 25. Table 25: Methodologies of benefit estimations BENEFIT METHODOLOGY Avoided injuries The benefit from the reduction in injuries was evaluated using a method from the US Department of Transportation that estimates the value of preventing injuries as a fraction of VSL. Injuries with and without interventions were estimated using the HAZUS methodology, where Severity 2 and 3 injuries were considered. 13 While ESHM13 was used for this analysis, it is not consistent with the procedures and the criteria used by the Italian seismic prevention program to identify the areas where the program is applicable, define the initial and the final safety conditions, and so on. The prevention program used the official 2004 seismic hazard model since 2004. 14 This is a simplification, where in reality fundamental design standards were issued at different times throughout the territory Case studies Earthquakes 85 Avoided fatalities The benefit associated with the reduction in fatalities was evaluated based on the VSL. Decrease in The difference between repair cost with and without intervention was evaluated for each of the repair cost buildings depending on the level of damage. Decrease in First, a decrease in non-functional days was estimated by taking the difference in disruption days losses due to without and with the intervention. Then, the benefits associated with decrease in service disruption interruption of were calculated using the buildings’ area, an assumed employee density, the decrease in disruption services days, and the average GDP per employee in a relevant industry. Furthermore, the benefits associated with decrease in disruption of residential buildings were calculated using the number of occupants, the decrease in disruption days, and the average rental price per person. This assumes that the displaced will have to find alternate accommodations while their residences are inaccessible. Source: World Bank analysis The benefits were calculated considering a 50-year and other common structures), a discount rate of 3 investment lifetime (building design working life, as percent, and a VSL of €6 million. prescribed in Eurocode, Category 4 building structures DATA were analysed. Figure 17 shows the distribution of The data on select investments of the National Plan for buildings across the 17 regions of Italy, with the color Seismic Risk Prevention were provided by the Civil showing the number of assets per region. Various types Protection Department. In total, 3,796 residential and of building interventions were undertaken as presented mixed-use private buildings and 694 public buildings in Table 26. Figure 17: Number of buildings per region in Italy (private buildings on left, public buildings on right) Source: World Bank ‘Local strengthening’ refers to less involved failures. Local strengthening is typically done in beam- intervention, where single structural elements or column joints of reinforced concrete framed structures portions of a structure are strengthened without or in the connections of orthogonal walls and walls with varying the global structural behaviour. In the seismic slabs in masonry buildings. The median intervention case, they can be aimed at reducing or eliminating cost of such an investment among public buildings is those unfavourable behaviours of single elements or approximately 10 percent of the building replacement structural parts that, due to inadequate local strength cost. and/or ductility, can produce anticipated brittle Case studies Earthquakes 86 ‘Seismic upgrading’ is a more global intervention that ‘Demolition and reconstruction’ is an intervention type alters the overall structural behaviour of the building that is undertaken when a building is considered to be and therefore requires more investment than local too costly to retrofit to acceptable safety standards or strengthening. Such an intervention is aimed at is functionally obsolete and requires reconstruction. producing immediate reduction of the seismic risk of The required investment for such an intervention vulnerable buildings. The median cost of intervention strategy is the replacement costs plus the demolition of ‘seismic upgrading’ for public buildings is cost. approximately 26 percent of the building replacement cost. Table 26: Number of building interventions conducted by sector and type of interventions NO. OF PUBLIC BUILDINGS WITH NO. OF PRIVATE BUILDINGS WITH TYPE OF INTERVENTION NEEDED INTERVENTION INTERVENTION Local strengthening interventions 70 2,400 Seismic upgrading 606 1,263 Demolition and reconstruction 18 133 Source: World Bank analysis; based on official data from the Italian Civil Protection Department Æ Results of the analysis The following is a summary of results of the BCA for public and private buildings (see Table 27 and Table 28). Table 27: Investment into public buildings PUBLIC BUILDINGS DESIGN LIFE ANALYSIS PML ANALYSIS (50 YEARS) (475-YEAR RETURN PERIOD) All By intervention type All By intervention type and reconstruction and reconstruction Seismic upgrading Seismic upgrading strengthening strengthening Demolition Demolition Local Local DIVIDEND 1 (€, millions) Avoided 26.6 3.4 21.9 1.3 66.1 8.5 54.4 3.1 injuries Avoided 127.2 14.6 105.8 6.8 298.7 32.3 248.2 18.2 fatalities Decrease in 30.2 3.3 26.0 0.8 123.1 13.9 105.7 3.4 repair cost Decrease in losses due to 67.7 7.6 58.4 1.7 319.9 36.3 275.6 8.0 interruption of services Case studies Earthquakes 87 Total 251.8 29.0 212.2 10.6 807.7 91.0 683.9 32.8 dividend 1 Total 251.8 29.0 212.2 10.6 807.7 91.0 683.9 32.8 benefits Total costs 461.1 26.0 415.3 19.8 461.1 26.0 415.3 19.8 BCR 0.55 1.11 0.51 0.54 1.75 3.5 1.65 1.66 NPV −209.3 3.0 −203.1 −9.2 −46.63 65.0 268.6 13.0 (€, millions) ERR (%) −45.39 11.54 −48.90 −46.46 75.17 250.0 64.68 65.66 PUBLIC BUILDINGS DESIGN LIFE ANALYSIS (50 YEARS) BY FACILITY TYPE Civil Education Health Military and Recreation Public protection care firefighting and sporting administration headquarters and civic DIVIDEND 1 (€, millions) Avoided injuries 0.8 10.6 2.4 1.5 1.7 9.5 Avoided fatalities 3.4 51.1 14.6 7.0 7.9 43.3 Decrease in repair cost 0.9 6.6 3.9 1.9 0.7 16.3 Decrease in losses due to interruption of 2.0 11.0 13.2 4.7 2.0 34.9 services Total dividend 1 7.0 79.3 34.1 15.0 12.3 104.0 Total benefits 7.0 79.3 34.1 15.0 12.3 104.0 Total costs 10.8 119.0 73.9 22.8 11.3 223.3 BCR 0.65 0.67 0.46 0.66 1.09 0.47 NPV (€, millions) −3.8 −39.7 −39.8 −7.8 1.0 −119.3 ERR (%) −35.19 −33.36 −53.86 −34.21 8.85 −53.43 PUBLIC BUILDINGS - PML ANALYSIS (475-YEAR RETURN PERIOD) BY FACILITY TYPE Civil protection Education Health Military and Recreation Public headquarters care firefighting and sporting administration and civic DIVIDEND 1 (€, millions) Avoided injuries 2.0 25.9 6.3 3.7 4.3 24.0 Avoided fatalities 8.6 113.1 35.5 17.8 20.6 103.2 Decrease in repair 3.7 27.4 14.9 7.5 3.1 66.5 cost Decrease in losses due to interruption 9.2 52.3 60.9 21.0 9.2 167.2 of services Case studies Earthquakes 88 Total dividend 1 23.5 218.7 117.6 49.9 37.2 360.9 Total benefits 23.5 218.7 117.6 49.9 37.2 360.9 Total costs 10.8 119.0 73.9 22.8 11.3 223.3 BCR 2.17 1.84 1.59 2.19 3.29 1.62 NPV (€, millions) 12.7 99.7 43.7 27.1 25.9 137.6 ERR (%) 117.59 83.78 59.13 118.86 229.20 61.62 Source: World Bank analysis; based on external data and information Note: a. Service interruption in education does not include the social losses and childcare costs due to interruption of education; service interruption in the health care sector does not include casualties associated with loss of hospital functionality but only casualties caused by damage. Several observations can be made from the public • The PML analysis results show that the projected buildings BCR results: fatalities decrease by 84 percent, injuries by 87 percent, days of service interruption by 59 percent, • The BCRs are higher for the PML analysis since it and repair costs by 53 percent, as a result of the considers the benefits realized in a more damaging investment into public buildings. event that can cause large losses. The results show that in the case of a large earthquake, the benefits • Local strengthening seems to be the most effective exceed strengthening costs for all types of investment; however, the benefits from demolition intervention across all the sectors. and reconstruction are likely underestimated since the analysis does not account for the benefits • The design life analysis results show that the associated with functional improvements, including projected fatalities decrease by 73 percent, injuries improved use of space and energy efficiency. by 80 percent, days of service interruption by 55 percent, and repair costs by 52 percent, as a result • Greatest benefits are derived from decrease in of the investment into public buildings. avoided fatalities and service interruption, followed by decrease in avoided repair costs and injuries. Table 28: Investment into private mixed-use buildings PRIVATE BUILDINGS DESIGN LIFE ANALYSIS PML ANALYSIS (50 YEARS) (475-YEAR RETURN PERIOD) All By intervention type All By intervention type Local strengthening Local strengthening and reconstruction and reconstruction Seismic upgrading Seismic upgrading Demolition Demolition DIVIDEND 1 (€, millions) Avoided 18.4 9.9 8.1 0.5 48.3 25.8 21.1 1.3 injuries Avoided 82.5 44.4 35.9 2.2 212.0 114.9 91.2 5.8 fatalities Case studies Earthquakes 89 Decrease in 45.3 25.2 19.0 1.1 210.0 117.1 87.6 5.3 repair cost Decrease in losses due to 13.9 5.4 8.3 0.2 69.5 26.7 41.7 1.1 interruption of services Total 160.2 84.9 71.2 4.1 539.7 284.6 241.7 13.5 dividend 1 Total benefits 160.2 84.9 71.2 4.1 539.7 284.6 241.7 13.5 Total costs 113.1 62.4 46.2 4.5 113.1 62.4 46.2 4.5 BCR 1.42 1.36 1.54 0.9 4.77 4.56 5.23 2.99 NPV 47.1 22.5 25.0 −0.4 426.6 222.2 195.5 9.0 (€, millions) ERR (%) 41.64 36.06 54.11 −8.89 377.19 356.09 423.16 200.0 Source: World Bank analysis; based on external data and information Note: The total costs reflect the government investment and do not consider private owners’ co-financing. Several observations can be made from the private decrease in repair cost, and then avoided injuries buildings BCR results: and decrease in service interruption. Since the occupancy per building of private buildings is less • The design life analysis results show that the than that of public buildings (that is, lower projected fatalities decrease by 85 percent, injuries concentration of risk), a larger benefit is derived by 85 percent, days of service interruption by 58 from reduction of repair costs. percent, and repair costs by 53 percent, as a result of the investments in private buildings. Æ Challenges and lessons learned • PML analysis results show that the projected The earthquake analysis could be completed by fatalities decrease by 90 percent, injuries by 89 inclusion of further aspects as outlined above. Other percent, days of service interruption by 62 percent, studies have shown substantial benefits with ex ante and repair costs by 55 percent, as a result of the analysis for retrofitting of a variety of buildings, for investments in private buildings. example, in Romania, as well as considerable variability of results depending on types of damages • In majority of the cases, the greatest benefits are and breadth of benefits considered or VSL assumed. derived from avoided fatalities, closely followed by a CO-INVESTMENT INTO SEISMIC STRENGTHENING AND ENERGY EFFICIENCY IMPROVEMENT OF EDUCATION FACILITIES IN EUROPE’S EARTHQUAKE PRONE COUNTRIES This case study is a new ex ante / hypothetical services to the local community, and can also function analysis under this project that involved modelling as a place for shelter and resources in emergency of hazards. response. Eight EU MS with moderate to high seismicity were considered: Austria, Bulgaria, Cyprus, Greece, The objective of this study is to evaluate the benefits Croatia, Italy, Romania, and Slovenia. and costs of investing in improved education facilities, particularly the returns on capital works intended to The study considers education facilities in higher make schools and universities safe in earthquakes and hazard areas (475-year peak ground acceleration improve their energy efficiency. Investment in the > 0.2g) and uses a representative school and university safety of education facilities is critical because these building for each of the countries to conduct the facilities house students, provide vital education analysis (see Table 29). A representative building Case studies Earthquakes 90 considers the average number of students per facility and building materials that are commonly used in each of the countries. Table 29: Number of schools and universities considered in the case study with associated national database websites MODELLED COUNTS COUNTRY SCHOOLS UNIVERSITIES Austria 275 3 Bulgaria 4,486 21 Croatia 795 70 Cyprus 326 20 Greece 15,083 237 Italy 35,506 266 Romania 7,370 1,076 Slovenia 415 5 Source: World Bank analysis; based on statistics from national databases (Database AT, 2021; Database CY, 2021; Database IT, 2021; Database RO, 2021; Database SK, 2021; Database SL, 2021) Æ Modelling methodology and data inputs evaluate the decrease in losses is similar to that in consisting of three major components of earthquake The benefits derived from the investment were risk analysis: hazard, exposure, and vulnerability. evaluated by modelling the consequences of numerous earthquake scenarios with and without interventions Hazard model: ESHM13, also known as the SHARE and quantifying the decrease in energy consumption project, was used to conduct the risk analysis from energy efficiency improvements. The quantified (Woessner, et al., 2015). ESHM13 provides a benefits include decrease in losses due to asset consistent seismic hazard model for all of Europe, damage, fatalities, and injuries from earthquakes whose creation involved several institutions and (dividend 1) and reduction in energy consumption and experts throughout the region, and it was built upon CO2 emissions due to improved energy efficiency several national and regional seismic hazard models (dividend 3). Dividend 1 benefits were evaluated based (see map of seismic countries in Figure 18, with the on two analyses: (1) a decrease in AALs (that is, colors in map showing the exposed value of education annual loss averaged over a very large number of facilities in the countries). years) assuming a 50-year building design life following the investment period (that is, building design working Exposure model and vulnerability model: For the life according to Eurocode, Category 4 building eight countries, an exposure model for school and structures) and (2) a decrease in losses from an university buildings was derived. Aggregated national infrequent large event corresponding to a 475-year counts and occupants were based on GPSS GLOSI return period, herein referred to as PML analysis. In statistics, while the average area and replacement addition, energy savings and reduction in CO2 emission value of buildings came from the construction costs for a 50-year building design life were considered in developed in the ongoing SERA project. The spatial both analyses. The following two sections briefly distribution of education buildings within each country describe the modelling procedures for earthquake leveraged national data (where available) and existing consequences and energy efficiency. OpenStreetMap data, and remaining buildings were distributed to the NUTS 3 areas proportional to the EARTHQUAKE CONSEQUENCE MODELLING population (as per Eurostat). To identify the proportion of buildings that would be retrofit candidates within this The earthquake consequence model that was used to hypothetical retrofit program, the exposure was Case studies Earthquakes 91 reduced further to consider (1) regions of relatively were not considered to be candidates for retrofit and high seismic hazard and (2) building classes with therefore removed from the study. Additionally, relatively high vulnerability. The seismic hazard buildings classes that are known to have better threshold was set at a minimum PGA of 0.2 g on soil for performance (that is, moderate to high ductility levels, the 475-year average return period earthquake - reinforced masonry) were not considered as candidates assets in locations that did not meet this threshold for retrofit and therefore removed from the study. Figure 18: Map of seismic countries in the EU by the exposed value of education facilities Source: World Bank analysis; based on external data and information Construction typologies for the school and university was required (see Figure 19 for percentage reduction buildings were inferred based on construction data for in AAL). The anticipated decrease in seismic losses is the residential and commercial buildings from the due to a decrease in the overall vulnerability of SERA project. Given the absence of building-specific education buildings, which was approximated by information regarding construction type, vulnerability considering a step change increase in the level of models that considered the range of possible ductility offered by each building class. For example, if construction types were derived. This approach a building was constructed to a ‘low’ code level for a involved the construction of weighted vulnerability given country, it was assumed the retrofitted building curves, where the weight was equal to the proportion would now achieve a performance level equivalent to of value of each construction type relative to the overall the ‘moderate’ code level of that country. This exposed value from the SERA Project (minus the improvement would be reflected by an increase in the better-performing building classes discussed in the capacity of that building to resist earthquake shaking previous paragraph). The better-performing building but not necessarily ensure that the building would be classes (that is, moderate to high ductility and able to achieve the performance level associated with reinforced masonry classes) were not considered as the latest (or ‘high’) code level of that country. The candidate buildings, as a hypothetical retrofit program retrofit cost was assumed to be 5 percent, 10 percent, is likely to target building classes known to have poor and 15 percent of the replacement cost, according to performance (that is, no to low ductility and the building’s risk level, which captures a range of unreinforced masonry classes). interventions from local strengthening to more substantial capital works in accordance with the To inform the BCA, an estimate of the decrease in literature review (see Table 30). anticipated losses and the associated retrofitting cost Case studies Earthquakes 92 Table 30: Estimated retrofitting cost ratios from multiple sources SOURCE DESCRIPTION RETROFITTING COST RATIO (%) Italy case study Seismic upgrading of schools 25 Strengthening with jacketing methods (that is, Calvi 2013 FRP, RC, and steel) applied to 50% of the 16 elements Calvi 2013 Adding new elements (for example, RC walls) 24 Kappos and Conventional retrofitting methods 12 Dimitrakopoulos 2008 Garcia, Hajirasouliha, and FRP retrofitting methods in Mediterranean 5–15 Pilakoutas 2010 countries (partial - full) Liel and Deierlein 2013 FRP retrofitting, RC jacketing, RC walls 10, 40, 30 Added shear walls to a multi-story RC frame Smyth et al. 2004 32–54 building retrofitted (partial - full) Source: World Bank analysis; based on information and data included in sources reviewed Note: FRP = Fibre-reinforced polymer; RC = Reinforced concrete. The risk analyses for the baseline and retrofitting case probabilistic risk assessment of spatially distributed were performed using the OpenQuake-engine, a free assets. The analysis was performed at the NUTS 3 and open-source software that conducts seismic level. Three risk metrics were considered: direct hazard and risk analyses. An event-based (or time- financial loss due to damage, injuries, and fatalities. based) analysis was conducted, which allows for a Figure 19: Percentage reduction in average annual direct losses due to damage for the retrofitted case Source: World Bank analysis; based on external data and information Case studies Earthquakes 93 ENERGY EFFICIENCY IMPROVEMENT MODELLING Key parameters of existing educational buildings.: It should be noted that most of the educational The objective of this analysis is to provide inputs into buildings do not correspond to the current energy BCA for evaluating the costs and benefits of energy efficiency requirements for buildings thermal efficiency improvement investments in school transmittance U-value (lower value means better buildings. The following sections describe the performance, see Table 31 for more details). Better assumptions made, data sources used, and analysis energy performance of building elements observed in results for energy efficiency improvement benefit Austria and Slovenia could be related to the fact that estimation. Estimates were first made on per m2 annual part of the buildings were renovated in those countries basis for the reference education buildings in each including replacement of windows and exterior doors country, and then multiplied by the total area of the and insulation of whole or part of the building envelope. schools in the country. In other countries, most of the education buildings were still not upgraded. Table 31: Key parameters of existing educational buildings AVERAGE AVERAGE AVERAGE FABRIC OF EXTERNAL WALLS FOR A U-VALUE OF U-VALUE U-VALUE COUNTRY REPRESENTATIVE EDUCATION BUILDING EXTERNAL WALLS OF ROOFS OF WINDOWS (W/M2K) (W/M2K) (W/M2K) Austria Reinforced concreate, masonry 0.53 0.49 2.06 Bulgaria Reinforced concreate, masonry, 1.1 0.77 2.64 confined masonry Croatia Reinforced concreate, masonry, 1.12 0.93 3.58 confined masonry Cyprus Reinforced concreate, masonry 1.7 2.1 4.19 Greece Reinforced concreate, masonry 1.61 1.49 4.18 Italy Reinforced concreate, masonry 0.6 0.87 4.11 Romania Confined masonry, masonry 1.34 0.89 2.27 Slovenia Reinforced concreate, confined 0.6 0.53 1.71 masonry, masonry Sources: European Commission (2020); European Union (2013a; 2013b; 2018) Energy efficiency measures description. Energy presents expected parameters of building elements efficiency measures required to improve energy after implementation of energy efficiency measures performance of the buildings are presented in Table 32 normalized for all 9 countries. Compared with the and expressed in thermal transmittance U-values. The U-values of existing buildings in Table 31, there is a normative requirements for energy performance of large gap in terms of achieving energy efficiency levels building elements vary among the countries. Table 31 presented in Table 32 below. Case studies Earthquakes 94 Table 32: Energy efficiency measures description ROOF WINDOWS HEATING, COOLING, EXTERNAL WALLS INSULATION LIGHTING INSULATION REPLACEMENT VENTILATION SHADING 7–20 cm thermal 20–30 cm Double glass Heating/cooling Lamps less External insulation on insulation with thermal device replacement; than 10 W/ moving shades exterior walls, (U < 0.2 W/m²K) break (U < 1.5 installed systems, m2 installing where beams, and W/m²K) cleaning optimization installation relevant columns (U < 0.35 W/m2K) Sources: Thermal transmittance U-values normalized for all countries based on the estimates from European Commission (2020); European Union (2013a; 2013b; 2018) Primary energy savings: Heat energy savings, savings would reach from 99 to 188 kWh/m2 per year. expressed in kilowatt hours (kWh) per m2 of building Electricity savings are estimated based on the useful area, estimated from 64 to 94 kWh/m2 per year electricity share used in each country for heating/ for ‘light/medium’ renovation with two to three energy cooling and lighting of educational buildings. More efficiency measures from Table 33 would be electricity is consumed in southern countries like implemented. For ‘deep’ renovation, four to six Greece and Cyprus, which use electricity as the main measures would be implemented, and primary energy source for cooling of buildings. Table 33: Primary energy savings NON- TOTAL PRIMARY ENERGY ‘LIGHT/MEDIUM’ TOTAL PRIMARY ENERGY ‘DEEP’ RENEWABLE SAVINGS FROM ‘LIGHT/ RENOVATION SAVINGS RENOVATION ELECTRICITY MEDIUM’ RENOVATION ELECTRICITY ‘DEEP’ RENOVATION (4 ELECTRICITY COUNTRY SHARE IN SAVED (2–3 EE MEASURES SAVINGS OR MORE EE MEASURES SAVINGS PRIMARY IMPLEMENTED) (KWH/ (KWH/M2/YEAR) IMPLEMENTED) (KWH/M2/ ENERGY (%) M2/YEAR) (KWH/M2/YEAR) YEAR) Austria 5 88 4 127 6 Bulgaria 15 60 9 116 17 Croatia 25 94 24 169 42 Cyprus 90 64 57 110 99 Greece 90 72 65 113 102 Italy 30 49 15 99 30 Romania 20 94 19 188 38 Slovenia 15 85 13 131 20 Sources: Primary energy consumption were estimated based on the comprehensive study of building energy renovation activities and the uptake prepared for the European Commission (European Commission, 2019b) Primary consumption for heat and electricity were reviewed and adjusted according to European Commission (2020); European Union (2013a; 2013b; 2018) Data for educational facilities is from the (European Commission, 2017) Note: EE = Energy efficiency. CO2 savings: Primary energy savings from Table 33 values of US$60 per tonne in 2020 and US$117 per were converted to tonnes of CO2 reduction using CO2 tonne in 2050 were used (World Bank, 2017b), which conversion factors for fossil fuels and electricity used were further extrapolated to the lifetime of the in buildings. CO2 reduction estimations were made for building. CO2-related reduction and CO2 economic ‘light/medium’ and ‘deep’ energy efficiency measures price values are presented in Table 34. packages. For the CO2 monetary benefits, reference Case studies Earthquakes 95 Table 34: CO2 savings CO2 CONVERSION FACTORS FOR CO2 CONVERSION CO2 SAVINGS ‘LIGHT/ CO2 ‘DEEP’ FOSSIL FUELS (NATURAL GAS, OIL FACTORS FOR MEDIUM’ EE RENOVATION COUNTRY USED ON-SITE OR DISTRICT ELECTRICITY RENOVATION (KG CO2/M2/ HEATING (KG CO2/KWH) (KG CO2/KWH) (KG CO2/M2/YEAR) YEAR) Austria 0.236 0.276 21 30 Bulgaria 0.29 0.819 22 43 Croatia 0.22 0.236 21 38 Cyprus 0.20 0.874 51 89 Greece 0.24 1.149 76 120 Italy 0.24 0.483 15 31 Romania 0.42 0.701 45 90 Slovenia 0.24 0.557 24 38 Source: World Bank analysis; based on data from Covenant of Mayors (2021) Note: EE = Energy efficiency. Energy costs and conversion factors: For the monetary savings are reduced energy from the primary energy estimation of energy savings of consumed heat and supply using less of primary fuels. Final energy electricity for each country’s education buildings, consumption covers energy supplied to the final respective energy prices and energy conversion consumer at the building level. Final energy supplied factors were used (see Table 35). While CO2 savings from the distribution network does not include losses assessment uses primary energy savings, the of the primary fuel conversion and supply, and thus it is assessment of monetary savings associated with usually lower quantity than primary energy. Final reduction in use of consumer energy used the final energy savings refer to the saved energy by the final energy savings at the building level. Primary energy consumer at the building level from the reduced refers to the energy that is converted directly from energy consumption or by using energy more efficiently natural resources (primary fuels). Primary energy after implementation of energy saving measures. Table 35: Energy costs and conversion factors HEAT ENERGY ELECTRICITY FINAL ENERGY TO PRIMARY FINAL ENERGY TO PRIMARY COUNTRY PRICE PRICE ENERGY CONVERSION ENERGY CONVERSION (€/KWH) (€/KWH) FACTORS (HEAT) FACTORS (ELECTRICITY) Austria 0.11 0.20 1.17 1.91 Bulgaria 0.06 0.11 1.30 3.00 Croatia 0.05 0.14 1.10 1.61 Cyprus 0.09 0.19 1.10 2.70 Greece 0.07 0.12 1.10 2.20 Italy 0.08 0.23 1.10 2.20 Romania 0.06 0.12 1.10 2.20 Slovenia 0.12 0.18 1.10 2.50 Sources: Conversion factors for heat and electricity were used according to European Commission (2020); European Union (2013a; 2013b; 2018). In case data in cost-optimal reports were not available, 1.1 primary energy conversion factor was used for heat and 2.2 for electricity conversion Case studies Earthquakes 96 Final annual benefit estimation: The investment costs uptake prepared for the European Commission as well of the ‘light/medium’ and ‘deep’ renovation options as the cost-optimal reports of each analysed country. were determined on the basis of a comprehensive Results of monetary benefits are presented in Table 36 study of building energy renovation activities and the and Table 37. Table 36: ‘Light/medium’ renovation monetary results INVESTMENTS ENERGY CO2 MONETARY CO2 MONETARY CO2 MONETARY COUNTRY (€/M2) EXPENDITURE BENEFITS MIN BENEFITS MEDIUM BENEFITS MAX VALUE SAVINGS (€/M2) VALUE (€/M2) VALUE (€/M2) (€/M2) Austria 240 8.21 0.70 1.05 1.40 Bulgaria 100 2.50 0.74 1.12 1.49 Croatia 192 5.24 0.71 1.06 1.42 Cyprus 160 4.55 1.73 2.59 3.45 Greece 126 3.93 2.56 3.84 5.12 Italy 151 4.18 0.52 0.77 1.03 Romania 127 5.38 1.50 2.26 3.01 Slovenia 153 8.80 0.82 1.23 1.64 Sources: Costs for energy efficiency measures implementation were estimated based on the comprehensive study of building energy renovation activities and the uptake prepared for European Commission (European Commission, 2019b). Energy efficiency measures costs were reviewed and adjusted according to European Commission (2020); European Union (2013a; 2013b; 2018) Table 37: ‘Deep’ renovation monetary results   INVESTMENTS ENERGY CO2 MONETARY CO2 MONETARY CO2 MONETARY (€/M2) EXPENDITURE BENEFITS BENEFITS VALUE BENEFITS MAXIMUM COUNTRY SAVINGS (€/M2) MINIMUM VALUE (€/M2) VALUE (€M2) (€/M2) Austria 294 11.86 1.01 1.52 2.03 Bulgaria 180 4.83 1.44 2.16 2.88 Croatia 288 9.45 1.27 1.91 2.55 Cyprus 227 7.86 2.98 4.47 5.96 Greece 182 6.17 4.02 6.03 8.04 Italy 265 8.48 1.04 1.57 2.09 Romania 246 10.76 3.01 4.51 6.02 Slovenia 225 13.52 1.26 1.89 2.53 Source: World Bank analysis; based on external data Case studies Earthquakes 97 RESULTS The results of the building design life analysis and PML analysis for schools and universities are presented in the following tables (Table 38 and Table 39). Schools: Table 38: BCA for schools AUSTRIA BULGARIA CROATIA CYPRUS Building PML Building PML Building PML Building PML design life analysis design analysis design analysis design life analysis analysis (475-year life (475-year life (475-year analysis (475-year return analysis return analysis return return period) period) period) period) DIVIDEND 1 (€, millions) Avoided 0.5 1.5 19.3 43.2 2.1 5.2 10.7 27.7 injuries Avoided 5.4 16.7 182.7 486.6 18.6 50.6 87.0 235.0 fatalities Decrease in 2.4 12.3 11.1 27.6 2.2 6.1 52.9 141.6 repair cost Total 8.2 30.5 213.1 557.5 22.9 62.0 150.6 404.3 dividend 1 DIVIDEND 3 (€, millions) Energy 227.7 227.7 445.3 445.3 139.9 139.9 464.5 464.5 savings CO2 49.0 49.0 334.4 334.4 47.6 47.6 444.0 444.0 savings Total 276.7 276.7 779.7 779.7 187.5 187.5 908.6 908.6 dividend 3 Total 285.0 307.2 992.8 1,337.2 210.4 249.5 1,059.2 1,312.9 benefits COSTS (€, millions) Seismic retrofit 78.0 78.0 270.2 270.2 60.9 60.9 600.9 600.9 costs Energy efficiency 219.5 219.5 645.0 645.0 165.8 165.8 521.6 521.6 improve- ment costs Total costs 297.5 297.5 915.2 915.2 226.7 226.7 1,122.5 1,122.5 BCR 0.96 1.03 1.08 1.46 0.93 1.10 0.94 1.17 NPV −12.5 9.7 77.6 422.0 −16.3 22.8 −63.3 190.4 (€, millions) ERR (%) −4.20 3.26 8.48 46.11 −7.19 10.06 −5.64 16.96 Case studies Earthquakes 98 GREECE ITALY ROMANIA SLOVENIA Building PML Building PML Building PML Building PML design analysis design analysis design analysis design analysis life (475-year life (475-year life (475-year life (475-year analysis return analysis return analysis return analysis return period) period) period) period) DIVIDEND 1 (€, millions) Avoided 77.8 105.5 139.1 150.2 35.7 35.7 6.0 13.7 injuries Avoided 859.1 1,247.3 1,366.8 1,781.8 136.8 188.2 55.1 161.7 fatalities Decrease in 403.0 478.1 609.7 590.0 46.8 56.0 25.7 67.0 repair cost Total 1,339.9 1,830.9 2,115.6 2,522.0 219.3 280.0 86.8 242.4 dividend 1 DIVIDEND 3 (€, millions) Energy 4,440.3 4,440.3 13,510.6 13,510.6 1,418.1 1,418.1 1,616.8 1,616.8 savings CO2 savings 7,278.6 7,278.6 4,191.8 4,191.8 998.6 998.6 380.3 380.3 Total 11,718.9 11,718.9 17,702.4 17,702.4 2,416.7 2,416.7 1,997.2 1,997.2 dividend 3 Total benefits 13,058.8 13,549.7 19,818.0 20,224.4 2,636.0 2,696.7 2,084.0 2,239.5 COSTS (€, millions) Seismic 4,791.2 4,791.2 15,548.2 15,548.2 811.8 811.8 459.8 459.8 retrofit costs Energy efficiency 5,087.3 5,087.3 16,410.3 16,410.3 1,259.9 1,259.9 1,045.7 1,045.7 improvement costs Total costs 9,878.4 9,878.4 31,958.5 31,958.5 2,071.7 2,071.7 1,505.6 1,505.6 BCR 1.32 1.37 0.62 0.63 1.27 1.30 1.38 1.49 NPV 3,180.4 3,671.3 −12,140.5 −11,734.1 564.3 625.0 578.4 733.9 (€, millions) ERR (%) 32.20 37.16 −37.99 −36.72 27.24 30.17 38.42 48.74 Source: World Bank analysis; based on external data Case studies Earthquakes 99 Universities: Table 39: BCA for universities AUSTRIA BULGARIA CROATIA CYPRUS Building PML Building PML Building PML Building PML design analysis design analysis design analysis design analysis life (475-year life (475-year life (475-year life (475-year analysis return analysis return analysis return analysis return period) period) period) period) DIVIDEND 1 (€, millions) Avoided 0.1 0.4 7.3 20.5 13.5 33.9 2.0 5.3 injuries Avoided 1.5 5.1 77.5 241.5 129.1 360.6 24.4 69.9 fatalities Decrease in 0.5 2.7 3.8 14.2 13.4 33.1 7.5 20.3 repair cost Total 2.1 8.2 88.5 276.2 156.0 427.7 33.9 95.6 dividend 1 DIVIDEND 3 (€, millions) Energy 34.9 34.9 104.8 104.8 431.6 431.6 92.9 92.9 savings CO2 savings 7.5 7.5 78.7 78.7 146.7 146.7 88.8 88.8 Total 42.4 42.4 183.5 183.5 578.4 578.4 181.7 181.7 dividend 3 Total benefits 44.5 50.6 272.1 459.7 734.3 1,006.0 215.6 277.3 COSTS (€, millions) Seismic 11.9 11.9 59.5 59.5 183.2 183.2 86.5 86.5 retrofit costs Energy efficiency 33.6 33.6 151.8 151.8 511.5 511.5 104.3 104.3 improvement costs Total costs 45.6 45.6 211.4 211.4 694.7 694.7 190.8 190.8 BCR 0.98 1.11 1.29 2.18 1.06 1.45 1.13 1.45 NPV −1.1 5.0 60.7 248.3 39.6 311.3 24.8 86.5 (€, millions) ERR (%) −2.41 10.96 28.71 117.46 5.70 44.81 13.0 45.34 Case studies Earthquakes 100 GREECE ITALY ROMANIA SLOVENIA Building PML Building PML Building PML Building PML design analysis design analysis design analysis design analysis life (475-year life (475-year life (475-year life (475-year analysis return analysis return analysis return analysis return period) period) period) period) DIVIDEND 1 (€, millions) Avoided 0.018 0.026 0.045 0.066 0.064 0.07 0.0007 0.0003 injuries Avoided 0.14 0.23 0.27 0.41 0.4 0.53 0.001 0.004 fatalities Decrease in 0.006 0.009 0.21 0.28 0.058 0.068 0.0004 0.0013 repair cost Total 0.22 0.35 0.52 0.76 0.53 0.67 0.0001 0.005 dividend 1 DIVIDEND 3 (€, millions) Energy 0.67 0.67 2.25 2.2 1.84 1.84 0.21 0.21 savings CO2 savings 1.09 1.09 0.7 0.7 1.29 1.29 0.005 0.005 Total 1.76 1.76 2.95 2.95 3.13 3.13 0.26 0.26 dividend 3 Total benefits 1.98 2.11 3.47 3.71 3.65 3.8 0.27 0.31 COSTS (€, millions) Seismic 0.61 0.61 2.2 2.2 0.62 0.62 0.005 0.005 retrofit costs Energy efficiency 0.74 0.74 2.74 2.74 1.63 1.63 0.13 0.13 improvement costs Total costs 1.37 1.37 4.94 4.94 2.25 2.25 0.18 0.18 BCR 1.44 1.53 0.70 0.75 1.62 1.69 1.49 1.70 NPV 0.61 0.73 −1.47 −1.22 1.4 1.55 0.089 0.13 (€, millions) ERR (%) 44.42 53.29 −29.77 −24.80 62.18 68.68 49.06 70.54 Source: World Bank analysis; based on external data Case studies Earthquakes 101 Several observations can be made from the BCR • The relative importance of different benefits differs results: across countries depending on their seismic risk, climate, and energy profile. In general, dividend 3 • Investment into strengthening and energy efficiency benefits tend to be high along with the avoided improvement of education facilities yields positive fatalities from seismic retrofit. returns in the majority of the considered countries, considering both design life and PML benefits. Æ Challenges and lessons learned • Co-investment into energy efficiency yields large The earthquake analysis could be completed by benefits and should therefore be considered in inclusion of further aspects as outlined above. Other tandem with seismic strengthening for higher studies have shown substantial benefits of investing in efficiency of investments and lower disruption to upgrading of school infrastructure in Turkey or facilities. The use of innovative combined Romania, which also benefitted from previous technologies is being widely investigated with a lot assessments that calculated benchmark data on of research in this area (for example, a European characteristics of buildings that allowed for precise pilot project on integrated techniques for the calculations of energy efficiency improvement seismic strengthening and energy efficiency of benefits. existing buildings). BENEFITS OF INVESTING IN RETROFITTING OF BUILDINGS IN ROMANIA This case study is an external analysis that was country’s emergency response system a national undertaken with ex-ante analysis that involved priority. And In the last few years, Romania has modelling of hazards. substantially invested in retrofitting buildings, strengthening the country’s preparedness and critical Æ Introduction and background emergency infrastructure, and improving its resilience and emergency response. Below, we will examine Romania is one of the fastest growing economies in the these investments using the Triple Dividend BCA. EU, with growth of 7 percent in 2017 (World Bank, 2018a). Yet, Romania’s vulnerability to geophysical Æ Description and climate-related natural disasters, which will be further exacerbated by climate change, stands in the The World Bank is supporting a series of three types way of the country’s growth trajectory. Romania is one of investment programs in Romania since 2018. of the most at-risk countries from earthquakes in the These investments are all aiming to support the EU, with hundreds of lives lost and tens of thousands of resilience against disaster risks by focusing on the buildings damaged in earthquakes in the last 200 retrofitting and reconstruction of selected public years. In addition to seismic risk, the country is also buildings while promoting sustainability aspects such one of the most flood-prone countries in Europe, and it as energy efficiency. In the aftermath of disaster, it is is susceptible to significant damage from critical that emergency coordination centres and hydrometeorological events occurring several times rescue facilities are undamaged and fully operational, per decade. Lastly, Romania is also experiencing with staff uninjured, equipment undamaged, and increased frequency and intensity of landslides, energy, water, and communication systems wildfires, drought, and extreme heat/cold events. Not functional. It is also critical that expected coverage of only is Bucharest one of the most earthquake-prone emergency operations is not compromised by capital cities in the EU, but it is also ranked fifth among damage to one or more buildings. the fastest-warming cities in the world. With the country’s unique natural hazard risks realized, The three investment programs are focusing in a first Romania is committed to improving their disaster risk phase on critical disaster and emergency response management and making improvements to their buildings: Case studies Earthquakes 102 Strengthening Disaster Risk Management AEP of earthquake hazard at 10 percent in 50 years, (World Bank, 2018a)15 and a corresponding earthquake with magnitude of approximately 7.9. The standard discount rate used The project that started in 2018 amounting to more was 5 percent and the VSL used €559,488 for the than €50.8 million is aiming to enhance the resilience first project (and €575,723 for the other two of critical disaster and emergency response projects). infrastructure and to strengthen the Borrower’s institutional capacities in disaster risk reduction and For the overall BCR, only the results from the first climate change adaptation. This is being achieved by Dividend were considered that were calculated enhancing the resilience of critical disaster and quantitatively and based on modelling scenarios. The emergency response infrastructure and to strengthen other results were presented qualitatively based in the Borrower’s institutional capacities in disaster risk parts on partial quantitative analysis to allow an reduction and climate change adaptation. The project approximation of possible benefits. focuses on around 35 buildings such as emergency coordination centres as well as fire and SMURD For the second Dividend, the Hallegatte framework (Emergency Rescue Service) ambulance services. was used as a benchmark (Hallegatte, 2012). This approach estimates the value of concurrent economic Improving Resilience and Emergency development being equivalent to 8 times the value of Response (World Bank, 2019a) avoided asset losses at the lower end of the spectrum, and 15 times at the higher end. Since, emergency The project that started in 2019 and amounting to response facilities constitute only a small part of an more than €50.92 million is aiming to enhance the overall earthquake hazard mitigation program; it is resilience of Romanian Police Facilities that are critical assumed that the economic development benefits to respond to Emergency Situations and disasters and associated with response building investments would to strengthen the institutional capacities for emergency be approximately equal to the value of the avoided preparedness and response. The project focuses on assets losses at the lower end, and three times as high around 37 buildings of the Romanian police. at the higher end. This logic allows the use a weighted factor of 2 to multiply the avoided asset losses (and Strengthening preparedness and critical related benefits) and to infer benefits due to triggered emergency infrastructure project (World economic development. Bank, 2019b) For the third Dividend, data constraints required an The project that started in 2019 amounting to more approximate calculation of possible benefits. Factors than €41.09 million is aiming to enhance the resilience taken into consideration were the square meters of of Romanian Gendarmerie Facilities that are critical to facilities being rebuild or retrofitted (including the respond to Emergency Situations and disasters and to share of types of interventions), energy efficiency strengthen the institutional capacities for emergency standards by shares of buildings (1/3 of buildings 2020 preparedness and response. The project focuses on targets, rest with moderate energy efficiency targets), around 27 buildings of the Romanian gendarmerie. monthly energy costs per square meter of €1.2 and a 20 (or 30 in two last case studies) year planning Æ Methodology horizon. The BCA for the three investment programs were Æ Results of the analysis by Dividends undertaken in a similar manner using the Triple and overall Dividend framework. Although the components slightly varied between the projects, the BCAs generally The results of the three projects are summarized in the included analysis based on two earthquake scenarios. tables below (Table 40 , Table 41 and Table 42). Overall, The first, EQ scenario 1, has a higher probability with we can see that the BCRs were greater than 1. an AEP of earthquake hazard at 39 percent in 50 years, and a corresponding earthquake with magnitude of approximately 7.5. The second, EQ scenario 2, has an 15 Original values in US dollars. Case studies Earthquakes 103 Strengthening Disaster Risk Management Table 40: BCR of strengthening disaster risk management in Romania (in million €) BCR: 1.7316/1.317 EQ1 EQ2 Dividend 1 benefits €64.5 €48.3 Dividend 1 costs € 37.33 € 37.33 Dividend 2 Dividend 3 Total Benefits €64.5 €48.3 Total Costs €37.33 €37.33 BCR 1.73 1.30 NPV €27.17 €11.02 IRR 14.6% 9.1% Source: World Bank analysis; based on data and information from World Bank (2018a) Improving resilience and emergency response Table 41: BCR of improving resilience and emergency response in Romania (in million €) BCR: 1.5718/1.0519 EQ1 EQ2 Dividend 1 benefits €64.5 €48.35 Dividend 1 costs €44 €44 Dividend 2 Dividend 3 Total Benefits €64.5 €48.35 Total Costs €44 €44 BCR 1.57 1.05 NPV €22.26 €2.01 IRR 10.26% 5.50% Source: World Bank analysis; based on data and information from World Bank (2019a) 16 Earthquake scenario 1 (EQ1). 17 Earthquake scenario 2 (EQ2). 18 Earthquake scenario 1 (EQ1). 19 Earthquake scenario 2 (EQ2). Case studies Earthquakes 104 Strengthening preparedness and critical emergency infrastructure project Table 42: BCR of strengthening preparedness and critical emergency infrastructure BCR: 1.1620 BENEFITS COSTS Dividend 1 €33.9 €29.1 Dividend 2 Dividend 3 NPV €4.8 IRR 6.58 Source: World Bank analysis; based on data and information from World Bank (2019b) This Table 43 compares the cost benefit analysis outputs for all three case studies in Romania considered, giving ranges corresponding to the two earthquake scenarios. Table 43: Comparison of BCA outputs for case studies in Romania STRENGTHENING IMPROVING RESILIENCE AND PREPAREDNESS AND STRENGTHENING DRM EMERGENCY RESPONSE CRITICAL EMERGENCY INFRASTRUCTURE PROJECT FIRST DIVIDEND Lives saved  2900 people (1700 building 1009-2491 (building staff 3636 (building staff and staff and 1200 community and community members); community members); member); €671 million €581 million €251 million Avoided direct stock €25.4 - 54 million €11.3 – 19.3 million €11.3 losses  (including direct damages to (including direct damages to (including direct damages to buildings 12.4-23.9, to buildings 10.1-17.5 and to buildings 10.7 and to equipment 2.2-4.1 and fire equipment 1.2-1.8) equipment 0.6) suppression to surrounding buildings 10.8-26) SECOND DIVIDEND Economic €44-94 million €22.6 million €22.6 million development multiplier effects due to avoided asset losses THIRD DIVIDEND Energy €8 million €7 million €8 million efficiency (energy costs savings) Source: World Bank analysis; based on data and information from World Bank reports cited above 20 Earthquake scenario 1 (EQ1) Case studies Earthquakes 105 Æ Challenges faced and lessons learned Data constraints on buildings specifically are major, which are preventing more precise calculations on It is noteworthy that the project’s efficiency parameters energy efficiency. Ideally energy audits on buildings in both earthquake scenarios are highly sensitive to would be necessary before the project, which would the VSL estimate and the number of lives saved, which necessitate an advance precise definition of which play a vital role in rendering the project feasible in buildings would be intervened in and this was not the economic terms. However, when the aspect of lives approach taken in these investments projects but may saved was eliminated from the analysis, the resulting also constrain estimations for other similar large IRR declined to below zero, indicating an infeasible investment programs led by the public sector. The investment prospect. Thus, an important feature of second dividend benefits are an approximation and this analysis is that the project will not be able to meet are constrained by methodological constraints on efficiency criteria unless the value of lives saved is what can reasonably be accounted for. Additional explicitly considered. In one of the projects for one of empirical literature (ideally global comparative the earthquake scenarios, a negative BCR has been estimates) would support future precise calculations found and this is likely to be due to an underestimation for dividend 2. to the lives saved by the personnel of the gendarmerie. THE BENEFITS OF INVESTMENT IN SCHOOL INFRASTRUCTURE IN TURKEY (WORLD BANK, 2019D)21 Æ Introduction and background Æ Description of the case study Turkey is vulnerable to a wide variety of natural hazards, With this €276.6 million investment (US$300 million), including earthquakes, landslides, and floods. Among 50 schools can be reconstructed and about 300 these, earthquakes have caused the greatest amount schools can be retrofitted over a 5-year investment of human and economic losses, with 90,000 fatalities period. As a result, this would correspond to 1,122,500 and direct losses of €22.3 billion spanning 76 square meters of floor space, providing protection to earthquakes since 1900. In 2005, the Government of approximately 280,000 students at full capacity. Turkey, with support from the Bank, initiated a comprehensive risk reduction program and launched Æ Methodology the Istanbul Seismic Risk Mitigation and Emergency Preparedness (ISMEP) project aimed at improving the Using the triple dividend framework as basis, a BCA resilience of the city’s public building stock and its was performed to inform the Project design. This capacity to respond to disasters. Within this ambitious analysis aims to estimate ERR, NPV and cost-benefit long-term disaster resilience plan, the government is ratios under a set of assumptions. It is conjectured focusing on scaling up risk reduction interventions in that one or more earthquakes (EQ) are expected to the education sector to substantially and systematically hit the targeted provinces in the order of Mw = 6.5 or reduce the risk that students and teachers face from higher leading to similar consequences as that of the earthquakes. Improving education infrastructure is an Marmara EQ, with an expected probability of 5 important strategic priority for the Turkish Government, percent. Human life has been valued as part of the and budget allocations toward such projects have analysis and the concept of VSL was used (VSL of increased in years. The Ministry of National Education €731,440 or US$820,000). (MoNE) is entrusted to oversee the retrofitting and maintenance of public education infrastructure, and Æ Results of the analysis by Dividends between 2003 and 2018, MoNE has invested and overall approximately €14.3 billion in the construction of new schools, reconstruction and retrofitting of existing Assuming that the current asset value is equal to schools, and the acquisition of sites. €133.8 million, the market value of the complete buildings that have been reconstructed, retrofitted, 21 Original values in US dollars. Case studies Earthquakes 106 and fully equipped ultimately results in an increment use a factor of 2 to multiply the avoided asset losses, of €160.6 million for the value of the property yielding some €321 million in benefits due to economic enhanced and saved as a result of project intervention. development even when the disaster never strikes Moreover, it expected that the improved buildings (see Table 44). will provide a safer school environment for some 280,000 students, 0.6 percent of whom risk losing Despite data paucity being a problem in this category their lives in the event of an earthquake without this of benefits as well, energy efficiency improvements in intervention. Consequently, this corresponds to a child existing public buildings are in the positive list of co- mortality estimate of 1680 for daytime and 910 for an benefits related to mitigation of climate change and average number after adjustments. yield savings on lighting, water and heating investments. The recent ISMEP Economic Impact Assessment As a possible benchmark we have used the Hallegatte (World Bank, 2018b) has calculated some benchmark framework (Hallegatte, 2012), which deals with hydro- data which have been imported for use. According to met related hazards, investments and benefits, where ISMEP, the monetary values of saving in lightening, the author estimates the value of concurrent economic water consumption, and heating per square meter are development being equivalent to 8 times the value of €0.0021, €0.020, and €2.418, respectively. It is avoided asset losses at the lower end, and 15 times at expected that 350 schools with 1.122.500 square the higher end. Since safe schools constitute only a meters of surface areas are to be intervened within the small part of an overall earthquake hazard mitigation Project, which would result in savings of about €2.68 program, we assume that the economic development million per annum and €41 million over the planning benefits associated with safe schools investments horizon with or without an earthquake occurring. This would be approximately equal to the value of the analysis is being extended to deal with the question of avoided assets losses at the lower end, and be perhaps social value of carbon. twice as high at the higher end. This logic allows us to Table 44: BCR of Turkey school infrastructure investment per dividend BCR: 1.53 BENEFITS COSTS Dividend 1 €660 million (gross) €267.6 million (gross) Dividend 2 €160.6 million (gross) Dividend 3 Total benefits €820.6 million (gross) Total costs €267.6 million (gross) BCR 1.53 NPV €120.4 million ERR Source: World Bank analysis; based on data and information from World Bank PADs Æ Challenges faced and lessons learned calculated benchmark data on characteristics in buildings (lightning, water consumption, heating per In addition to the sensitivity of results to the choice of square meter) that allowed for a more precise VSL, it can be said that the economic analysis under calculation of energy efficiency improvements this project benefitted from previous assessments that benefits. Case studies Earthquakes 107 3.2.3. EARTHQUAKE EARLY 2011) and Turkey (Alcik, et al., 2009). WARNING SYSTEMS The study by Cremen examines the feasibility of EEWS An EEWS is an effective measure for reducing risks for Europe. The initial analysis examines the density of from European earthquakes, which consists of station coverage across the continent and finds that physical infrastructure and software that can alert over half of the interdistance ranges between 0 km stakeholders (for example, the public and civil and 20 km are optimal for EEWS performance (Cremen, protection offices) to an incoming earthquake seconds et al., 2020). This is a preliminary signal that there is to minutes before they experience the resulting strong significant potential for operational EEWS across the shaking. During this time, actions can be taken to content. The report also finds that 44 percent of the significantly decrease detrimental impacts from examined target sites benefit from warning times that shaking (Cremen, et al., 2020). These actions include, are long enough to accommodate major risk but are not limited to, performing drop, cover, and intervention actions, such as shutting down of hold on (Porter, 2016) to avoid lives lost and injuries; industrial equipment or the removal of vehicles from moving to a safer location either within a building or garages. The longest lead times are found in Greece, outside to avoid injuries; slowing down high-speed Turkey, and Iceland, while the shortest lead times are trains (Fabozzi, et al., 2018); shutting off gas pipelines in north-western Georgia and southern Russia. The to prevent fires; and switching signals to stop vehicles work provides strong evidence that an operational from entering vulnerable infrastructure components EEWS could be an effective tool for supporting (Le Guenan, et al., 2016). earthquake-related DRR across a significant portion of Europe. This benefits the new three-year Horizon 2020 The Euro-Mediterranean area has a strong need for European project called TURNkey (European effective EEWS and measures for mitigating seismic Commission, 2021). The project seeks to develop a risk (Crowley, et al., 2018). This is due to the estimation holistic earthquake information system that of annual European GDP affected by earthquakes incorporates seismic risk mitigation tools for both which exceeds €17.7 billion (World Bank, 2017a). In operational forecasting and EEWS in real and near-real addition, the only European countries with current time, with selected testbeds in Italy and Greece to be operational EEWS are Romania (Mărmureanu, et al., the focus of more detailed analysis. EARTHQUAKE EARLY WARNING IN BUCHAREST This case study is a new ex-post analysis under this of people with a view to releasing a set of mobile project that involved modelling of hazards. applications that will be freely available for general users (Clinton, 2016). Æ Introduction and background Æ Description Currently, the Romanian Seismic Network consists of 73 digital seismic stations that have been installed This case study is an appraisal of the EEWS in since 1995 for warning critical facilities. Bucharest is Bucharest as part of the DACEA program 2007–2013 situated 140–170 km from the Vrancea epicentre that was partially funded by the EU (Dimitrova, et al., zone and encountered great damage and casualties 2015; European Union, 2021; European Commission, from the high energy Vrancea earthquake in 1977 and 2015). The DACEA program seeks to prevent natural other events on the same subduction zone. The lead disasters generated by earthquakes in the cross- time is predicted to be 25–27 seconds for an EEWS to border area of Romania and Bulgaria through early issue preventive actions at the warned facility. Key warning integrated communication networks. Due to facilities that trigger action upon receipt of alerts the high seismicity in the cross-border area, the include the Nuclear Research Institute in Bucharest, nuclear power plants and chemical plants located the Basarab Bridge, and the Vidaru Dam. The National along the Danube are particularly vulnerable to Institute for Earth Physics (NIEP) that operates the earthquakes. The project provides a response system real-time national network is currently testing the that can alert authorities to help avoid natural disasters communication performance with a restricted group caused by earthquakes by promptly shutting down Case studies Earthquakes 108 critical infrastructure like nuclear power plants, included in the BCA. elevators, and trains, as well as reducing negative impacts to the environment. The case study Data used for the case study were as follows: undertaken is a hypothetical appraisal of the EEWS operationalized to reduce losses, focusing on the • Total investment information from the project for defined investment of the DACEA program for nuclear EEWS cost, half of which is assumed to be applied and infrastructure alerting. The program included the to Bucharest (European Union, 2020) installation of 16 earthquake sensors in the cross border area.22 • Data from the United States (Strauss and Allen methodology) for cost of one train car and cost of Æ Methodology maintenance of EEWS, adjusted to Romanian consumer price indexes (Strauss & Allen, 2016) As few methodologies exist for systematically evaluating the costs and benefits of the EEWS, this • Eurostat symmetric input-output tables for study employs a recent methodology by Strauss and construction sector macroeconomic benefits. The Allen (2016) that estimates the costs and benefits of EU estimation for construction sector input of every the ShakeAlert system in the Western United States. €1 yields €0.47 of value added to other industries Quantifying the benefits of the EEWS will include (European Commission, 2021). This is an indirect assessing the annual costs of creating and maintaining and direct economic value added from the an EEWS compared to the costs and savings from construction or installation of sensors and other annual avoided losses. In the methodology applied to infrastructure for EEWS. Bucharest, benefits are hypothetical and conservative losses avoided are estimated based on infrastructure Æ Results of the analysis by Dividends alerting to the train/transportation sector. and overall Due to the challenges and variability in predicting the The overall benefit is greater than 1 compared to the full benefits of earthquake early warnings, the case annualized cost including up-front investment for the study intends to compare the expected first-time start- EEWS in Bucharest (see Table 45). The benefits up cost of installation and maintenance to a highly computed are those of direct losses avoided and value conservative set of benefits. The costs are compared added to the greater economy by investment in to the avoidance of one fatality avoided and the construction projects. The true BCR is likely much physical asset loss avoided of one train being derailed. larger but difficult to capture in the life span of use The objective is to compare the incremental losses considering the return periods of low-frequency, high- avoided to the start-up cost and maintenance of the consequence earthquake impacts. However, the EEWS. Due to a lack of available data, the losses inclusion of loss of life avoided when comparing the avoided from nuclear and chemical earthquake early full costs of implementation will typically yield high warning are not included in the study. BCR values as indicated below. In addition, the losses avoided from environmental pollution due to the As earthquake early warning has a short lead time reduction and prevention of natural and technical risks (up to 27 seconds in Bucharest) (Neagoe, 2016), its will likely increase the BCR. There are also co-benefits main purpose is to prevent loss of life and injuries. such as increased awareness by alerting for EEWS There are also other immediate organizational actions that have positive social consequences but are difficult that can be taken (both automatically or procedurally), to capture in a quantitative BCA. High and low values such as turning off gas pipes to avoid conflagration, based on upper and lower bound limits of the cost of or slowing down trains to avoid derailment—and hence train derailment (low of €3.2 million per train car and lowering the likelihood of causalities and asset loss. high of €26.8 million) results in a BCR range of Therefore, while other co-benefits may exist, these are 3.4–11.1 (see Table 46). largely unexplored in literature and therefore not 22 The team assumed that half of the sensors were installed in Bucharest. Case studies Earthquakes 109 Table 45: BCR of implementing EEWS in Bucharest, Romania (in million €) BCR: 7.0 BENEFITS (€) COSTS Dividend 1 20.64 Dividend 2 1.34 Dividend 3 n.a. Total benefits 21.98 Total costs 3.06 BCR 7.17 NPV 18.92 ERR (%) 617.33 Source: World Bank analysis; based on external data and information Table 46: Detailed breakdown of implementing EEWS in Bucharest, Romania (in million €) FIRST DIVIDEND (€) Life saved 5.91 Train derailment avoided 14.18 Total first dividend 20.09 SECOND DIVIDEND (€) Value-added to broader economy from construction of EEWS 1.34 infrastructure Total second dividend 1.34 First cost item First time capital cost of sensors and monitoring system 2.85 SECOND COST ITEM (€) Maintenance cost 0.21 TOTAL DIVIDEND 21.43 Total cost 3.06 BCR 7.0 NPV (€) 18.36 ERR (%) 599.27 Source: World Bank analysis; based on external data and information Note: All values are in 2013 euros as this was the end of the programming year for funds. Case studies Earthquakes 110 Æ Challenges faced and lessons learned • Including fire following earthquake damage avoided with manual and/or automated gas shut Very little data exist on the full benefits of an EEWS in offs; Europe, particularly in Bucharest. It is challenging to disaggregate a multi-alert system like the one found in • Assessing the costs and benefits over a reasonable France, and some judgements must be made to time horizon, capturing the longevity of such a estimate a cost per incremental sensor installation system as well as longer-return-period earthquakes and maintenance over time to constitute a meaningful and their consequences; BCA. For future studies with additional data available, the BCA could expand on • Evaluating the losses avoided of environmental damage from natural and technical disasters in the • Accurately estimating alerting system as well as cross-border area; and monitoring and evaluation costs; • Quantifying the benefits of increased awareness • Determining the efficiency of alerting dissemination and use of EEWS by personnel operating critical of EEWS; infrastructure to further reduce losses. This also includes quantifying the level of effective awareness • Providing specific information on costs like nuclear building that should be included as a regular cost to damage, chemical, industrial, and other critical implementing any EEWS (Becker, et al., 2020). infrastructure damage; 3.2.4. RESPONDER CAPACITY BUILDING The case studies described in this section are new ex post analyses under this project that involved an innovative quantification of benefits from soft investments. INTRODUCTION TO THE ASSESSMENT OF ECONOMIC BENEFITS OF CAPACITY BUILDING IN DISASTER RISK PREVENTION The case studies described in this section are new initiatives are shown in Figure 20 and see Annex 4 for ex post analyses under this project that involved further details). Personnel and modules (self-sufficient an innovative quantification of benefits from soft civil protection capacities capable of overseas investments. deployment) are trained in many aspects of the international response context. Benefits are numerous, Æ Introduction and background ranging from improved coordination between international resources from different countries and The effectiveness of disaster response is directly the Host Nation to improved effectiveness of on-the- associated with the skills of the responders at a disaster ground personnel in this international response site as well as their effective coordination with other context (Perry, 2004). resources deployed (Sinclair 2012). Therefore, it is essential for authorities to establish emergency Æ Description management training and live exercise programs to build capacity of responders and response A BCA is conducted of DG ECHO investments in coordinators. emergency responders and response coordinators through the UCPM/Union Civil Protection Knowledge DG ECHO funds capacity building of civil protection Network. Two specific events are considered: the personnel through what is now called the Union Civil November 2019 Albania Earthquake and the March Protection Knowledge Network (capacity-building 2020 Croatia Earthquake. The Albania earthquake Case studies Earthquakes 111 was magnitude 6.3; killed 51 people; damaged response had received international training. See 39,000 residential buildings; required 17,000 people Annex 4 for a more detailed description of the to be housed in temporary accommodation; and led to Knowledge Network23 and the two case study events. a significant international response including personnel on-the-ground, in-kind assistance, and Æ Methodology international pledges from multiple donors. The Croatia earthquake was of magnitude 5.5, killed one The costs and benefits assessed quantitatively for person, damaged 26,000 buildings, and displaced these events are shown in Figure 20. The calculation 30,000, and although there were no EU personnel methodology, the additional costs/benefits assessed deployed internationally (due to COVID) many of those qualitatively, and key results are described in more responsible for the national coordination of the detail for each case study in the next sections. Figure 20: Costs (investments) and benefits considered for quantitative analysis to provide the BCR. Note that additional costs/benefits are analysed both quantitatively and qualitatively and discussed in the text Source: World Bank analysis Note: Additional costs/benefits are analysed both quantitatively and qualitatively and discussed in the main report. CP = civil protection; EUCPT = European Union Civil Protection Team; MODEX = module exercises; UCPM = Union Civil Protection Mechanism. The analysis for both case studies is conducted in four questionnaires to targeted experts in coordination stages: roles in both case-study events 1. Calculate costs of training and deployment of Costs and benefits are calculated only for the events EUCPT, modules, and other capacities that considered. This means that benefits that may occur responded to the case study events, either for future events are not expressly calculated (for internationally (Albania earthquake) or nationally example, trained personnel may deploy to multiple (Croatia earthquake). events). that is, calculations are deterministic, based on specific real events, not a probabilistic calculation 2. Calculate benefits associated with (a) urban based on possible future scenarios. search and rescue (USAR) and (b) post-disaster damage assessment. Qualitative analysis of these additional costs and benefits is conducted through questionnaires, which 3. Outline costs and benefits that have not been aim to determine whether international training or included in the BCR calculation above. experience of previous deployments improved response to the case study events. The questionnaire 4. Evaluate these additional costs/benefits using was sent to: 23 Note that the term ‘Knowledge Network’ is used throughout to refer to the training activities shown in Figure 20. This also refers to these activities, even before the term was formalized in 2019. Case studies Earthquakes 112 1. International teams and EUCPT members who with peers to create synergies in respective work areas, deployed to the case study event (Albania) and and (f) intrinsic value of knowledge networks and trainings for people to feel as part of a community of 2. National civil protection staff who have received practitioners and contribute to a greater cause. The international training and were in a coordination advantages of WTP to capture some of these more role during the case study event (Croatia). intangible benefits may also be a disadvantage, given that it may be difficult to disentangle the various 3. Alternative methods considered. benefits and therefore to describe what kind of monetary benefits specifically these knowledge In a theoretical case, we would be able to either networks would have, for example, in terms of actual directly compare the effectiveness of interventions of disaster response. More details on WTP methodologies international teams in comparable disaster situations can be found in Annex 4. Although the team was not before and after a training, and thereby reduced using a full WTP methodology, it aimed to create negative impacts or increased benefits, or compare questionnaires and distributed to relevant teams to the performance of teams with and without training pilot possible approaches that could approximate during the same disaster in geographically separated WTP methodologies, would collect more qualitative areas but with similar characteristics. However, as information on benefits of knowledge networks, and these theoretical scenarios are not available, we would collate subjective estimates from expert instead examine the real emergency responses to the practitioners on what they would perceive the share of Albania and Croatia earthquakes to create possible benefits from knowledge networks and trainings to be counterfactual scenarios (‘what-if’ analysis) and in terms of actual disaster response on the ground. thereby estimate the possible added value of these More details and results from the pilot surveys can teams. be found below as well as information on the questionnaires sent is provided in Annex 4. The first approach is to create logical links between coordination mechanisms and training, improved Æ Results of the analysis by Dividends rescue and coordination or provision of damage and overall assessments during a disaster, and lives saved or reduced losses in productivity, for example. As the The analysis finds positive net benefits for capacity- latter have a monetary value, it is then possible overall building investments related to disaster risk reduction to estimate monetary benefits from the original and response. Overall, for both case studies, the provision of training and coordination mechanisms. following can be further noticed: However, this is only possible in the case of disasters where these logical links can somehow be created (for • Effective coordination of USAR and post-disaster example, in the case of the quantitative calculation for damage assessments are significant contributors Albania outlined below). to lives saved and to saved costs of temporary accommodation and GDP-per-capita loss of Another method often used to estimate more intangible displaced people, by facilitating a rapid return investments such as training or upgrading of natural to work and to medium-term/permanent spaces is to apply a willingness to pay (WTP) method accommodation. to be able to estimate the perceived benefits of the investment in monetary terms. This method would • Coordination effectiveness is improved through have the advantage of capturing several benefits of international training (such as that through the trainings, including (a) better response capacity of knowledge network). teams and individuals during their deployment, (b) improved ‘peace of mind’ to those displaced by • A BCR greater than 1 has been found, even where damage assessments providing certainty on damage there is no deployment of personnel through the to their homes and businesses, (c) enhanced potential UCPM, in cases where national resources earnings or career opportunities, (d) enhanced human coordinating response have received international capital and knowledge that they can transmit to others training. (positive spillover effects), (e) networking opportunities Case studies Earthquakes 113 • This BCR greater than 1 is found even when making accurate evidence-based damage assessments. the conservative assumptions to ignore (a) co- benefits (dividend 3) of career benefits for These results make a quantitative case for DG ECHO’s international rescuers, coordinators, and assessors investments in capacity building through the who have received international training/ knowledge network, even in cases where the trained deployments and (b) economic impacts (dividend personnel are not deployed internationally. 2) of international finance made available due to BENEFITS OF KNOWLEDGE NETWORK INVESTMENTS DURING THE ALBANIA EARTHQUAKE Æ Description international assistance is calculated based on data from the November 2019 earthquake, and During the Albania earthquake in November 2019 in observations in the September 2019 Albania Durres, the EU response to the event included Earthquake for which damage assessments were deployment of an EUCPT, and several modules, other conducted without international assistance. These capacities, and in-kind assistance were deployed both observations were made directly by the author of through UCPM and on a bilateral basis. International this section, who was an EUCPT member in both the assistance facilitated both live rescues and damage September and November 2019 events. assessments. See Annex 4 for further description of event and international response. Co-benefits (dividend 3) are calculated as improved job prospects for those who have received international Æ Methodology training. This also encompasses capacity-building of local assessors, who received training through Costs of deployment are calculated for the EUCPT, knowledge-exchange with international assessors. modules, and other capacities. Both capacities that The benefit is quantified as a small estimated uplift of are deployed through the mechanism and bilaterally final salary at retirement, with an assumed linear are considered (but only those registered on the increase in annual salary from current to final salary. VOSOCC24 or with the Damage Assessment Coordination Centre [DACC]). Costs are separated by Benefits of USAR are calculated from the number of those borne by DG ECHO or the sending country. lives saved: Figure 21 ranks the various costs and benefits, showing that the cost of training outweighs the 1. Direct rescues by internationally trained costs of deployment, and that modules are a higher personnel; cost than the EUCPT. The total of these costs is less than the combined benefits of lives saved and reduced 2. Rescues achieved after international coordination costs of temporary accommodation and production established, established through the USAR loss for those displaced. Coordination Cell (UCC). Benefits of damage assessment are calculated based Benefits of post-disaster damage assessment are on the time saved due to international assistance/ calculated through a counterfactual analysis (Woo G. , training. The approach assumes that people are able 2019) that is, an estimate of the time taken for to return to medium-term/permanent accommodation assessments to be completed with no international and work sooner, with faster and more effective assistance/training. The bases for these estimations damage assessments. This time is then associated are described in the case studies below. Benefits with cost savings due to reduced time in temporary considered are shown in Figure 21 and Table 47, and accommodation and the associated reduction in GDP these benefits are achieved through both: per capita. The difference in time with/without 24 VOSOCC = Virtual On-Site Operations and Coordination Centre, part of the Global Disaster Alert and Coordination System (GDACS). Case studies Earthquakes 114 1. Direct assessments by international assessors Æ Results of the analysis by dividends and and overall 2. Improvements in the overall damage assessment The results of the quantitative analysis (Table 47) show coordination system due to international that the benefits of saving lives, getting people back to assistance (Albania earthquake) or national staff work, and providing certainty on the status of damaged with international training/deployments (Croatia buildings outweigh the costs of training and deploying earthquake). personnel through the UCPM, even without considering private co-benefits for individuals (Dividend 3). For Data are gathered and summarized for other costs and context, the PDNA-estimated losses (not physical benefits that have not been included in the BCR damages) from the event were €141 million (€116 calculation. These are listed in the text beneath million for housing and productive sectors). Table 48. It can be noted that the BCR does not include dividend 3, which includes some private benefits for individuals (see description below). If dividend 3 is included, then the BCR rises to 2.7. Figure 21: Costs and benefits further broken down and ranked for each actor. Note that costs and benefits are often associated with different actors Source: World Bank analysis Note: Costs and benefits are often associated to different actors. DG ECHO = Directorate General for European Civil Protection and Humanitarian Aid Operations; EUCPT = European Union Civil Protection Team. Case studies Earthquakes 115 Table 47: Capacity-building BCA for November 2019 Albania Earthquake BCR: 1.9 BENEFITS COSTS Dividend 1 (€, millions) 7.10 Dividend 2 (€, millions) 3.00 Dividend 3 (€, millions) 6.00 (1.10 within Albania, 4.90 internationally) Total (dividends 1 and 2) 11.30 6.0 Total costs 6.00 BCR 1.88 NPV (€, millions) 5.00 ERR (%) 88.33 Source: World Bank analysis; based on external data and information Table 48: Detailed breakdown of BCA items for case study: November 2019 Albania Earthquake COSTS (€, MILLIONS) FIRST COST ITEM (€, millions) Deployment of modules and EUCPT personnel 2.8 Second cost item Training of modules and EUCPT personnel that deployed to 3.2 Albania DIVIDENDS DIVIDEND 1 (€, millions) Lives saved due to improved emergency response/coordination 2.80 Saved costs of temporary shelter/accommodations 4.30 Reduced costs of managing national assessors 0.03 Total first dividend 7.10 DIVIDEND 2 (€, millions) Reduced loss in productivity or income of those displaced 3.00 Total second dividend 3.00 DIVIDEND 3 (€, millions) Improved job security and final salary for deployed Albanian 1.10 assessors (capacity building of local engineers) (not included in BCR) Improved job security and final salary for 1.40 trained international rescuers (not included in BCR) Improved job security and final salary for 3.50 deployed international assessors Total second dividend 3.00 Total cost 6.00 Case studies Earthquakes 116 Total benefits 11.30 (not including dividend 3 benefits to international individuals) BCA 1.90 (not including dividend 3 benefits to international individuals) NPV (€, millions) 50.00 ERR (%) 88.33 Source: World Bank analysis; based on external data and information BENEFITS OF KNOWLEDGE NETWORK INVESTMENTS DURING THE CROATIA EARTHQUAKE Many of the assumptions and methods used are as per time with/without international training is estimated the Albania case study and are therefore not repeated based on comparison with other events and responses here for brevity. A brief description of the Croatia during interview with the Zagreb damage assessment Earthquake case-study is provided here. leads, many of whom had received international training and experience including Æ Description of the case study • PDNA Training ( DPPI SEE, 2020) Due to COVID-19 and the smaller size of the Croatia • MATILDA Structural Assessment Training, earthquake in March 2020 (no national state of • Previous deployment to the November 2019 emergency, no USAR undertaken), no EUCPT or Albania Earthquake for damage assessment, and modules were deployed to Zagreb. However, in-kind • PhD incorporating Damage Assessment in Croatian and financial assistance was provided, and many of (ROSE School, University of Pavia). those responsible for the national coordination of the response had received international training (through Co-benefits (dividend 3) are calculated as improved the knowledge network or otherwise). International job prospects for those who have received international training facilitated a successful damage assessment training/experience. See the Albania description programme, which in turn facilitated a faster return to above for the assumptions/method. work and to medium-term/permanent accommodation for those immediately displaced. See Annex 4 for Note that the recent earthquake in Croatia is another further description of the event and international example where capacity-building benefits accrued response. and it could potentially be assessed using the same methodology but adapting it to a different scenario in Æ Methodology terms of assessors, location, and hazard impact. Costs of training are calculated for Croatia civil Co-benefits (dividend 3) are calculated as improved protection personnel. Only costs borne by DG ECHO job-prospects for those that have received inter­ are considered, that is, costs of the activities now part national training/experience. See Albania description of the knowledge network (Table 50). above for assumptions/method. Benefits of damage assessment are calculated based Note: The recent earthquake in Croatia is another on the time saved due to international training. See the example where capacity building benefits accrued Albania description above for assumptions/method. and it could potentially be assessed using the same The counterfactual assessment is based on the ‘what- methodology, but adapting it to the different scenario if scenario’ of assessments without the expertise of the in terms of assessors, location and hazard impact. Zagreb damage assessment leads. The difference in Case studies Earthquakes 117 Æ Results of the analysis by dividends Results also show that benefits of capacity building and overall accrue over several events, as those who led the Zagreb damage assessment had received inter­ The results of the quantitative analysis (Table 49) show national training and applied that training to both the that the costs of training personnel through the UCPM Albania earthquake and Croatia earthquake. are outweighed by the benefits of providing certainty Furthermore, the experience of the recent Albania on the status of damaged buildings (facilitating earthquake aided the rapidity of the response for the getting people back to work and into medium-term/ damage assessment leads. permanent accommodation), even when trained personnel do not deploy internationally. Table 49: Capacity-Building BCA for March 2020 Croatia Earthquake. BCR: 1.1 BENEFITS COSTS Dividend 1 (€, millions) 0.9 Dividend 2 (€, millions) 1.3 Dividend 3 (€, millions) 1.5 Total benefits (€, millions) 3.7 3.4 Total costs (€, millions) 3.4 BCR 1.09 NPV (€, millions) 0.3 ERR (%) 8.82 Source: World Bank analysis; based on external data and information; Note that this is a conservative estimate as costs include all civil protection personnel (who contributed to all aspects of the response), but the benefits are only calculated for the damage assessments. Table 50: Breakdown of BCA items for the case study: March 2020 Croatia Earthquake COSTS (€, MILLIONS) FIRST COST ITEM (€, millions) Training of national civil protection (civil protection staff and modules) 3.4 through the knowledge network BENEFITS (€, millions) DIVIDEND 1 Saved costs of temporary shelter/accommodations (due to more 0.8 effective damage assessment) Total first dividend 0.8 DIVIDEND 2 Reduced loss in productivity or income of those displaced (due to 1.3 more effective damage assessment) Total second dividend 1.3 DIVIDEND 3 Case studies Earthquakes 118 Improved job security and final salary for deployed Croatian assessors 1.1 (valuable experience for local engineers) Improved job security and final salary for trained CP personnel 0.4 Total third dividend 1.5 Total cost (€, millions) 3.4 Total benefits (€, millions) 3.7 BCA 1.1 NPV (€, millions) 0.3 ERR (%) 8.82 Source: World Bank analysis; based on external data and information Æ Challenges faced and lessons learned events, without including the added uncertainty of probabilistic calculations for possible events. Benefits not considered include (not exhaustive) the following: • Diplomatic and political benefits. International responses fall within a range of diplomatic tools • PDNA supported by damage assessment data. For used to boost international standing and relations example, in Albania, the joint EU/World Bank/UN (besides the prime goal of saving lives and PDNA relied on damage data collected through livelihoods). The benefits of this would be difficult to damage assessment coordinated by the EUCPT quantify and have not been considered. and UN Disaster Assessment and Coordination (UNDAC). • Mental health costs of displacement and ‘peace of mind’ of international assessments/assistance. • International finance made available due to This is evident from experience on the ground but accurate evidence-based damage assessments. difficult to quantify. For example, in Albania, the PDNA led to a donor conference resulting in €1.15 billion of pledges. In • Inspection of critical infrastructure (bridges, Croatia, the RDNA supported the EU’s provision of hospitals, and so on). The cost-benefit calculations €683.7 million through the EU Solidarity Fund. only consider assessment of residential buildings, These are omitted in the BCR calculation as it is as it is assumed that critical infrastructure would be difficult to define which pledges would not have prioritized and assessed by local competent been made without the internationally supported engineers regardless of international assistance. damage assessments. Costs not considered include (not exhaustive) the • In-kind assistance. While the monetary value of the following: donated goods may be estimated, the benefits from their use would require more detailed data and • Training personnel who do not deploy analysis. This could perhaps be addressed in future internationally. Not all persons trained through the BCAs, with sufficient data. knowledge network will deploy internationally. The costs of training these additional personnel are not • Benefits accrued over multiple events (national and considered, as it is shown in this study through international). All costs and benefits are for the interview and questionnaires that the skills learned specific case study event. Benefits from training are also valuable for national deployments (which being applied to multiple events (past or possible trained personnel are assumed to partake in). This future events) have not been considered. This is to is demonstrated clearly with the Croatia case study. maintain a consistent focus on the known case study Case studies Earthquakes 119 • Staff and overheads outside of the deployed (and costs) occur regardless of international teams. For example, the time and overheads for the deployment/training. Emergency Response Coordination Centre (ERCC), EU Delegation, and Copernicus Satellite activation • Costs due to non-EU training. This may include are not considered. training from the UN, Disaster Preparedness and Prevention Initiative (DPPI), PDNA, International • Costs of module upkeep/salaries (outside of Federation of Red Cross and Red Crescent deployment). These are not considered, as Societies (IFRC), and so on. This is omitted as the deployed modules fulfill more ‘day-to-day’ functions focus of this study is on benefits from DG ECHO than when they are not deployed. These functions investments. Case studies Earthquakes 120 3.3. Extreme Heat 3.3.1. SUMMARY OF FINDINGS FOR on the health of European citizens and have saved EXTREME HEAT thousands of lives during the summertime. With EU funding, the Municipality of Cascais, Portugal was able A significant number of studies have been undertaken to transform the Ribeira das Vinhas valley into a natural to analyse heat risk and its social and economic green wind corridor that provides a cool place for local impacts, yet these analyses were usually conducted residents when heatwaves strike. In Bologna, Italy, EU- with the goal of understanding the effects of climate funded satellite data was used in city-planning, with change. As a result, these studies usually exhibit the goal to install 10 green roofs on public buildings limitations and cannot present the burden of heatwaves and create more green spaces in the city centre entirely (Schmitt, et al., 2016). The Intergovernmental (European Union, 2020). In addition, the European Panel on Climate Change (IPCC) (Murray & Ebi, 2012) Copernicus Climate Change Service (C3S) also pointed out that many existing studies emphasize (Copernicus, 2021) have provided information the impacts on infrastructures and assets in about the temperature and climate in European comparison to those on human health and the countries as well as useful climate indicator tools that ecosystem. Also, there were studies on the costs and can be accessed by the public, which enhance benefits of investments in heat risk reduction being authorities’ preparedness and response to heatwaves. conducted across Europe. For instance, an economic assessment has been undertaken to examine the In this section, we demonstrate benefit-cost effectiveness of heatwave warning systems (HWWS) in assessments for green and white measures25 to Europe. BCAs were undertaken under several mitigate the UHI effect and heatwave EWS for overall scenarios that represent long-term climate changes heatwave impacts. BCAs for different types of and weather variabilities, and the result shows positive interventions are undertaken with detailed quantitative outcomes for most of the analyses (Hunt, et al., 2017). analysis including modelling, with both prospective and retrospective assessments, and qualitative reviews The European Union has supported national and local of other examples. Table 51 summarizes main data investments in natural solutions that deal with extreme and information sources. heat, which reduce the negative impacts of heatwaves 25 Green measures here refer to green roofs, whereas white measures refer to highly reflective surfaces such as walls, roofs and streets. Case studies Extreme Heat 121 Table 51: Overview of data and information sources for extreme heat analysis INVESTMENT CASE STUDY DATA SOURCE NAME AND REFERENCE UHI effects Green and • An estimation of the attributable number of deaths according to the methodology white of Gasparrini and Leone, published in Attributable Risk From Distributed Lag solutions to Models the UHI effect in Vienna • Urban climate model for Vienna, published in Modelling Reduction of Urban Heat Load in Vienna by Modifying Surface Properties of Roofs • Daily climate variables obtained from the Central Institutions of Meteorology and Geodynamics, Vienna Austria • Daily air pollution obtained from the Environment Agency Austria • Daily mortality obtained from Statistik Austria • Reduction in labour productivity estimated with the approach used in Costs of Climate Change: The Effects of Rising Temperatures on Health and Productivity in Germany • Heating and cooling savings estimated according to Green Roof Valuation: a Probabilistic Economic Analysis of Environmental Benefits • World Bank’s Guidance Note on Shadow Price of Carbon in Economic Analysis Heat early HEWS for • Reduction of heat-related morbidity based on estimations performed by Dé warning reducing Donato et al. in the article Changes in the Effect of Heat on Mortality in the Last system(s) health 20 Years in Nine European Cities: Results from the PHASE Project (HEWS) impacts of heat in Paris • Reduction in heat-attributable deaths based on assumptions from ‘Climate and Weather Service Provision: Economic Appraisal of Adaptation to Health Impacts and Valuing Deaths or Years of Life Lost? Economic Benefits of Avoided Mortality from Early Heat Warning Systems’ • Information on cost of HEWS obtained from the National Observatory for the Impacts of Global Warming (Observatoire National sur les Effets du Réchauffement Climatique, ONERC) report ‘Climate Change: Costs of Impacts and Lines of Adaptation’ Source: World Bank analysis; based on external data and information Models need to be adapted to the type of investment attributable mortality is made. analysed. To estimate the impacts of extreme heat, epidemiological models are used to determine the Although significant research has been put into the temperature-mortality and temperature-morbidity understanding of the health-related impacts of relationships, which indicates the vulnerability of the extreme heat, it is also important to consider costs and population. Adequate data on hospital admissions are benefits, as citywide implementation efforts can incur often not available, and linear approximations are significant sums. BCRs of HEWS tend to be high even if made from the temperature-mortality response. For using a VOLY or a VSL approach. Recent studies from UHI effects, urban climate modelling is incorporated academic literature indicate BCRs to range between to estimate reductions in extreme heat (for example, 23 (London) to 1,375 (Madrid) (Hunt, et al., 2017) the number of hot days) given a scenario of green or depending on the climate of the city, effects of climate white solutions implementation, which is then change, socio-demographic change, and how reduced combined with spatially explicit population data to mortality is valued (that is, premature versus displaced estimate the exposure of the population to these deaths) (Chiabai, et al., 2018). For mitigating the extreme temperature reductions. For the HEWS, a UHI effect, complete cost-benefit analyses of comparison of the temperature-mortality relationship citywide application of green and white solutions before and after the implementation is assessed, are still lacking in the literature, with only one study and an approximation of the reduction in heat- finding BCRs of combined green and white solutions Case studies Extreme Heat 122 to range between 1.3 and 2.7 for small and medium- Figure 22 presents boxplots that display the size cities in Austria (Johnson, et al., 2020). distribution of BCRs for different types of investments in extreme heat based on a five-number summary: Results of the analysis are generally showcasing net minimum (shown in orange), first quartile, median benefits of interventions. This is consistent with (shown in red), third quartile, and maximum (shown in findings in the literature for heatwaves prevention, orange). The outliers are shown as dots. Extreme although it has to be noted that the case studies values are excluded from the top graph and included considered are also different in terms of scales of in the bottom one. investments. More details are included in Figure 22, Figure 23 and Figure 24. Figure 22: Findings of benefit-cost analysis for extreme heat (B/C ratios) Source: World Bank analysis; based on external data and information Figure 23 below presents boxplots that display the number summary: minimum (shown in orange), first distribution of NPVs (in millions of EUR) for different quartile, median (shown in red), third quartile, types of investments in extreme heat based on a five maximum (shown in orange). Case studies Extreme Heat 123 Figure 23: Findings of benefit-cost analysis for extreme heat (NPVs) Source: World Bank analysis; based on external data and information Figure 24 below presents boxplots that display the (shown in red), third quartile, and maximum (shown in distribution of ERRs for different types of investments orange). Extreme values are excluded from the top in extreme heat based on a five number summary: graph and included in the bottom one. minimum (shown in orange), first quartile, median Figure 24: Findings of BCA for extreme heat (ERRs) Source: World Bank analysis; based on external data and information Case studies Extreme Heat 124 The UHI effect is a result of a high coverage of consistent with findings in the literature. This is impermeable surfaces, a lack of vegetation, and dense despite the fact that adapted methodologies and concentration of structures that absorb and re-emit conservative assumptions were used to assess this the sun’s heat slower than natural landscapes such as type of disaster (such as using VOLY instead of VSL. forests (Oke, 1982). The UHI effect can have This type of research could be improved by having detrimental consequences for urban populations such more detailed hospital data to empirically assess as increased heat-related mortality (Dang, et al., 2018) the temperature-morbidity relationship and surveys Several EU initiatives such as LifeMedGreenRoof on behavioural changes due to the HEWS to (EU+Life) and the Urban GreenUP Project understand third dividend benefits better. As (Horizon 2020) have promoted the R&D of solutions outlined above, a general intellectual discussion of to the UHI effect. Mitigating the impacts of UHI the high BCRs found when assessing EWS could includes solutions such as the greening of roofs (green improve the understanding of whether impacts of solutions), to increase vegetation and modifying other complementary investments are captured to buildings to have higher reflectivity of sealed surfaces ensure how these synergies can be enhanced. (white solutions) or enhance the coverage of water for Moreover, it has to be noted that the scale of analysis cooling effects (blue solutions). It is important to is different from other case studies presented in this consider costs and benefits, as citywide implementation report as national-scale programmes. efforts can incur significant sums. Other solutions however can be implemented that are more integrated 3.3.2. UHI EFFECTS in other interventions and can therefore yield substantial co-benefits, such as the EU co-funded GENERAL INTRODUCTION TO MEASURES TO Life+ Programme (LIFE, 2020). MITIGATE UHI EFFECTS • Case study 15 (new analysis under this project, ex Cities are increasingly affected by increasing ante (Schwaiger, et al., 2015)): The analysis of temperatures due to climate change as well as the UHI hypothetical citywide interventions in Vienna to effect in which urban temperatures are higher than dampen UHI effects such as green roofs and surrounding areas (Oke, 1973). The UHI effect can reflective surfaces yielded BCRs higher than 1 for have detrimental consequences for urban populations green solutions (depending on intervention choice: such as increased heat-related mortality (Dang, et al., BCR 1.78–1.79, NPV €1.6–3.2 billion, and ERR 2018). Two examples of mitigating the impacts of UHI 78–79 percent) but no net benefits for combined are the greening of roofs (green solutions) to increase green-white interventions with smaller coverage of vegetation and modifying buildings to have higher green roofs (BCR 0.82, NPV −€2 billion, ERR −18.49 reflectivity of sealed surfaces (white solutions) (World percent) or small BCR for green roofs with white Bank, 2020a). solutions (BCR 1.03, NPV €300 million, ERR 2.90 percent). This can be explained by the relatively Several EU initiatives have promoted the R&D of higher cost of white solution and environmental co- solutions to the UHI effect. The EU Life+ funded project benefits of green solutions, although it has to be LifeMedGreenRoof investigated the properties and considered that this is specific to the case of Vienna feasibility of green roofs for Malta and Italy and (costs may be more affordable in lower-income supported the development of guidelines for improved cities, for example). The analysis could be improved uptake of green roofs in reduce energy consumption by considering a spatial disaggregation of the age due to the UHI effect. The URBAN GreenUP project, composition and considering targeted placement funded through the EU Horizon 2020 program, is an of measures rather than overall cover, likely to ongoing project aiming to increase the understanding reduce in higher BCRs. and awareness of the benefits of NBS for urban areas with a focus on the mitigation of UHI. Moreover, the • Case study 16 (new analysis under this project, ex EEA has highlighted the development of numerous post (Rey, et al., 2007)): The analysis of a national research projects that showcase the UHI mitigating program implementing a heatwave EWS (HEWS) in potential of green and white solutions (EEA, 2020b). France after 2003 has yielded high net benefits Numerous initiatives have also supported the climate (BCR 130.67, NPV €1.87 billion, and ERR 12,966.7 proofing of social housing such as in the United percent) and a thorough sensitivity analysis has Kingdom (see Box 8 below). shown that the lowest BCR would be 48, which is Case studies Extreme Heat 125 Box 8: Climate-proofing social housing Climate change is expected to cause more extreme weather founded the Climate Proofing Social Housing Landscapes events across Europe, such as winter flooding and summer project (LIFE, 2020), which had a total budget of heatwaves, and the impacts of these events will be €1,615,636, to demonstrate water-sensitive urban design particularly exacerbated in urban areas, as high soil sealings measures and other climate adaptive actions can transform and drainage systems are already at or near capacity. This urban housing estates into a vital entity for acclimatizing means that metropolitans are susceptible to increased cities to climate change. This project implemented a threat of surface water flooding. Not to mention, the mass of package of climate change adaptation measures in three construction material and reduction in vegetated surfaces social housing estates in the West London borough of in urban areas signify a higher risk of overheating in the Hammersmith & Fulham. This mix of SuDS, rain gardens, summertime. and drought resilient planting and micro green roofs supported by rainwater harvesting tackled the whole It is important to specifically target climate adaptation housing management cycle while providing effective and interventions towards social housing because these affordable low-technology solutions for social housing residents are typically more vulnerable to the effects of estates to meet heightened environmental and economic climate change and are the least likely to afford necessary targets. For example, the University of East London measures that could help them mitigate this risk. Existing monitored the effectiveness of these solutions using housing structures are not designed to withstand future technical software and found that green roofs absorbed 89 climate scenarios; therefore, it is important to maximize the percent of rainfall and diverted 100 percent of rainfall from limited outdoor space and adopt climate adaptation storm drain systems. As a result, these climate change solutions that minimize the local effects of urban adaptation measures implemented during this project development. Green and white solutions can be low-cost demonstrated that these strategies have the ability to and low-technology solutions that enable cities to achieve reduce water run-off and local flooding, improve water their environmental and economic goals. quality, and help mitigate the UHI effect to create wildlife habitats and improve biodiversity, despite limited resources. Between 2013 and 2016, the EU Life+ Programme co- Although significant research has been put into the Belgium, and just over 3.3 for green facades in Italy understanding of the UHI mitigating effects of green (EEA, 2020b) . However, less is known about the costs and white solutions, it is also important to consider and benefits of citywide adaption to the UHI effect, costs and benefits, as citywide implementation efforts with only one study on small and medium-size cities in can incur significant sums. To address these concerns, Austria finding BCRs to range between 1.3 and 2.7 for the EU Horizon 2020-funded Climate Resilient Cities combined white and green solutions (Johnson et al. and Infrastructures (RESIN) project created tools to 2020). Although some studies estimate the health support the development and implementation of benefits of UHI mitigation strategies (Chen et al. 2014), various strategies in addressing multiple urban risks. and some even quantify the benefits monetarily (Mills This effort led to the creation of an adaptation option & Kalkstein, 2012), complete BCAs of such strategies library, which identifies several BCA cases and are lacking. Therefore, the current case study analyses scientific papers that address heatwaves. The BCRs the costs and benefits of green and white solutions to for green roofs may be as high as 2.4, for example, in mitigating UHI effects. GREEN AND WHITE SOLUTIONS TO THE UHI EFFECT– VIENNA, AUSTRIA This case study is a new ex ante / hypothetical solutions) helps decrease the UHI impacts, such as analysis under this project that involved modelling increased mortality, morbidity, and labour productivity of hazards. loss (EEA, 2020b) . By converting typically dark and heat-absorbing surfaces (that is, roofs, streets, and Æ Introduction and background facades) to highly reflective surfaces, more of the solar radiation is transmitted back into the atmosphere due Creating and/or expanding urban green infrastructure to higher albedo factors. Implementing green (green solutions), such as green roofs, as well as infrastructure in planning against UHIs not only implementing highly reflective surfaces (white addresses the first dividend but also provides for Case studies Extreme Heat 126 numerous other economic and environmental benefits 165 of 95 percent confidence intervals). The that are addressed through the second and third temperature-mortality relationship is then combined dividends of the triple dividend of resilience approach. with results from an existing urban climate model for the case study site of Vienna, Austria. Æ Description The results of the urban climate model indicate the In 2018, the Vienna Environmental Protection spatially explicit distribution of the current average Department released the ‘Urban Heat Island number of hot days in the city. Furthermore, several Strategy - City of Vienna’ to implement a strategy for scenarios of the implementation of green solutions reducing the UHI effect to minimize health and and white solutions demonstrate the reduction of the other impacts. Protecting and increasing the number of hot days. Two scenarios indicate the implementation of green infrastructure is one of the changes in the urban climate for a 50 percent green core aims of the strategy as well as increasing the roof implementation of all technically feasible roofs albedo of surfaces such as roofs, facades, and in Vienna as well as a 100 percent implementation. streets. The framework lays the foundation for Two further scenarios include the 50 percent and consideration of UHI mitigating measures that can 100 percent implementation of green roofs while be incorporated in the planning of urban areas. converting the remaining potential roof areas to Currently, of the total amount of roof space (5,184 highly reflective roofing materials and converting ha), Vienna has green roofs on only 2 percent (104 potential wall and street space to highly reflective ha), although the potential for implementing green materials. The analysis further incorporates the roofs is estimated at 45 percent of the total roof space exposure of the population to the heat hazard with a (Schwaiger, et al., 2015). Moreover, most roofs, map of the population distribution across the city and streets, and facades do not currently exhibit high solar considers the application of these strategies. reflectance. The strategy also maintains the importance of financial incentives to improve the To estimate the societal value of reducing mortality uptake of green roofs. For example, the city of Vienna risk, we employ the VOLY approach, as extreme heat supports investments in green roofs with €8–25 per tends to disproportionately affect older individuals, m2 of the roof. Given the financial and policy-relevant and valuing complete statistical lives would likely aspects of the Vienna strategy, we have chosen this overestimate the economic impact of this hazard as the case study of interest for an appraisal analysis (Chiabai, et al., 2018). We estimate the VOLY for addressing UHI risks. according to a €7,286,000 value of a statistical life (VSL) for Austria (Viscusi & Masterman, 2017) and an Æ Methodology and results of the analysis by average life expectancy of 80.7 years (Statistik Austria, dividends and overall 2020). Detailed descriptions of the methodology, analysis, Due to a lack of available hospitalization data at the and calculations can be found in Annex 4. proper scale, we estimate the heat-attributable morbidity by linear approximating from the number of Dividend 1: Health-related impacts of extreme heat heat-related mortality counts saved by the implementation scenarios. Donaldson et al. (2001) To understand the effects on the first dividend tier, this demonstrated a significant relationship between the case study models the impact of temperature on number of heat-related deaths and heat-related human mortality. Mortality counts are regressed with hospital admissions. In line with Hunt et al. (2017) , we daily maximum temperature to understand the relative assume 102 patient days avoided per reduced heat- risk of temperature on mortality and estimate the related death. We use the average daily cost of hospital number of heat-attributable deaths on hot days (days stays (2008–2017) for the city of Vienna to estimate with a maximum temperature greater than 30°C) - the the value of reduced hospital admissions. baseline scenario approach for this case study. With Furthermore, the avoided time spent in the hospital is this approach, we calculated an annual number of also valued by taking the VOLY as an estimate of the heat attributable deaths above a daily maximum quality of a life year and reducing this down to 75 temperature of 30°C to be 106 deaths (ranging 39– percent (Karlsson & Ziebarth, 2018). Case studies Extreme Heat 127 Dividend 2: Property values and building longevity surfaces and value this change according to a stormwater charge for sealed surfaces. Green infrastructure, such as green roofs, offers numerous additional benefits besides the reduction of Heating savings from the second dividend also incur the UHI effect that can be economically valued. saved pollution and carbon dioxide as negative The benefits either fall under the second or third externalities that society bears as a third dividend dividend. Green roofs have been cited to increase benefit. Therefore, we value the reduction of this property values in a range of 2–5 percent (Bianchini & externality to society at the EU-wide rate of €12/MWh Hewage, 2012; Perini & Rosasco, 2016). Assuming a for reduced heating with combined heat and power 3 percent increase in the average property values of with natural gas (Alberici, et al., 2014). several sizes in Vienna (PWIB Wohnungs-Infobörse GmbH, 2020), we take a conservative approach in Furthermore, green roofs provide habitats in urban this valuation. areas for organisms, which was otherwise nonexistent (Currie & Bass, 2010). Since the quality of the green For the second dividend, we also assess the roof is only a fraction of a completely natural space, we improvement of the building longevity with the value the improvement to urban habitats with 15 installation of green roofs. Green roofs extend the percent of the cost (Bianchini & Hewage, 2012) for working life of a roof to an average of 50 years (Clark, et restoring land (MacMullan, et al., 2009). Lastly, green al., 2008). Taking the average cost of major repairs and roofs support urban areas in pollution mitigation and maintenance that would typically accrue in the 25th carbon dioxide sequestration. We take removal rates year of a conventional roof, we value the building of pollutants, including nitrous oxide, ozone, sulphur longevity improvements of installing green roofs as a dioxide, and particulate matter (Yang, et al., 2008), saved replacement cost. and carbon sequestration rates of green roofs (Getter, et al., 2009) to estimate the reduction of these Dividend 3: Economic and environmental co-benefits negative externalities to society. The valuations incorporate the average of the high and low shadow Several economic and environmental benefits are prices of carbon (World Bank, 2017b), which are assessed for green infrastructure under the third increasing into the future, as well as the shadow prices dividend. Energy efficiency improvements are valued of the air pollutants according to EU-wide damage given the additional insulating layer of green roofs costs (Holland, et al., 2014). (Berardi, et al., 2014). We compare the differences in the thermal properties of green and conventional roofs Æ Costs of green and white solutions according to Clark, et al. (2008) to estimate heating and cooling savings. For the cost estimates of green roof, we used the median estimates of retrofitting roofs from a large Extreme heat can have significant impacts on both sample of actual costs from the literature (Strehl & indoor and outdoor labour productivity in Europe, Offermann, 2017). We also take the estimates of leading to large economic losses (Naumann, et al., Bretz, et al. (1998) for high albedo measures on roofs, 2020). Given time and data constraints, we employ the streets, and facades. These are meant to be guiding approach of Hübler, et al. (2018) to estimate the values of the installation and operation and reductions in labour productivity loss with scenarios of maintenance costs. implementation that would otherwise occur on hot days, assuming an average reduced worker productivity Æ Results of the analysis by Dividends loss of 7 percent (Vöhringer, et al., 2017). and overall Green infrastructure, such as green roofs, offers Overall, the analysis finds positive net benefits for numerous environmental benefits alongside the three types of interventions but not for the abovementioned economic benefits. Green roofs intervention with smaller green roof coverage and improve stormwater management in urban areas by white solutions (see Table 52). This could be reducing the amount of stormwater run-off being explained by the relatively high cost of white conveyed in municipal sewer systems. We assume a solutions and the higher co-benefits of green roofs in 50 percent decrease in the run-off from greened roof terms of environmental benefits, for example. Case studies Extreme Heat 128 Table 52: Costs and benefits of green and white solutions to reduce UHI effect (in hundred millions €) GREEN ROOFS GREEN ROOFS GREEN ROOFS GREEN ROOFS (50%) (100%) + WHITE (50%) (100%) + WHITE SOLUTIONS SOLUTIONS FIRST DIVIDEND (€) Reduced heat-related 4.25 8.65 39.76 40.84 mortality Reduced heat-related 0.1 0.2 0.91 0.93 hospitalizations Reduced time spent in the 0.04 0.09 0.4 0.41 hospital Total first dividend 4.39 8.93 41.08 42.18 SECOND DIVIDEND Increase in property values 16.12 32.25 16.12 32.25 Total second dividend 16.12 32.25 16.12 32.25 THIRD DIVIDEND (€) Economic co-benefits Improved energy efficiency (savings on heating and 4.92 9.84 4.92 9.84 cooling) Reduced labour 2.39 3.88 10.46 10.76 productivity loss Building longevity increase 4.3 8.59 4.3 8.59 Environmental co-benefits Stormwater runoff 2.52 5.04 2.52 5.04 reduction Reduced externalities of 0.51 1.03 0.51 1.03 energy production Habitat creation 1.3 2.6 1.3 2.6 Air quality improvements 0.4 0.79 0.4 0.79 Carbon sequestration 0.18 0.36 0.18 0.36 Total third dividend 16.52 32.15 24.59 39.02 TOTAL DIVIDEND 37.04 73.33 81.79 113.45 Total cost 20.64 41.29 100.34 110.25 BCR 1.79 1.78 0.82 1.03 NPV (€) 16.4 32.04 -18.55 3.19 ERR (%) 79.43 77.61 -18.49 2.90 Source: World Bank analysis; based on external data and information Case studies Extreme Heat 129 Æ Challenges faced and lessons learned of heat-related mortality show rising rates in many cities across the globe (Gasparrini, et al., 2017). Future studies should disaggregate benefits of reduced productivity loss according to the sector of the The PESETA IV project of the JRC of the European economy. A spatially explicit representation of the age Commission alluded to high benefits in terms of composition of the population across cities could reduced mortality, morbidity, and productivity loss if further improve the accuracy of the benefit estimations HEWS were implemented for EU regions (Paci, 2014). of reduced mortality. Furthermore, a study under the EC-funded EUPORIAS project found that improving current warning systems Including white solutions into the scenarios greatly with better forecasts can further improve the heat- increases the costs and results in lower BCRs than the related mortality (Lowe, et al., 2016). Current EU- green solutions on their own. However, it should be funded work is under way to implement a Europe-wide maintained that the scenarios assumed complete heat-warning system that addresses workers and application of technically feasible areas across the productivity loss and is researched under the EU city. However, it may not be necessary to obtain such a Horizon 2020 HEAT-SHIELD project (Casanueva, et level of application across the city, and a strategic al., 2019). Moreover, these systems can complement placement of measures could improve the balance other efforts in mainstreaming the use of NBS. For between the costs and benefits. example, to achieve the goals set in France’s second national climate adaptation plan and future plans, the 3.3.3. HEAT EARLY WARNING SYSTEMS €16.6 million Life IP Artisan project (Coreau, 2020) (with an EU contribution of €10 million) attempts to GENERAL INTRODUCTION TO BENEFITS OF increase the country’s resilience to climate change. EARLY WARNING FOR HEATWAVES Its main objective is to generalize the implementation of NBS and good practices to the extent possible by Extreme heat can have detrimental impacts on human 2030, which creates a good framework for the health and well-being. The 2003 heatwave that swept emergence of local projects that emphasize climate across Europe was estimated to have claimed the adaptation and the ecosystem. lives of around 30,000 people (UNEP, 2004). In just one hospital in Paris, 2,400 additional emergency Several BCAs have demonstrated that the benefits of care visits and 1,900 excess hospital emissions were such systems strongly outweigh the costs. Ebi et al. recorded during the heatwave (Åström, et al., 2013), (2004) estimated net benefits of €417 million and the number of excess deaths that occurred due to (US$468 million) for 1995–1998 for the HEWS in the 2003 heatwave in France is estimated at 14,800 Philadelphia. Hunt et al. (2017) also showed positive (Bouchama, 2004). Given that numerous heatwaves results with BCRs of median scenarios of climate in the past have led to considerable excess mortality change greater than 1 and ranging from 23 for London in France (Rey, et al., 2007), there is significant to 1,375 for Madrid. In a study by Chiabai, Spadaro, concern for the human health-related impacts of and Neumann (2018), BCRs ranged from 42 to 1,350 extreme heat. These concerns are further for the HEWS of Madrid, depending on whether the compounded when considering the future impact of VSL or VOLY was used and whether displaced versus climate change on temperatures and how projections premature deaths were considered. Case studies Extreme Heat 130 HEWS FOR REDUCING HEALTH IMPACTS OF HEAT IN PARIS, FRANCE This case study is a new ex-post analysis under this HEWS has been studied for its effectiveness, we this project that involved modelling of hazards. have chosen this HEWS as the case study because no BCA has been performed for it thus far. Æ Introduction and background Æ Methodology and results of the analysis by HEWS can provide important health benefits in terms dividends and overall of avoided heat-related mortality and morbidity. It supports emergency managers and countries to To assess the reduction in heat-related mortality and implement preparedness measures like cooling morbidity through the implementation of the HEWS, stations and targeted messaging as well as informing we rely on empirical modelling carried out in academic energy providers ahead of time of increased cooling health literature. This method has been proposed due load demand. to time and data constraints, especially given the extensive data needs to quantify the heat-related Æ Description mortality before and after the initiation of the HEWS. We take a city-level approach for calculating the costs Due to the high societal losses in the 2003 heatwave, and benefits, as the heat-related mortality relationships France put forward a plan to help prevent further high are usually quantified in such a manner. excess mortality during heatwaves. The core of the plan was the implementation of HEWS to alert The approach of this analysis is to estimate baseline vulnerable groups of the ensuing high temperatures to costs and benefits of the HEWS and to perpetuate have better preparedness. Studies have shown positive these into the following 50 years. Climate change and effects of HEWS in reducing heat-related mortality demographic change are not considered in this (Bassil & Cole, 2010). Given indications that the HEWS analysis. However, given the strongly positive results of of France has improved the heat-mortality responses the analysis, it can be assumed that the BCRs that are to extreme heat (Fouillet, et al., 2008), this case study greater than 1 will not worsen over time due to these analyses the costs and benefits of the system. factors. With the progression of climate change on the one hand, the costs of the system will increase since The French HEWS was implemented following the the system is triggered more often (ECONADAPT, disastrous 2003 heatwave that resulted in tens of 2015). On the other hand, the benefits will also thousands of deaths. The aim was to provide a system greatly increase as more vulnerable portions of the of alerting authorities of ensuing extreme heat events populations are increasingly addressed to prevent to set up preventive measures that address health consequences, which was demonstrated in the vulnerable groups. The system is based on threshold analysis by Hunt et al. (2017). Furthermore, given temperatures that lead to an excess of mortality demographic changes trending towards increased when reached and is active between June 1 and portions of the vulnerable population in older age August 31. If the three-day averaged minimum and groups, these groups would also be addressed by the maximum forecasted temperatures are likely to reach HEWS, which would further increase the benefits. predefined thresholds, warnings are issued, and Therefore, the changes arising in socio-climatic information is disseminated to the media and general scenarios can generally be negligible since both the population. If high levels of the system are activated, benefits and costs are proportional to the number of specific advice is provided to vulnerable groups (for extreme heat events (Chiabai, et al., 2018). example, schools, hospitals, and businesses). Although Case studies Extreme Heat 131 Dividend 1: Valuing reduced health-related impacts deaths saved, we differentiate between the 0–74 age of extreme heat group and the 75+ years age group, given that 80 percent of the heatwave deaths in the 2003 heatwave Heat-related mortality is modelled by means of a occurred in this age group (EEA, 2004). We value the distributed lag nonlinear model that includes the saved years of life in the 75+ age group by subtracting lagged effects of heat on mortality. With this modelling from the life expectancy and multiplying in by the procedure, the main effects of heat on mortality are VOLY, whereas the average age is used for the 0–74 captured, and the additional effect of a heatwave may age group. only be insignificant (Gasparrini & Armstrong, 2011). Fouillet et al. (2008) already indicated the significant Empirical evidence suggests that the number of positive effect of the HEWS on the temperature- hospital admissions rises with extreme heat. Using mortality relationship of France with a modelling hospital climate data from 1991 to 1995, Michelozzi et procedure using projections of the number of expected al. (2009) demonstrated that daily hospital admissions deaths that would have occurred in the 2006 heatwave rose by 1.3 percent on days with a maximum apparent given the number of deaths in the 2003 heatwave. temperature above 27.8°C. To value the reduced heat- Their analysis predicted a much higher expected related morbidity, we take a linear approximation of number of deaths for the 2006 heatwave than what the number of hospitalizations given the number of did occur with a resulting 4,400 deaths saved. reduced heat-related deaths. We assume 102 patient However, we rely on the estimations performed by Dé days per heat-related death as found by Donaldson et Donato et al. (2015) since their analysis empirically al. (2001) and a central cost value of €750 per patient estimates the heat-related mortality for several years days in line with the analysis by Hunt et al. (2017). before and after the implementation of the HEWS. Dé Given that prevented hospitalizations results in less Donato et al. (2015) regressed daily all-cause mortality time spent in the hospital, we further adopt the with daily mean temperature while controlling for approach in Karlsson and Ziebarth (2018) to value the potential confounders, such as air pollution, relative prevented time spent in the hospital. A 25 percent humidity, barometric pressure, and wind speed, to fraction of the quality of a life year for France (Téhard, estimate the heat-related risk and attributable deaths. et al., 2020) is estimated while scaling down to the Their analysis concluded a significantly reduced number of saved patient days. relative risk of extreme heat following the implementation of the HEWS by comparing the relative The former benefits all address the first dividend of risks between 1997–2002 and 2004–2009. the Triple Dividend Framework of resilience. This analysis demonstrates the significant societal value The number of heat-attributable deaths was reduced provided by valuing the impacts of this dividend, by 787 over the six-year period. For the current although some qualitative impacts in the other analysis, we take this figure and divide by the six years dividends are also deemed noteworthy. HEWS are to arrive at an assumed annual reduced heat-related increasingly important to improve the awareness of mortality. Given the possibility that many other factors the population of the health-related impacts of extreme might have reduced the relative risk to heat, we assume heat, and the implementation of such systems can be an effectiveness of the HEWS of 38 percent considering of great value to the policy and planning to ensure the the assumptions of Hunt et al. (2017). Furthermore, safety of workers (Kjellstrom, et al., 2019). we rely on some assumptions of the analysis by Chiabai, Spadaro, and Neumann (2018) in that a Dividend 3: improved awareness and preparation for portion of the deaths may have been displaced deaths the workforce as opposed to premature deaths. Premature deaths would entail a loss of life at some period in the otherwise The effectiveness of the HEWS relies on the be­ healthy individual, whereas a displaced death relies on havioural changes adapted by the population. Given the harvesting hypothesis that the death occurred for the apparent effectiveness of the system in moderating an individual who would have otherwise passed away the temperature-mortality relationship at the extreme in a short time afterwards (Hajat, et al., 2005). For the heat end, it appears that behavioural adaptations are baseline scenario, we assume that 35 percent of the happening at some scale within the population. heat-related deaths are displaced deaths, which are Moreover, this study has only quantitatively considered valued at 16 days of the VOLY. For the remaining impacts to the population in terms of mortality and Case studies Extreme Heat 132 morbidity, which excludes the benefits accruing to the can help prevent extended health consequences in population arising from general pressures of extreme the workforce by providing timely warnings of extreme temperatures and the decrease of personal comfort. A heat events. Therefore, we have addressed these study in Arizona concerning the awareness and under the social co-benefits of the third dividend. perceived risk of heat given the introduction of HEWS showed that although not all surveyed individuals 65 The costs of EWS are generally low compared to other years and older adjusted their behaviour during alert forms of adaptation. The estimated cost of the initial events, almost 50 percent of all respondents actually implementation considering preparations was altered their behaviour having been aware of the alerts €286,933, and the estimated operational cost from (Kalkstein & Sheridan, 2007). Such behavioural June 1 to the end of August was €454,006 (ONERC, changes as a result of HEWS likely provided some 2009). These costs are similar to the ranges seen for benefits in improved thermal comfort for individuals, other systems in London, Madrid, and Prague (Hunt, et and these benefits were not captured quantitively in al., 2017). this analysis. Furthermore, heat-related worker productivity loss is an increasing concern given climate Æ Results of the analysis by dividends change-related temperature increases. However, the and overall introduction of HEWS sets the stage for future warning systems that also specifically address the health of the The BCR is high for this type of intervention, which is workforce, such as the current work in the HEAT- likely due to the high share of benefits from lives saved, SHIELD project on a European-wide occupational even though this study has used the VOLY approach warning system (Morabito, et al., 2019). Given these and assumed 35 percent of the deaths were displaced concerns, it can be assumed that HEWS as in France deaths rather than premature deaths (see Table 53). Table 53: BCR for HEWS by dividends HEWS FIRST DIVIDEND 1 (€) Reduced heat-related mortality €1.8 B Reduced heat-related hospitalizations €63.8 M Reduced time spent in the hospital €25.7 M Total first dividend €1.9 B THIRD DIVIDEND 3 (€) Economic co-benefits Improved productivity of outdoor labourers through knowledge of heat-related (qualitative) health effects Social co-benefits Improved awareness of heat-related health effects and potential for individual (qualitative) adaptation to increase heat stress TOTAL DIVIDEND €1.9 B Total cost €14.45 M BCR 130.67 NPV (€) €1.9 B ERR (%) 12,967 Source: World Bank analysis; based on external data and information Case studies Extreme Heat 133 To test these results given the assumptions made, we values as the minimum and maximum, respectively. account for the sensitivity of the BCR parameters of With 10,000 iterations in the Monte Carlo analysis, we the cost-benefit model in a Monte Carlo simulation. arrived at a mean BCR of 131, a median BCR of 119, The ranges of the parameters are given in Table 54, and BCRs at the 5th and 95th percentiles of 48 and and all parameters follow triangular distributions with 246, respectively. Furthermore, in all iterations, the the baseline values as the mode and low and high BCR remained greater than 1. Table 54: Ranges of parameters used in Monte Carlo simulation following triangular distributions LOW BASE HIGH Installation cost (€) 277,095 346,369 415,642 Operation cost(€) 438,439 548,049 657,659 Discount rate (%) 1.5 3 5 Effectiveness (%) 9 38 68 Deaths in the 75+ age group 60 80 100 (%) Displaced deaths ratio (%) 0 35 75 Attributable deaths (number) 630 787 944 Source: World Bank analysis; based on external data and information Æ Challenges faced and lessons learned VOLY, which has been done in this study. Recent studies have found BCRs for Madrid to range from 42 There is generally a lack of publicly available hospital to 1,350 depending on whether the VSL or VOLY is data that could be used to empirically assess the used and whether displaced and premature mortality temperature-morbidity relationship. Surveys on the is valued using VSL or VOLY. In the current case study, awareness of and behavioural changes due to the we have adopted the VOLY for both premature and HEWS in France could provide insights into the displaced mortality (which could provide a understanding of the third dividend benefits. conservative estimate) while furthermore assuming that only 38 percent of effectiveness is achieved with BCRs are generally high for HEWS. For these reasons, the HEWS (that is, only 38 percent of the saved lives it is preferred to value reduced mortality according to could be attributed to the HEWS). Case studies Extreme Heat 134 3.4. Droughts 3.4.1. SUMMARY OF FINDINGS water use model LISFLOOD is used, with high- FOR DROUGHTS resolution regional climate projections for RCP4.5 and RCP8.5 being applied. The result of the study shows In terms of DDR investments in droughts, the EU has that in southern Europe, extreme low river flows will taken massive strides to transform their approach to become more severe and persistent, especially in the water scarcity and drought from being crisis oriented context of global warming. At the same time, most of to preventative directed within the last two decades western Europe will become more vulnerable to (Stein, et al., 2016). These actions include developing frequent and intense droughts (Cammalleri, et al., irrigation and water provision systems, EWS, such as 2020). the European Drought Observatory (EDO), and multisector partnerships (MSPs) with various Minimum river streamflow is an important indicator stakeholders of a specific region. when conducting economic analysis and research on droughts because it is a reflection of the spatially In 2000, the Water Framework Directive (WFD) integrated shortage in water supply over river basins, established the EU-wide framework for water which is a great concern to water managers, according management. The occurrence of major drought events to the study conducted by PESETA IV (Cammalleri, et between 2000 and 2006, mainly the widespread al., 2020). When conducting drought assessments drought in 2003, catalysed policy conversation on how with streamflow simulations, the hydrological and the Environment Council should address the water use model LISFLOOD is used, with high- environmental, social, and economic impacts of water resolution regional climate projections for RCP4.5 and scarcity and drought at a political and a technical level. RCP8.5 being applied. The result of the study shows After several analyses, they found that drought affects that in southern Europe, extreme low river flows will all EU countries. Under former European Parliament become more severe and persistent, especially in the Environment Commissioner Potočnik, the European context of global warming. At the same time, most of Commission’s JRC helped establish the EDO as part of western Europe will become more vulnerable to ongoing efforts to integrate drought into policy. Since frequent and intense droughts (Cammalleri, et al., 2011, the EDO has been the leading communicator on 2020). drought-relevant information and maps. Though undertaking economic analysis of investments Minimum river streamflow is an important indicator in drought prevention is difficult, some reports have when conducting economic analysis and research on shown the logical links that can support the analysis droughts because it is a reflection of the spatially and research on drought impacts (see Figure 25 integrated shortage in water supply over river basins, below as well as page 29 of the report from the Global which is a great concern to water managers, according Water Partnership and Central and Eastern Europe to the study conducted by PESETA IV (Cammalleri, et (2015)). The literature has mainly focused on al., 2020). When conducting drought assessments estimating the costs of droughts (Pulwarty & Sivakumar, with streamflow simulations, the hydrological and 2014) and the benefits of approaches to drought risk Case studies Droughts 135 management. Research on economic impact would fore their consequences to ecosystems, such there­ benefit from improved drought risk assessments and as limited public water supplies, agricultural losses, comparison of scenarios with and without interventions and damage to buildings and infrastructure due to (Pulwarty & Sivakumar, 2014) . The damage caused by soil subsidence, are not monetized. Figure 25 droughts in the EU at a 95 percent confidence interval demonstrates the framework for assessing the impact is estimated to be between €7.4 billion and €14.2 of droughts and the approaches and benefits of billion per year, assuming an annual loss of €9 billion drought risk management and Figure 26 shows the for the baseline conditions (1981–2010) (Cammalleri, share of drought losses by economic sector under et al., 2020). Drought conditions remain unnoticed the baseline (1981 -2010) and climate projection for until water shortages become severe and their adverse 2100. impacts on the environment are severe, and Figure 25: Conceptual framework of the impacts of drought events and approaches to drought risk prevention Case studies Droughts 136 Source: Gerber & Mirzabaev (2017) Figure 26: Share of drought losses by economic sector (agriculture, energy, water supply, subsidence, and transport) for EU + UK and the four IPCC AR5 European subregions in the baseline (1981–2010) and in 2100 Source: Cammalleri, et al. (2020) In this section, we have presented benefit-cost shown qualitatively. Drought-related risks in most case assessments for irrigation and water provision systems studies are mitigated through the improvement of water against droughts as well as early warning and capacity systems. Some examples also show the effectiveness of building for drought preparedness. Results from one BCA monitoring and enhancing preparedness and public for an investment in drought management are presented awareness in terms of drought risk reduction. A table for an external analysis that was undertaken with ex-post summarizing main data and information sources can be assessments, while the benefit of other interventions are found below (see Table 55). Case studies Droughts 137 Table 55: Overview of data and information sources for droughts analysis INVESTMENT CASE STUDY DATA SOURCE NAME AND REFERENCE Irrigation and Drought planned External econometric assessment from the study Assessing the water provision management in the Effectiveness of Multi-Sector Partnerships to Manage Droughts: systems Jucar River Basin The Case of the Jucar River Basin Source: World Bank based on external data and information BCRs have generally not been calculated for this type • Case study 17 (external research analysis, ex post of disaster. Droughts are among the most damaging (Carmona, et al., 2017; European Commission, and least understood of all natural hazards and their 2011)): The analysis of a comprehensive program onset is slow, which makes the economic analysis of for drought prevention in the Jucar River Basin in preventive investments inherently difficult (Pulwarty & Eastern Spain, including institutional frameworks, Sivakumar, 2014). Also, models need to be adapted to environmental protection measures and water the type of investment analysed. Generally, estimation saving plans yielded high net benefits. The economic of (predicted) ‘average’ soil moisture is essential to be analysis focused on the impact of emergency able to conduct economic analysis and research on drought wells, but the study also provides an droughts. overview of economic assessments methodologies for droughts, including how to estimate benefits or BCAs generally show net benefits of interventions, effectiveness from softer interventions such as although generally in a qualitative manner. Given the governance arrangements (polycentric risk lack of understanding of this hazard, there is little management governance) at least qualitatively. comparison possible with the literature, but the case study presented can provide interesting insights into 3.4.2. IRRIGATION AND WATER PROVISION how to consider governance of DRR investments in SYSTEMS AGAINST DROUGHTS economic efficiency analysis. Æ Introduction and background Irrigation and water provision systems constitute preventive investments against droughts. These Investments in structural improvements and include investments in structural improvements and interventions of water supplies as well as irrigation interventions of water supplies as well as irrigation systems provide civilians with access to improved systems providing civilians with access to improved water resources and enhanced water and food water resources and enhanced water and food security. Preventive investments, such as drought security. Preventive investments, such as drought wells, dams, and efficient irrigation have a variety of wells, dams, and efficient irrigation, have a variety of environmental, economic, and social benefits. Not benefits as they reduce the need for high-cost post- only are these areas better prepared for drought drought rehabilitation and relief efforts, beyond occurrences, but they are also able to supply residents benefits of lives saved, health, and productivity, such with water during these times without hesitation or as the large-scale water project ‘Ligação Pisão-Roxo’ worries of scarcity. This preparedness reduces the (European Commission, 2011) in South Portugal that need for high-cost post-drought rehabilitation and systematically improved the water supply system or relief efforts. Moreover, the construction of these EWS such as the DriDanube project (Interreg Danube, structural investments creates jobs for residents, 2020). which helps stimulate the economy further. Box 9 below provides an illustration of the aforementioned benefits obtained from the structural investments. Case studies Droughts 138 Box 9: Investing in improving water security infrastructure and supply system The following example showcases how structural of a larger water network with a canal extension of 23.13 improvements to the water security systems directly benefit km. The project was implemented with a total cost of €65.2 civilians and lead to positive economic impacts. In Southern million, and it is expected to provide greater supplies of Portugal, a large-scale water project called “Ligação Pisão- water for the region and its residents. An analysis of the Roxo” (European Commission, 2011) was launched with benefits and impacts of the project was conducted, which the objective to improve the water supply system of the shows that the improved water system benefits an estimation Guadiana River. As a part of the Alqueva Dam Project, of 44,486 people and also generates economic benefits investments were made to build a new dam, which is a part through the creation of 40 new jobs. ECONOMIC BENEFITS OF DROUGHT PLANNED MANAGEMENT IN THE JUCAR RIVER BASIN This case study is an external analysis that was through the use of stochastic forecasting models undertaken with ex post assessments. to estimate future volume stored in reservoirs and use of forecasted scenarios to estimate the Æ Description evolution of the systems Jucar River Basin, located in Eastern Spain, has 3. Water saving plans improving the efficiency of suffered many historical droughts with significant water distribution systems and the establishment socio-economic impacts due to the region’s semiarid of irrigation turns adopted by urban and climate, high water exploitation indexes, and high agricultural users spatial and temporal variability of precipitation which causes highly seasonal and inter-annual variability in 4. Alternative water sources and generation of river flows. Future climate change-related impacts can additional including the use of drought wells, create future hydrological problems, such as increased recirculation of irrigation returns back to the head salinity in coastal aquifers and higher water turbidity, of the system, and reuse of treated wastewater which can have severe social and economic from the urban areas. implications. Throughout history, there have been different governance structures established in the The objective of this case study is to demonstrate the Jucar River Basin to tackle the multi-faceted risks positive economic impacts effective water associated with droughts and other climate change management can have on mitigating droughts and the scenarios. Some of these structures have taken shape broader metropolitan communities the basin serves. as MSPs, and currently, the Jucar River Basin To do so, we will look at the economic impacts of Partnership’s Water Council and the Permanent groundwater pumping from drought wells and how it Drought Commission (PDC) are in action to address maintains crop production and production value. every officially declared drought. The PDC, which was established in December 2005 after the start of the Æ Methodology 2005–2008 Drought Event in the Jucar River Basin, approved measures to address the following goals: Two methodologies were used to evaluate how effective the creation and institutionalization of MSPs 1. Environmental protection ensuring the continuity are in supporting the development of an efficient of streamflow and protecting drought-vulnerable drought management system. However, for this case wetlands study, we will examine the econometric approach in detail to analyse the economic efficiency of emergency 2. Management and control of water resources drought wells, a key drought mitigation measure supporting the decision making in the PDC suggested and implemented by the PDC. Case studies Droughts 139 Æ Results of the analysis by dividends and overall Table 56: Fitted impact model to determine economic efficiency of emergency drought wells Pv=283.84*W+1484.98*G+275,923*lp Source: Carmona, et al. (2017) From Table 56 we see that the dependent variables are 3.4.3. EARLY WARNING AND CAPACITY statistically significant with a p-value less than 0.05. BUILDING FOR DROUGHT Therefore, the fitted model is able to simulate the PREPAREDNESS production value, while considering the historic time series of water deliveries (surface and groundwater) Accurate monitoring and effective early warnings are [W], index of crop prices [G], and production value of important as they allow people to be better prepared irrigated agriculture [lp], with a R^2 value of 99 when a disaster strikes. EWS technology is especially percent. During 2006, 2007, and 2008, the additional important for agriculture and water resource groundwater pumping for drought was estimated at 40 management because it helps decrease risk associated mm3, 40 mm3, and 25 mm3, respectively. As a result, with crop and food loss. According to the Climate according to this model, the additional drought Technology Centre and Network (CTCN) (2020), the pumping reduced drought losses by €59 million, 59 operational arm of the United Nations Framework million, and 37 million during those respective years, Convention on Climate Change (UNFCC) Technology compared to a scenario in which this mitigation Mechanism, effective drought monitoring warning measure was not implemented. There were no systems must include appropriate drought indicators, additional costs to the stakeholders for the drought meteorological data and forecasts, a warning signal, pumping, since the pumping cost was supported by public awareness and education, institutional other Jucar River Basin users receiving surface water cooperation, and data sharing arrangements. Some deliveries, in agreement with the conditions of the environmental and socio-economic benefits of drought Alarcon treatment. monitoring EWS are improved land use practices which decrease soil and land degradation; mitigation Æ Challenges faced and lessons learned of human fatalities caused by health risks, poor water, and food security; a reduction of high costs related to The analysis focused on one drought period and a post-drought rehabilitation and relief efforts; and single risk mitigation measure (emergency wells) to refined network connectivity between and within local analyse the economic benefits of the intervention and communities. comment on the effectiveness of drought/disaster governance measures. The focus of the analysis is on Integrated and comprehensive approaches are polycentric risk management governance, and essential for effective drought monitoring and early methodologies may also be applied to other drought warning given the complexity of the hazard, including management interventions with sufficient data the combination of connected local and international available. capacity and systems (Hayes, et al., 2005; Pulwarty & Sivakumar, 2014). While there have been significant Case studies Droughts 140 efforts made to understand the value of early hydro- economic benefits of climatic and meteorological meteorological warning systems, it remains that the information: direct valuations, indirect valuations, valuations of information may vary by sector since market approaches, and non-market approaches. A there is no standardized approach. As a result, Liu et project in the Danube regions (see Box 10) reveals al. (2019) narrowed down their literature review to how an early warning and monitoring system reduces explore four methods and tools used to examine the the negative impact of droughts. Box 10: Investing in Early Warning and preparedness for Droughts The following example shows the benefit early warning and involved in drought management to be better prepared and monitoring systems yield in terms of disaster risk reduction. more efficient when they are responding to drought With the objective of increasing the capacity to manage emergencies. With a cost of €1.97 million, the project drought-related risks, the DriDanube project (Interreg accomplished its goal with the output “Drought User Danube, 2020) in the Danube region was launched in 2017. Service”, which allows efficient and accurate monitoring The Danube is a river region that experiences droughts and early warnings of droughts. This enables better frequently, which leads to water scarcity and negative cooperation between agencies and emergency responses impacts on the economy and welfare of the people. to droughts, which decreases the losses in lives and Therefore, the DriDanube project helps all stakeholders damages when a drought occurs. Case studies Droughts 141 3.5. Wildfires 3.5.1. SUMMARY OF FINDINGS FOR of Europe near the Mediterranean, moisture levels of WILDFIRES forests are the lowest. As a result, the countries with the highest danger of wildfires are Spain, Portugal, and Across Europe, forests cover approximately 215 Turkey. Greece, parts of central and southern Italy, million ha and other wooded lands cover an additional Mediterranean France, and the coastal region of the 36 million ha, which amount to over one-third of the Balkans are also susceptible to increased danger. continent’s total land area (De Rigo, et al., 2017). More European countries suffered from large forest There are initiatives and studies conducted at the fires in 2018 than ever before, and Sweden European supranational level to understand the experienced the worst fire season in reporting history. impacts of forest fires. For instance, collaboration The unprecedented forest fires in several European between European countries and the European countries in 2017 and 2018 coincided with record Commission developed the European Fire Database, droughts and heatwaves in these years (EEA, 2020). In the largest repository of information on individual fire 2010 alone, wildfires were responsible for the events and forest fires in Europe. Furthermore, the damage of 0.5 million ha forests in Europe. Factors PESETA IV report analysed how fire danger in most of that contribute to forest fire occurrence include the Europe would increase under different global moisture content of the forest surface and climate warming scenarios (1.5°C, 2 °C, and 3°C) and how the variables, such as wind speed. A wetter surface can severity, frequency, and damage of forest fires decrease potential spreading of a fire and the ease of throughout Europe will be affected by climate change ignition, while wind speed can affect the rate a fire (see Figure 27), (Costa, et al., 2020). might spread following ignition. In the southern parts Case studies Wildfires 142 Figure 27: Forest fire danger in the present, and under two climate change scenarios, according to two different climate models (1.5°C, 2 °C, and 3°C) Source: (Costa, et al., 2020) Note: The climate models were selected to demonstrate the effects of the different models. In this section, we have demonstrated benefit-cost mitigation at a forest level as well as a property level assessments for a variety of wildfire prevention with creation of fuel and firebreaks as well as clearing investments. These include structural wildfire for defensible space, respectively. The decision protection to homes and industries (for example, support tools for wildfire risk inform cross-border fire creation of defensible space, firebreaks, and fuel service organizations on coordinated efforts for breaks), decision support tools (for example, cross- enhanced fire suppression. Climate change adaptation border emergent fire information and climate change through improved silviculture as a decision support adaptation information for small forest owners), and tool also informs small forest owners how to best wildfire preparedness (for example, EWS, property- manage their own forestlands against future fires. level defensible space, and development of evacuation Alerting and preparedness case studies with both plans). BCRs for the different types of interventions are government-funded and homeowner-enacted shown by a combination of detailed case study preparedness measures are assessed as priority analyses including both prospective and retrospective actions for stakeholders in wildfire-prone areas. types of assessments. The majority of wildfire Table 57 summarizes main data and information management case studies considered use structural sources. Case studies Wildfires 143 Table 57: Overview of data and information sources for wildfires analysis INVESTMENT CASE STUDY DATA SOURCE NAME AND REFERENCE WUIs Wildland-urban • Housing damage based on data from the Association for the Development interfaces: of Industrial Aerodynamics (ADAI) at the University of Coimbra in Portugal Improvements to • Data for housing cost referenced the Portuguese National Institute of homes in Portugal Statistics • Loss reduction interpreted from the impacts calculated in the Technical Specifications for the Use and Occupational Charter of Continental Portugal for 2018 (COS2018) • Reduction in death and cost for treatment derived from the October 2017 fires in Portugal in the study Population exposure to particulate-matter and related mortality due to the Portuguese wildfires in October 2017 driven by storm Ophelia as well as consultations with the Regional Tourism Office for the Centre of Portugal • Potential burnt area based on COS2018 data and the emission factors provided in Estimativa de Emissões Atmosféricas Originadas por Fogos Rurais em Portuga • Avoided property value losses estimated from COS2018 data as well as through the database on land value through PORDATA • Avoided lost tourism based on values from the 2017 fires and information provided by the Regional Tourism Office for the Centre of Portugal • Fire suppression costs based on information provided by the Agency for the Integrated Management of Wildfires (AGIF) WUIs Wildland-urban • Industry damage calculated as a percent of total destruction using data interfaces: from ADAI at the University of Coimbra in Coimbra, Portugal Improvements to • Loss information based on data provided by the Central Regional industries in Portugal Coordination and Development Commission (CCDR-C) in Portugal in June 2018 • Average cost of the intervention based on the Manual of Fuel Management for operations with bush cutters • Loss reduction interpreted from the impacts calculated in the Technical Specifications for the Use and Occupational Charter of Continental Portugal for 2018 (COS2018) • Reduction in death and cost for treatment derived from the October 2017 fires in Portugal in the study Population exposure to particulate-matter and related mortality due to the Portuguese wildfires in October 2017 driven by storm Ophelia • Potential burnt area based on COS2018 data and the emission factors provided in Estimativa de Emissões Atmosféricas Originadas por Fogos Rurais em Portuga • Avoided property value losses estimated from COS2018 data as well as through the database on land value through PORDATA • Fire suppression costs based on information provided by the AGIF • Data on the co-benefit from the sale of biomass obtained through conversations with biomass producers Case studies Wildfires 144 Fuel Fuel Management for • Losses estimated by ex post analysis of the 2017 fires in Pedrógão Grande Management forests in Poturgal • Reduction of losses to forestry calculated from previous fires in Technical for Wildfire Specifications for the Use and Occupational Charter of Continental Portugal Risk for 2018 (COS2018) Reduction in forests • Reduction in death and cost for treatment derived from the October 2017 fires in Portugal in the study Population exposure to particulate-matter and related mortality due to the Portuguese wildfires in October 2017 driven by storm Ophelia • Avoided lost tourism based on values from the 2017 fires and information provided by the Regional Tourism Office for the Centre of Portugal • Fire suppression costs based on information provided by the AGIF • The co-benefit from sale of cork trees calculated based on data from the Portuguese Industry of Cork Decision Decision Support • Avoided direct and indirect forest fire costs obtained from the 2020 white Support Tools Tools for Climate paper on Forest Fires in the Alps for Climate Change Adaptation • The co-benefit from improved silviculture calculation based on information Change on the economy of Finland Adaptation and Alerting • Information on the cost of the tool and the estimated users obtained from for Wildfire consultations and coordination with a senior researcher who developed the Risk decision support tool Reduction Decision Alerting and • Data on potential injuries and lives lost obtained from assessment of the Support Tools Preparedness for past fires in Portugal and validated with ex post data on nonexistent DRM for Climate Wildfires in Portugal measures for extreme hazard events in Pedrógão Grande, Mati, and Rafina Change cities in Greece Adaptation • Cost of injuries based on the Portugal Health Regulatory Authority and Alerting for Wildfire • The cost of alerting obtained by telephone company data interpolated for Risk Pedrógão Grande Reduction Decision Alerting and • Data on potential injuries and lives lost obtained from assessment of the Support Tools Preparedness in past fires in Portugal and validated with ex post data on nonexistent DRM for Climate Greece measures for extreme hazard events in Pedrógão Grande, Mati, and Rafina Change cities in Greece Adaptation • Costs of injuries in Mati obtained with data from consultations with Greek and Alerting fire specialists and on the ground estimations following deployments to for Wildfire Greece Risk Reduction Cross-border Cross-border support • Cost of the tool obtained from the project manager and developer of support, and coordination SPITFIREa coordination mechanisms for • Direct costs obtained from data provided by the Portuguese Institute for mechanisms wildfires Nature and Forest Conservation and by the Polytechnic University of and capacity Valencia building for wildfires Source: World Bank analysis; based on external data and information Case studies Wildfires 145 Models need to be adapted to type of investment. lessening reductions in biomass and biodiversity. The When modelling hypothetical prevention investments, ratios also help decision-makers determine what such as WUI management and fuel management for future climate adaptation strategies should be wildfire risk reduction, the BCA is assessed over a considered. certain time horizon and includes a sensitivity analysis of low-to-high hazard impacts and discount rates. For Results of wildfire risk reduction investments benefit- the modelling of decision support tools, the start-up cost assessments yield net benefits. However, and assumed maintenance cost is measured in consistent with research findings, some regional and comparison to forest fire direct and indirect costs forest-level infrastructure investments tend to have avoided in the region as well as improved GDP with relatively smaller BCRs. Comprehensive analysis to efficient silviculture. This model is based on a study inform mitigation projects (including considering from Ireland that was used to estimate the overall GDP climate change scenarios) and data on second and improvement as well as studies on Austrian forest third dividend costs avoided could therefore be highly management. beneficial for investments to maximize benefits temporally and across sustainability goals. More Economic analysis and research on wildfires are details are included in Figure 28 below. extremely important because, even with climate change mitigation, the danger of forest fires is imminent Figure 28 presents boxplots that display the dis- unless effective adaptation strategies are adopted. tribution BCRs for different types of investments in BCRs for investments in wildfire prevention in the wildfire based on a five number summary: minimum, context of climate change adaptation reveal how such first quartile, median (shown in red), third quartile, and investments address the detrimental impacts of maximum. Extreme values are excluded from the top climate change on forest fires and yield co-benefits in graph and included in the bottom one. Figure 28: Findings of BCA for wildfires (BCRs) Source: World Bank analysis; based on external data and information Case studies Wildfires 146 WUI is a transition zone where wildlands interact with vegetation meant to stop or control fire around humans and their activities (Stein, et al., 2018), an buildings, farms, and residential properties as they area where communities and economic activity can provide a fixed safety distance that protects the therefore particularly be directly affected by wildfires. civilians (Natural Resources Conservation Services, Studies have shown that there is a lack of standardized 2011; WUIVIEW, 2019). Fuel breaks are strips or building codes and interventions related to blocks of vegetation that have been altered to slow or development and protection of houses and buildings control a fire and slow the spread of fire because they in WUI areas. These codes and interventions are are managed to provide far less fuels to carry the essential for the reduction of risks and losses to flames. These adaptation measures are typically communities. However, the reality is that the implemented by forest managers and have shown to development of these standards is complex and substantially reduce fire risks but are not evenly implementation non-uniform (Pastor, et al., 2020). applied in fire-prone areas. Moreover, wildland-industry interfaces are areas of considerable risks as they can lead to large amounts of • Case study 20 (new analysis under this project, ex industrial damages and even follow-up disasters. It is post (Bennett, et al., 2010)): The analysis of an therefore essential for homes and industries in WUI investment in fuel management using fuel breaks in areas to invest in prevention by use of the creation of the Central Region of Portugal yields positive net defensible space. Government-led preparedness and benefits (BCR 11.9 greater than 1). This case study regulations should be undertaken and implemented, uses a novel methodology to evaluate losses such as minimum safety distance or vegetation straps, avoided, the additional benefits of implementing around homes and industrial facilities. In Europe, fuel breaks as a preventive investment. In addition research, laws, and monitoring of industrial facilities in to limitations of research in terms of data and or near the forest or wildland perimeters tend to be information like for case studies 18 and 19, general limited, except fire research projects such as SPREAD research on effectiveness of fuel breaks would be (2020). important as assumptions for this analysis were based on expert judgement. As for other case • Case study 18 (new analysis under this project, ex studies, transferability of this analysis and ante (Augusto, et al., 2020)): The analysis of a assumptions is low given that it is a technical hypothetical investment of managing WUI in management and service-related solution. Pedrógão Grande, Portugal, yields positive net benefits (BCR 3.1 greater than 1). This is possibly Decision support tools can support climate change underestimated given lack of data and information adaptation and alerting for wildfire risk reduction. on longer-term impacts such as soil erosion impacts Decision support tools are tools based on computers from fires or land and property value increase in and data that people use during the process of areas. decision-making for various objectives. There has been an increase in the use of decision support tools • Case study 19 (new analysis under this project, ex for climate change planning and adaptation to promote ante (WUIVIEW, 2019)): The analysis of a effective investment decisions and sustainable hypothetical investment of managing WUI in management of areas. These tools have been assessed Oliveira do Hospital, Portugal, yields positive net by EU projects like Impacts and Risks from High-End benefits (BCR 2.1 greater than 1). Limitations of the Scenarios: Strategies for Innovative Solutions research are similar to case study 18. (IMPRESSIONS) and it is important that they are tailored to local conditions to produce most efficient Fuel management interventions can support wildfire outcomes, particularly for decisions on green risk reduction. The increase in fire danger is projected infrastructure. Early warning and monitoring systems to increase in Western-Central Europe, but the absolute can support preparedness for wildfire risks. An fire danger remains highest in Southern Europe. Fuel example is the European Forest Fire Information management interventions such as firebreaks and fuel System (EFFIS) developed by JRC that provides breaks have been used for fire prevention and fire warnings and damage assessments (EFFIS, 2021). spread mitigation within forest areas and on their Alerting for wildfire emergencies can consist of days to peripheries where buildings and other assets may minutes of notification to residents in a region or area exist. Firebreaks are strips of bare soil or fire retarding that has imminent fire danger. Alerting systems are Case studies Wildfires 147 typically meant to save lives and reduce injuries and investment in alerting, evacuation planning, and are most effective as part of an emergency plan that independent fuel management of homes by includes evacuation routes and stationing of victims in homeowners in the Attica region of Greece yields safe zones. positive net benefits (BCR 39.3 greater than 1). Developing incentives for homeowners to manage • Case study 21 (new analysis under this project, ex their fuel loads surrounding personal property post (Bennett, et al., 2010)): The analysis of an requires consistent education and awareness investment in a Forest DSS (2013) implemented in raising as well as developing capacity-building the forest regions of Carinthia in Austria that was campaigns to encourage informed responses to developed for forestry extension services for small- alerts and executing emergency/evacuation plans. scale private landowners. The intention of the tool is The impact of softer investments such as alerting to provide information for owners to improve and community sensibilization to wildfire hazards is silviculture in a sustainable manner and understudied in the literature and therefore benefits simultaneously reduce the chance for forest fires may not or insufficiently be captured, particularly due to climate change. The analysis of the impacts of behavioural changes. The high BCR of hypothetical future benefits yielded positive net this case study can be explained by the scenario on benefits (BCR 5.8, NPV of around €0.99 million). It which it is based, namely, the second deadliest fire has to be noted however that this analysis was in the 21st century (Mati fire from 2018). Results of based on numerous assumptions given lack of data both case studies 22 and 23 would support low- for this project and further research would be cost investments with potential to save many lives needed to understand relationships between and assets. improved silviculture and GDP, as this was a main factor assumed that affected the BCR to be higher Cross-border support, coordination mechanisms, and than 1. Micro- and macro-studies could generally capacity building can reduce wildfires risks. Disasters improve the understanding on multiple benefits of and hazards are not bound by the borders of countries improved silviculture in a region, including, for and it is essential for European countries to work example, socio-psychological factors to private collaboratively and share their resources and good forest owners. practices when a disaster strikes, especially in cross- border areas that are vulnerable to disasters such as • Case study 22 (new analysis under this project, ex forest fire and floods. Several EU projects have been ante): The analysis of a hypothetical investment in launched to enhance cooperation across borders in alerting, evacuation planning, and independent fuel terms of responses to disasters and emergencies. management of homes by homeowners in the The project INTER’RED (European Commission, 2020) Central Region of Portugal is undertaken to assess is an ongoing project that improves rescue services the benefits of both government-initiated alerting in the cross-border Grande Région, which covers and preparedness as well as citizen-driven fuel Luxembourg, France, Germany, and Belgium. management on private homes. This case study Capacity-building investments in the Czech Republic, yields positive net benefits (BCR 11 greater than 1). Poland, or Spain have shown qualitatively high Developing incentives for homeowners to manage impacts and benefits of training for the effectiveness their fuel loads surrounding personal property of response. requires consistent education and awareness raising as well as developing capacity-building • Case study 24 (new analysis under this project, ex campaigns to encourage informed responses to ante (FEU Fire Officer Associations, 2020): The alerts and executing emergency/evacuation plans. analysis of an investment in creating and deploying The impact of softer investments such as alerting the SPITFIRE tool (European Commission, 2017) and community sensibilization to wildfire hazards is found net benefits (BCR 1.6). This decision support understudied in the literature and therefore benefits tool offers high resolution meteorological and may not or insufficiently be captured, particularly forest weather forecasts presented in a GIS impacts of behavioural changes. environment to allow its joint management with other information needed by end users, such as • Case study 23 (new analysis under this project, ex forest managers and firefighters. This information ante (BBC, 2018)): The analysis of a hypothetical includes protected spaces, surveillance posts, Case studies Wildfires 148 roads, water points, distribution of material and Future deployments should investigate actual human resources, and so on). The results must be deployments and benefits of information platforms considered with caution given lack of research on as well as analyse the benefits of tools with a longer impacts of this type of investment and lack of data. lifetime than SPITFIRE. 3.5.2. WILDLAND-URBAN INTERFACES WILDLAND-URBAN INTERFACES: IMPROVEMENTS TO HOMES IN PORTUGAL This case study is a new ex-ante analysis under led to the evacuation of more than 2,000 people in the this project that involved modelling of hazards. city of Valencia (Pastor, et al., 2020). Moreover, because of climate changes, global warming and the Æ Introduction and background increase in heatwaves have increased the number and duration of forest fires in recent years, which has The WUI is a transition zone where wildlands interact resulted in an increase of fire risks in European with humans and their activities (Stein, et al., 2018). countries (EEA, 2020). In addition, due to housing As a result, forest fires occurring in WUI areas demands and lack of management, more development negatively affect urban and rural communities. WUI is occurring in the WUI without appropriate forest fires are prevalent in Northern and Southern Europe, management and those homes and industries near which leads to destruction and generates great social the wildland are increasingly susceptible to fire when and economic losses. The 2017 fire in Portugal interventions to reduce fuel in surrounding areas is not resulted in more than 110 deaths and thousands of undertaken (see Figure 29 for an illustration of a fuel destroyed buildings, while the two WUI fires in Spain break for WUIs). Figure 29: Image of a fuel break for WUIs Source: (Portugal Wildfire, 2018) Studies have shown that there is a lack of standardized damage exceed far beyond property and lives. building codes and interventions regarding the houses and buildings in WUI areas. An analysis of forest fire Æ Description prevention and WUI protection systems in Spain suggests that it is essential to establish housing and urban planning This case study is an appraisal of the hypothetical standards and regulations in WUI areas. Also, the investment of managing WUI in the municipality of establishment of such standards requires the Pedrógão Grande in Portugal to study the fire impacts coordination of multiple agencies, which includes to homes with and without WUI management. The architects, forest and social scientists, and engineers case study considers the necessary actions taken by specializing in landscape, civil, and fire (Pastor, et al., regional authorities, whether by incentives, code 2020). These regulations are essential for the reduction changes, or direct management, that aid to create of risks and losses for the WUI communities. To better defensible spaces surrounding homes to reduce the understand the factors leading to the vulnerability of risk of fire to homes in the WUI. The June 2017 Portugal people, infrastructure, assets, and the outcomes of loss, fires in central Portugal saw the greatest loss of life in it is essential to assess cost benefit analyses since Pedrógão Grande, where 66 lives were lost in the area, wildfires are ever increasing in the EU region and loss and 254 people faced injuries, and nearly 1,000 homes Case studies Wildfires 149 were affected by the wildfires. The hypothetical (see Figure 30). The risk of damage related to the fuel investment is an ex post appraisal of the homes that management distance represents the probability of a were burned in 2017 in the municipality of Pedrógão house being damaged as a function of fuel Grande. This study seeks to analyse the advantages of management distance (University of Coimbra, 2020). having an acceptable fuel management 10–50 m around dwellings in the area to minimize fire ignition • Determination of the potential damage related to the and spread. The approach of this study is to use fuel management distance considering the probability existing research on losses from fires in Portugal and of damage and the potential of destruction (risk of estimate the triple dividend benefits that could have damage and the percentage of loss: 100 percent, 75 been realized had there been an investment in the percent, 40 percent, 20 percent, 0 percent). See Pedrógão Grande region for WUI management for Figure 31. dwelling fire risk reduction. • Next, the cost elements are calculated for economic Æ Methodology loss from damage to housing. The estimated area of a typical home in Pedrógão Grande is 10 m × 10 m = The BCA is over a 30-year time horizon and undertakes a 100 m2 and the cost of a house in Pedrógão Grande is sensitivity analysis of low-to-high hazard impacts and €600 per m2. The data used for housing costs discount rates. A 30-year time horizon was chosen as the referenced the Portuguese National Institute of Institute for Nature Conservation and Forests in Portugal Statistics (Instituto Nacional De Estatistica, 2020). describes the 2017 fire as the one-in-29-year fire (ICNF, The average costs of each fuel management strip 2020). The discount rates used in the study vary from 3.5 (0–2 m, 2–10 m, 10–50 m, and >50 m) is estimated percent to 5 percent based on uncertainty of triple to be €1,078 per ha based on the Manual of Fuel dividend factors calculated during the 30-year period. Management for operations with bush cutters (Guiomar & Fernandes, 2011). See Figure 32. Æ The methodology is as follows: • The cost of fuel management around the typical • Analysis in the field of 963 houses affected by the fire house in the area as well as the potential damage is event with focus on the fuel management distance determined in euros. The costs include the use of and its impacts on damage (and damage avoided with bush cutters, which are normally used in this type of intervention). The distances studied are 0–2 m, 2–10 fuel management. Cost figures also include m, 10–50 m, and >50 m. employees, taxes, fuel, equipment, and so on. The discount rate used when evaluating the cost is 3.5 • Characterization of housing damage from 2017 as a percent over 30 years. The potential damage percentage of total destruction using data from ADAI reduction in euros per home is driven by each fuel at the University of Coimbra in Portugal. Houses that management strip option. Therefore, the investment are totally destroyed are considered 100 percent in fuel management in addition to the cost of destruction, severely damaged are those with 75 damage (costs avoided with interventions) is percent destruction, moderately damaged homes are estimated per house per year for each fuel those with 40 percent destruction, and light damage management option. The counterfactual investment are those with 20 percent destruction. compared in the BCA is the difference in losses between a no fuel management case and fuel • Analysis through spatial images of houses undamaged management of approximately 30 m surrounding in 2017 (0 percent destruction) by the fire event is the home. undertaken to determine fuel management distances Case studies Wildfires 150 Figure 30: Assessment of housing in Pedrógão Grande for destruction assessment and WUI distances Source: World Bank analysis; based on external data and information Figure 31: Variation of potential damage (%) as a function of fuel proximity to homes in Pedrógão Grande Source: World Bank analysis; based on external data and information Note: the x-axis represents the different types fuel management strip (by length). Case studies Wildfires 151 Figure 32: Fuel management investments and corresponding economic losses to homes in WUI Source: World Bank analysis; based on external data and information The Triple Dividend Framework includes the following impacts calculated in the Technical Specifications benefits described. for the Use and Occupational Charter of Continental Portugal for 2018 (COS2018) (Caetano, et al., Triple dividend 1 (costs avoided): 2010). • Reduction of lives lost was calculated using 2017 • The reduction in deaths related to cardiorespiratory fatalities within the municipality of Pedrógão Grande problems as well as the costs for treatment are corresponding with fuel management distances. calculated as direct losses avoided, referring to the COS2018 data. The values are derived from the • Reduction of injuries using 2017 injuries in Pedrógão October 2017 fires in Portugal in a paper by Augusto Grande. The Portugal Health Regulatory Authority et al. (2020). Based on the actual values of losses of (Direção Geral de Saúde) provides the cost per day lives and injuries, the ratio of injury to life lost is of injuries based on severity of injury, using which approximately 4:1. Therefore, the number of injuries the team estimated that 40 percent of cases were is arrived at by the number of deaths multiplied by 4 light injuries, 40 percent were medium injuries, and with the same distribution of injury severity as 20 percent were severe injuries (INFARMED, 2020). described above but focused on cardiorespiratory The total number of injuries is proportional to the problems. deaths during the 2017 event (approximately 4 injuries to 1 life lost) and calculated from the deaths • The cost of CO2 avoided from the reduction of avoided in TD1. The 4:1 injuries-to-fatalities ratio is wildfires is estimated to be €13 per tonne, the area based on the actual losses and injuries from the that could be burned based on COS2018 data, and Pedrogão Grande fire (June 17, 2017) and the the emission factors provided in Silva et al. (2006). region around Oliveira do Hospital (October 15, 2017) in Portugal as well as in Mati fires in Greece. • Avoided property value losses are estimated using The discount rate for the cost of treating injuries COS2018 data as well as through the database on during the time horizon is 3.5 percent. land value through PORDATA following the 2017 fire land and property value decline (PORDATA, • Fire damage prevented to housing is explained 2020b). above in methodology. • Avoided lost tourism income is based on actual • Reduction of losses to agriculture, forestry, and values from the 2017 fires. Results are based on the grazing is considered a direct cost to losses in the information provided by the Regional Tourism Office region. These values were interpreted from the for the Centre of Portugal (PORDATA, 2020a). Case studies Wildfires 152 • Cost of sheltering and displacement avoided is • Increased security from lessened impacts and less estimated by the cost of rental per day per person volatility due to wildfire management is assumed to (approximately €15 per day per person), the number be 1 percent of GDP for the region—this figure was of people requiring shelter (based on damaged estimated based on the Portuguese economic housing), and the average time sheltering was growth of 1.8 percent forecasted by the Bank of needed after the 2017 fires. It is assumed that 50 Portugal, which will be lower in inland areas such as percent of people stayed with relatives and therefore Pedrógão Grande. A discount rate of 3.5 percent is no additional cost was borne, and the remaining 50 used when calculating this dividend over the period. percent stayed in rentals. The average time to recovery is estimated at 6 months. In addition, the • Increase in land purchases estimates the value of loss to productivity by displaced persons is land that is increased due to a decrease in wildfire calculated as a GDP per capita reduction per risk due to WUI management. A 1 percent increase working person per day and assuming that persons in land value (approximated as housing value) in staying in rentals/hotels or with family have 50 fire-prone areas is assumed. Also considered in this percent productivity. conservative estimate is the possibility that people tend not to buy land at typical market value in areas • Soil erosion due to the wildfires is estimated based where tragic accidents have occurred, such as lives on the cost of soil lost in 2008 at €5.82 per ha lost in the 2017 fires, especially in a short time (US$7.03 per ha) over 12 years (Pinheiro, 2015). following the event. Hectares burned in Pedrógão Grande are quantified in COS2018. A discount rate of 5 percent is used Triple dividend 3 (co-benefits) over the period. • Fixed fire suppression costs are those that are • Fire suppression costs avoided are operational related to the existing fire service structure costs based on the AGIF that provides national cost regardless of whether there is a fire or not. It includes values. These costs have been scaled to the fire brigade costs, administration, aerial rentals with Pedrógão Grande region to estimate the reduction basic contracts, and so on. Fire suppression costs in yearly operation costs due to enhanced WUI are evaluated using data from the AGIF that have management (AGIF, 2020). The operational costs been scaled to the Pedrógão Grande region to are those resulting from service needs during fire estimate the reduction in yearly fixed costs due to suppression, including equipment, hourly payment enhanced WUI management (AGIF, 2020). The to firefighters, overtime payment for aerial means, justification is that with yearly reductions in fire meals in the field of operations, and so on. Over the losses due to improved fuel management, fixed period of study, a discount rate of 5 percent has costs could be reduced to a reasonable degree been used. without compromising fire services. A discount rate of 5 percent is used over the period. Triple dividend 2 (unlocking economic potential): • The sale of biomass is considered a co-benefit of • The economic value added to the Portuguese WUI fuel management due to increased biomass economy from biomass production (TD3) activities production from clearing forest fuel. It is estimated is a multiplier of 1.77 based on existing data of as 30EUR/ton plus the cost of operations. The data biomass production in California (2020) and scaled was obtained through conversations with biomass to Portuguese consumer price indices (University of producers. California, 2020). This multiplier captures the indirect and induced economic contribution from Æ Results of the analysis by dividends wood biomass production based on the purchasing and overall of materials and services directly within the forestry supply chain (indirect) and the purchasing of goods Overall, the analysis shows a high BCR greater than 1, and services by workers in the industries (induced which indicates a positive economic rationale for effects). The economic ripple effects are accounted undertaking this preventive investment (see Table 58). for in TD2 as they offer additional economic The highest benefits appear to be those from avoided potential regardless of a wildfire occurring. losses, but the second order economic effects Case studies Wildfires 153 (dividend 2) as well as co-benefits (dividend 3) are protecting over the 30-year time horizon (see likely to be underestimated due to lack of data for Table 59). Table 58: CBR of WUIs in Pedrógão Grande (in million €) BCR: 3.1 BENEFITS (€) COSTS (€) Dividend 1 140.68 Dividend 2 1.45 Dividend 3 2.17 Total 144.29 46.75 Source: World Bank analysis based on external data and information Table 59: Expanded triple dividend BCR calculation of WUIs in Pedrógão Grande (in million €) WUI MANAGEMENT - HOMES FIRST DIVIDEND (€) Reduction of lives 107.25 Reduction of injuries 4 Fire Damage prevented (houses) 22.7 Reduction of losses to agriculture 0.84 Reduction of losses to forestry 1.51 Reduction of losses to grazing 0.003 Reduction in deaths related to cardiorespiratory problems 1.14 Reduction in treatment costs related to cardiorespiratory problems 0.01 Cost of CO2 avoided 0.16 Avoided loss of property values 1.03 Avoided loss of tourism income 0.24 Cost of sheltering/displacement avoided - lodging 0.55 Cost of sheltering/displacement avoided - productivity 0.69 Soil erosion costs avoided 0.01 Fire suppression, operational costs, lowered with WUI management 0.54 Total first dividend 140.68 SECOND DIVIDEND (€) Longer-term economic add from biomass production (induced/indirect) 0.73 Security/reduced volatility from mitigation/risk perception 0.71 Increase in land purchases 0.005 Total second dividend 1.45 THIRD DIVIDEND (€) Economic co-benefits Case studies Wildfires 154 Fire suppression, fixed costs, lowered with WUI management 0.02 Sale of biomass for energy production 2.15 Social co-benefits Improved awareness of WUI management by homeowners (qualitative) Total third dividend 2.17 TOTAL DIVIDEND 144.29 Total cost 46.75 BCR 3.1 Source: World Bank analysis based on external data and information Æ Challenges faced and lessons learned benefits factors could be valuable to an expansion of this study. Distributional impacts of the creation of Data that could not be ascertained from Portuguese defensible space for appropriate WUIs are that these sources, including soil erosion from fires, should be zones enable homeowners to avoid property value investigated for the Portuguese and/or European losses and for tourism in the area to remain context since fires are becoming more prevalent and uninterrupted in the case of future wildfires. Moreover, long-term costs are not always evaluated. In addition, the property value of homes and land in the sur- accurate estimations of land and property value rounding area is expected to increase with the increase from reduced volatility in the area due to establishment of appropriate defences in WUI, which lessened fire starts, direct and indirect fire suppression benefit home and landowners in the area. costs avoided, and other triple dividend 2 and 3 WILDLAND-URBAN INTERFACES: IMPROVEMENTS TO INDUSTRIES IN PORTUGAL This case study is a new ex-ante analysis under this distance is 50 m for isolated infrastructures and 100 m project that involved modelling of hazards. for industrial parks) (Caballero, et al., 2007). Æ Introduction and background However, there is still progress that is needed regarding industries in WUI areas. European countries face a While forest fires cause fatalities, injuries, and property lack of standardized laws and monitoring of industrial losses for residents living in the WUI areas, they also facilities located in or near the wildlands. Fire and cause industrial damage that can lead to accidents safety measures in Europe are usually categorized and natural-technological (Natech) emergencies based on established activity such as nuclear and (WUIVIEW, 2019). Wildland-industry interface is a chemical, while measures related to WUI scenarios branch of WUI and looks particularly at the impacts of are usually limited to fuel-reduced fringes (WUIVIEW, fires on industries and cascading consequences that 2019). Though there are forest fire research projects may arise from fire hazards. Fires near industrial areas like SPREAD that produced fire risk maps and analysed can cause accidents where large amounts of toxic or fire spread patterns in Europe (CORDIS, 2020), more flammable materials are accumulated. Therefore, it is investments and studies should be undertaken with a particularly important for industries in WUI areas to be focus on WUI improvements to industries to reduce well prepared for the occurrence of forest fires to avoid damages and economic losses in the industrial sector. economic and social losses during fire seasons by the To better understand the factors leading to the creation of appropriate defensible space surrounding vulnerability of people, infrastructure, and assets and properties. To date, some regulations have been made the outcomes of loss, it is essential to assess cost for WUI improvements to industries. For instance, in benefit analyses since wildfires are ever increasing in Spain, it is required to have a low-density vegetation the EU region and loss and damage exceed far beyond strap around the industrial infrastructures with a property and lives. minimum safety distance of 30 m (in Portugal this Case studies Wildfires 155 Æ Description Æ Methodology This case study investigates the hypothetical The BCA is an appraisal of wildland-industry interface investment of managing WUI in the municipality of over a 40-year time horizon and undertakes a sensitivity Oliveira do Hospital in Portugal to study the impacts to analysis of low-to-high hazard impacts and discount industries with and without WUI management. The rates. A 40-year time horizon was chosen as the Institute case study considers the necessary actions taken by for Nature Conservation and Forests in Portugal describes regional authorities, whether by incentives, code the 2017 fire as the one-in-39-year fire (ICNF, 2020). The changes, or direct management, that aid to create discount rates used in the study vary from 3.5 percent to defensible spaces surrounding industries to reduce 5 percent based on uncertainty of factors calculated the risk of fire to industries in the WUI. The October during the 40-year period. 2017 Portugal fires in Oliveira do Hospital in Portugal’s interior led to casualties, losses in industrial facilities, The methodology is as follows: as well as affected other industries in the area. The hypothetical investment studies the industries that • Analysis in the field of 65 industrial facilities affected were damaged in 2017 and analyses the advantages by the fire event with focus on the fuel management of having acceptable fuel management around distance and its impacts on damages with and industrial buildings to minimize fire ignition and without WUI risk reduction interventions. The spread. The approach of this study is to use existing distances studied are 0–2 m, 2–10 m, 10–50 m, research on losses from fires in Portugal and estimate and >50 m. Table 60 below includes information on the triple-dividend benefits that could have been the industrial facilities that were totally or partially realized had there been an investment in the Oliveira destroyed by the fire and not the distribution of all do Hospital region for WUI management of industrial 95 industries analysed. Data on the industry types fire risk reduction. of the 30 facilities that were not affected by the fires were not available. Industries and number of each type are Table 60: Table 60: Industrial facilities affected by industry CONSTRUCTION AND BUILDING MATERIALS 20 Timber and cork 8 Vehicles, machinery, and equipment 9 Metal products 3 Agriculture, forestry, ranching, and hunting 2 Food and beverage industry 6 Furniture and mattresses 1 Transports 5 Water, gas, and electricity supply 5 Manufacture of textiles 1 Other 5 Total 65 Source: World Bank analysis based on external data and information Case studies Wildfires 156 • Characterization of industry damage from 2017 is a represents the probability of an industry being percentage of total destruction using data from damaged as a function of the fuel management ADAI at the University of Coimbra in Coimbra, distance. Portugal (2020). • Determination of the potential damage related to • Assessment of fuel management from spatial the fuel management distance which considers the images26 of 30 industrial facilities undamaged in probability of damage and the potential of 2017 (0 percent destruction) by the fire event to destruction (risk of damage and the percentage of determine fuel management distances. The risk loss: 100 percent, 75 percent, 40 percent, 20 damage related to the fuel management distance percent, 0 percent). See Figure 33. Figure 33: Variation of potential damage (%) as a function of fuel proximity to industries in Oliveira do Hospital Source: World Bank analysis based on external data and information Note: the x-axis represents the different types fuel management strip (by length). • Next, the cost elements are calculated to determine surrounding the industrial property). Therefore, the economic loss from damage to industrial the investment in fuel management along with the facilities. The estimated average cost of costs of damage (costs avoided with interventions) infrastructure, equipment, and raw materials of an was estimated per industrial facility per year for industrial facility in Oliveira do Hospital is around each fuel management option. The discount rate €0.83 million. Data from the CCDRC (CCDRC, 2020) used when evaluating the cost is 3.5 percent over in Portugal provide loss information to industrial 40 years. The potential damage reduction in euro facilities from the 2017 October fire from which the per industry is driven by each fuel management number above is derived based on data available strip option. Therefore, the investment in fuel for affected facilities that requested support from management along with the costs of damage the government. In addition, based on the image- (costs avoided with interventions) was estimated based analysis, the estimated area of each industrial per industry per year for each fuel management facility is approximately 50 m × 20 m = 1,000 m2. In option. The counterfactual investment compared addition, based on the image-based analysis, the in the BCA is the difference in losses between a no estimated area of each industrial facility is fuel management case and fuel management of approximately 50 m × 20 m = 1,000 m2. approximately 30 m surrounding the industrial facility. The average costs of each fuel management • The cost of fuel management around the typical strip (0–2 m, 2–10 m, 10–50 m, and >50 m) industrial facilities in the area as well as the around the industrial facilities were estimated to potential damage was determined in euros. The be €1,078 per ha based on the Manual of Fuel potential damage reduction in euro per industrial Management for operations with bush cutters facility is driven by each fuel management strip (Guiomar & Fernandes, 2011). The creation and option (that is, creation of defensible space maintenance of defensible space is considered at 26 These images were taken in August 2017, two months before the fire event. Case studies Wildfires 157 a frequency of every two years within the time facilities as related to a decrease in economic horizon Figure 34 shows increased fuel impacts from wildfire losses. management investment costs of industrial Figure 34: Fuel management investments and corresponding economic losses to industries in Oliveira do Hospital Source: World Bank analysis based on external data and information The Triple Dividend Framework includes the following benefits: Triple dividend 1 (costs avoided): • Reduction of losses to agriculture, forestry, and grazing is considered a direct cost to losses in the • Reduction of lives lost was calculated using 2017 region. These values were interpreted from the fatalities corresponding with fuel management impacts calculated in the Technical Specifications distances. for the Use and Occupational Charter of Continental Portugal for 2018 (COS2018) (Caetano, Igreja, and • Reduction of injuries using 2017 injuries in Oliveira Marcelino 2010). do Hospital. The Portugal Health Regulatory Authority (Direção Geral de Saúde) provides the • The reduction in deaths related to cardiorespiratory cost per day of injuries based on severity of injury, problems and the costs for treatment are calculated using which the team estimated that 40 percent of as direct losses avoided, referring to the COS2018 cases were light injuries, 40 percent were medium data. The values are derived from the October 2017 injuries, and 20 percent were severe injuries fires in Portugal (Augusto et al. 2020). Based on the (INFARMED, 2020). The number of injuries is actual values of losses of lives and injuries, the ratio proportional to the deaths during the 2017 event of injury to life lost is approximately 4:1. Therefore, (approximately 4 injuries to 1 life lost) and the number of injuries is arrived at by a multiple of calculated from the deaths avoided in TD1. The 4:1 four to the number of deaths with the same injuries to fatalities ratio is based on the actual distribution of injury severity as described above losses and injuries from the Pedrogão Grande fire but focused on cardiorespiratory problems. (June 17, 2017) and the region around Oliveira do Hospital (October 2017) in Portugal as well as in • The cost of CO2 avoided from the reduction of Mati fires in Greece. The discount rate for cost of wildfires is estimated to be €13 per tonne, the area treatment of injuries during the time horizon is 3.5 that could be burned based on COS2018 data, and percent. the emission factors provided in Silva et al. (2006). • Fire damage prevented to industries is explained • Avoided property value losses are estimated using above in methodology. COS2018 data as well as through the database on Case studies Wildfires 158 land value through PORDATA (2020b) following the for in TD2 as they offer additional economic 2017 fire land and property value decline. potential regardless of a wildfire occurring. • Avoided productivity due to lost jobs from damage • Increased security from lessened impacts and less to industries as the number of labour days reduced volatility due to wildfire management is assumed to (PORDATA, 2020b) is estimated at €104 per labour be 1 percent of GDP for the region - this figure was day per worker. estimated based on the Portuguese economic growth of 1.8 percent forecasted by the Bank of • Avoided lost tourism income is based on actual Portugal, which will be lower in inland areas such as values from the 2017 fires based on consultations Oliveira do Hospital. A discount rate of 3.5 percent with the Regional Tourism Office for the Centre of is used when calculating this dividend over the Portugal. period. • Soil erosion due to the wildfires is estimated based Triple dividend 3 (co-benefits) on the cost of soil lost in 2008 at €5.82 per ha over 12 years (Pinheiro 2015). Hectares burned in • Fixed fire suppression costs are related to the existing Oliveira do Hospital are quantified in COS2018. A fire service structure regardless of whether there is a discount rate of 5 percent is used over the period. fire or not. It includes fire brigade costs, administration, aerial rentals with basic contracts, and so on. Fire • Fire suppression costs avoided are operational suppression costs are evaluated using data from the costs based on the AGIF that provides national cost AGIF. These costs have been scaled to the Oliveira do values. These costs have been scaled to the Oliveira Hospital (AGIF 2020). The justification is that with do Hospital region to estimate that reduction in yearly reduction in fire losses due to improved fuel yearly operation costs due to enhanced WUI management, fixed costs could be reduced to a management (AGIF 2020). The operational costs reasonable degree without compromising fire services. are those resulting from service needs during fire A discount rate of 5 percent is used over the period. suppression, including equipment, hourly payment to firefighters, overtime payment for aerial means, • The sale of biomass is considered a co-benefit of WUI meals in the field of operations, and so on. Over the fuel management due to increased biomass period of study, a discount rate of 5 percent has production from clearing. It is estimated at €30 per been used. tonne plus the cost of operations. The data were obtained through conversations with biomass Triple dividend 2 (unlocking economic potential): producers and are referred to 2020. • The economic value added to Portuguese economy Æ Results of the analysis by Dividends from biomass production (TD3) is a multiplier of and overall 1.77 based on existing data of biomass production in California (2020) and scaled to Portuguese Overall, the analysis shows a high BCR greater than 1, consumer price indices (University of California which indicates a positive economic rationale for 2020). This multiplier captures the indirect and undertaking this preventive investment (see Table 61). induced economic contribution from wood biomass The highest benefits appear to be those from avoided production based on the purchasing of materials losses, but the second order economic effects and services directly within the forestry supply (dividend 2) and economic co-benefits (dividend 3) chain (indirect) and the purchasing of goods and are likely to be underestimated due to lack of data (see services by workers in the industries (induced Table 62). effects). The economic ripple effects are accounted Case studies Wildfires 159 Table 61: BCR of WUI management to industries in Oliveira do Hospital (in million €) BCR: 2.1 BENEFITS (€) COSTS (€) Dividend 1 86.44 Dividend 2 4.49 Dividend 3 2.1 Total 93.04 44.48 Source: World Bank analysis; based on external data and information Table 62: Expanded Triple Dividend Cost Benefit Ratio Calculation of WUI management to industries in Oliveira do Hospital (in million €) WUI MANAGEMENT - INDUSTRIES FIRST DIVIDEND (€) Reduction of lives 33.02 Reduction of injuries 0.12 Fire Damage prevented (industries) 7.04 Reduction of losses to agriculture 2.5 Reduction of losses to forestry 1.58 Reduction of losses to grazing 0.01 Reduction in deaths related to cardiorespiratory problems 2.76 Reduction in treatment costs related to cardiorespiratory problems 0.03 Cost of CO2 avoided 0.27 Avoided loss of property values 33.81 Avoided productivity loss 0.35 Avoided loss of tourism income 3.61 Soil erosion costs avoided 0.02 Fire suppression, operational costs, lowered with WUI management 1.32 Total first dividend 85.44 SECOND DIVIDEND (€) Longer-term economic add from biomass production (induced/indirect) 0.7 Security/reduced volatility from mitigation/risk perception 3.8 Total second dividend 4.49 THIRD DIVIDEND (€) Economic co-benefits Fire suppression, fixed costs, lowered with WUI management 2.05 Sale of biomass for energy production 0.06 Social co-benefits Improved awareness of WUI management by industry operators (qualitative) Case studies Wildfires 160 Total third dividend 2.1 TOTAL DIVIDEND 93.04 Total cost 44.48 BCR 2.1 Source: World Bank analysis; based on external data and information Æ Challenges faced and lessons learned increase in fire danger is projected to increase in Western-Central Europe, but the absolute fire danger Data that could not be ascertained from Portuguese remains highest in Southern Europe. Fuel sources, including soil erosion from fires, should be management interventions such as firebreaks and investigated for the Portuguese and/or European fuel breaks (see Figure 35 and Figure 36) have been context since fires are becoming more prevalent and used for fire prevention and fire spread mitigation the long-term costs are not always evaluated. In within forest areas and on their peripheries where addition, accurate estimations of land and property buildings and other assets may exist. Firebreaks are value increase from reduced volatility in the area due strips of bare soil or fire retarding vegetation meant to to lessened fire starts, direct and indirect fire stop or control fire around buildings, farms, and suppression costs avoided, and other triple dividend 2 residential properties as they provide a fixed safety and 3 benefits factors could be valuable to an distance that protects the civilians (Natural Resources expansion of this study. Conservation Services, 2011; WUIVIEW, 2019). Fuel breaks are strips or blocks of vegetation that have 3.5.3. FUEL MANAGEMENT FOR WILDFIRE been altered to slow or control a fire and slow the RISK REDUCTION IN FORESTS spread of fire because they are managed to provide far less fuels to carry the flames. These adaptation Æ Introduction and background measures are typically implemented by forest managers and have shown to substantially reduce More severe fire weather in Europe and substantial fire risks but are not evenly applied in fire-prone expansion of the fire-prone area and longer fire areas. The countries with the highest absolute seasons are projected in most regions of Europe, danger to wildfire remain Portugal, Spain, and Turkey particularly for high-emissions scenarios. The (De Rigo, et al., 2017). Figure 35: Fuel-reduced fringes (firebreaks and fuel breaks) provide a fixed safety distance Source: Bennett, et al. (2010) Case studies Wildfires 161 Figure 36: View of a fuel break in a pine stand in Central Portugal (photo of ADAI) Source: ADAI (2020) Climate change projections suggest substantial of the 2017 fires in Pedrógão Grande, as well as other warming and increases in the number of heat waves, countries that have faced large fires, to develop droughts and dry spells across most of the relationships between fire hectares burned and Mediterranean area and Southern Europe, which casualties. Portuguese legislation requires the would increase the length and severity of the fire existence of fuel breaks around a maximum non-urban season. For these reasons as well as the densification area of 100 km2. These are called primary fuel breaks of lived areas near forests, the need to understand the as other narrower fuel breaks may exist in the impacts of interventions to reduce and alleviate fire interspatial areas. The primary fuel break can have hazards is of paramount importance (EEA, 2020). some vegetation that is less combustible, like cork BCAs such as the one performed for this and other trees, which are also examined for co-benefits in this studies attempt to comprehensively quantify the triple study. A novel methodology is employed to evaluate dividend benefits that are often not included in wildfire the benefit of fuel breaks as a priority fuel management intervention BCAs. More such studies should be investment. Based on past fires and literature review undertaken in fire-prone parts of Europe, and this case of the outcomes, interpolations have been made for study can provide a sample methodology on how to the fuel break economic effectiveness for industry, capture triple dividend benefits. housing, and other asset losses avoided. Æ Description Æ Methodology The case study analyses pine tree forest plots in the The BCA is over a 30-year time horizon and undertakes Central Region of Portugal to appraise the cost of fuel a sensitivity analysis of low-to-high hazard impacts management using fuel breaks and comparing them and discount rates. A 30-year time horizon was chosen to losses avoided, including lives saved, injuries as an analysis carried out using data from the Institute avoided, and losses avoided to homes, forestry, and for Nature Conservation and Forests in Portugal shows tourism. Such an intervention would be undertaken by that this is a median value for the occurrence of very forest managers by direction of the regional large fires in central Portugal (ICNF, 2020). Lives lost government or appropriate ministry. Losses included are estimated with an investigation of 22 case studies in this study have been estimated by ex post analysis of large fires with fatalities in different countries that Case studies Wildfires 162 shows that there is an increase of fatalities with the management operations over 30 years with a discount extension of the fire.27 Excluding five cases of rate of 5 percent over that period. The cost also relatively small fires with many fatalities as outliers, an includes the fuel break development costs of €3,000 approximate linear relationship between number of per ha and plantation of cork at €1,000 per ha. fatalities and burned area in large fires can be found. This amounts to a 0.339 fatalities per 1000 ha burned It is important to note that the effectiveness of a fuel in very large fires.28 It should be noted that not all large break is not 100 percent as it depends on the hazard fires cause causalities, as there are other factors that conditions and the level of firefighting presence. The may cause or avoid casualties. Conversely, we can see percentages in Table 63 are based on expert that there are fire events that create a large number of assessment of the capacity of a fire crew stopping a victims with relatively small burned areas. From the fire in a well-managed firebreak (also a designated fuel analysis, it is found that any effort to reduce the area of break) in a 10 × 10 km2 forest plot. In the case of an a large fire will contribute to saving lives at an average approaching fire of a very high hazard, it is assumed rate of 2,950 ha per life. that in 30 percent of the cases, fire crews will be successful in stopping the fire. The 30 percent also The cost of fuel management considers an extension relate to the area of forest that is preserved from fire of forestland covered by a single species (either Pine damage. However, in the case of spot fires or very high or Eucalyptus) in a plot of land 10 × 10 km2 with a fuel winds, the fire suppression efforts by crews might not break 125 m wide in the case of a very high hazard be as efficacious, and it is assumed that this occurs in condition. The fuel break assisted by fire suppression 70 percent of cases (70 percent unsuccessful and 30 forces will reduce the probability of a fire burning that percent successful fire suppression). The effectiveness plot to 70 percent, in comparison to not having a fuel of firebreaks is dependent on the fire hazard break. The estimated cost of creating a fuel break and (extreme to medium in this study), which is a function converting the species to cork trees is €1 million to of weather conditions, fuel loads, topography, and protect a plot of 10 kHa. The maintenance of the fuel other elements, and its characterization is based on break using machinery will cost an average of €500 historical data and events in Portugal. The values per ha every three years. The total cost of the fuel shown in Table 63 are used in the study to evaluate management intervention in the 250 ha of fuel break is the effectiveness of fire break. approximately €1.2 million and includes nine fuel Table 63: Estimation of effectiveness of fuel breaks with regard to the hazard level and degree of effective fire suppression Effective or Low Suppression Level ofFire Hazard Existence of Fuel Break Services Extreme V. High High Medium Effective fire suppression services 5% 30% 60% 80% Yes Low fire suppression services 1% 5% 30% 50% Effective fire suppression services 1% 5% 30% 60% No Low fire suppression services 0% 1% 5% 30% Source: World Bank analysis; based on external data and information 27 The countries studied include Portugal, Greece, the United States, France, and Australia. 28 From large fire events in various countries, a linear relationship was made between fatalities per area to determine this value. Case studies Wildfires 163 The following scenarios on investment in fuel break • Injuries avoided estimates the number of injured and fire suppression are considered: people as four times the number of fatalities based on actual ratios from past fires in Portugal. Therefore, 1. No fuel break and effective fire suppression under an investment in creating and maintaining a fuel extreme fire hazard: 1 percent effectiveness break would avoid about 33.9 injuries per 10 kHa of intervention based on relationships shown in 2. No fuel break and effective fire suppression under Table 63 The discount rate of the cost of treatment very high fire hazard: 5 percent effectiveness for injuries over the period analysed is 3.5 percent. 3. Fuel break and effective fire suppression under • Fire damage prevented to houses is based on the extreme fire hazard: 5 percent effectiveness analysis of 31 cases of fires with an area larger than 10 kHa up to 2 MHa that yielded an average rate of 4. Fuel break and effective fire suppression under 0.65 houses per kHa. Comparing scenarios 2 and 4 very high fire hazard: 30 percent effectiveness. above, the investment in fuel breaks would correspond to an avoided loss of 0.65 × 3 = 1.95 The BCA compares the difference in losses avoided houses for each plot of 100 kHa of intervention. The between scenarios 2 and 4. The expected burned area discount rate for fire damage over the time horizon in a very high fire hazard within a 30-year time horizon is 3.5 percent. Using data on the average value of comparing no fuel break and fuel break cases. This houses in central Portugal, provided by the National results in avoided losses of protected areas of 25 kHa Institute of Statistics (PORDATA, 2020b), these within every 100 kHa of forest managed in the case of avoided losses amount to €0.23 million. an effective fuel break with effective fire suppression. Based on the success rates of fire suppression • Reduction of losses to forestry considers the described previously, on average, 30 percent of the impacts calculated from previous fires in Technical area will be saved from fire burn. On the other hand, if Specifications for the Use and Occupational Charter there is no investment in fuel breaks, the probability of of Continental Portugal for 2018 (COS, 2018; protecting the forest from fires will be decreased to 5 Caetano, et al., 2010). percent (considering factors that may contribute to the success of operations, such as the lack of spot fires • The reduction in deaths related to cardiorespiratory and crown fires). The difference between the two problems as well as the costs for treatment are scenarios (with and without firebreaks but both with calculated as direct losses avoided, referring to the effective fire suppression services) amounts to avoided COS2018 data. The values are derived from the losses of 25 percent (= 30 − 5 percent). As the unit of October 2017 fires in Portugal in a paper by Augusto land used for the calculations is 100,000 ha, the et al. (2020). Based on the actual values of losses of avoided loss is estimated as 25,000 ha of managed lives and injuries, the ratio of injury to life lost is forest area. approximately 4:1. Therefore, the number of injuries is arrived at by a multiple of four to the number of The Triple Dividend Framework includes the following deaths with the same distribution of injury severity benefits: as described above but focused on cardiorespiratory problems. Triple dividend 1 (costs avoided): • A stand of pine (Pinus pinaster) emits 26 tonnes of • Considering the two cases of with and without fuel CO2 per each hectare burned (Silva, 2006). The break interventions in a plot of 100 kHa the avoided investment in fuel management in creating a fuel loss of burned area is 25 kHa/100 kHa. According breakin plots of 100 kHa would correspond to an to the present analysis of lives lost explained above, avoided loss of 25 kHa after a period of 30 years in this corresponds to avoided fatalities of about 8.48 an area with a return period of 30 years. This is lives per 100 kHa of intervention in the case of a equivalent to an amount of 650,000 tonnes of CO2 major conflagration. A discount rate of 3.5 percent emissions avoided per 100 kHa with intervention. is used for fire damage avoided to housing plots for the time horizon. Case studies Wildfires 164 • Property value decrease assumes a 5 percent • Increased security from lessened impacts/less decrease avoided with fuel breaks (PORDATA, volatility due to wildfire management is assumed to 2020b). be 1 percent of GDP for the region. A discount rate of 5 percent is used over the time horizon for this • Avoided lost tourism income is based on actual factor. values from the 2017 fires. Data were obtained from the Regional Tourism Office for the Centre of • Increase in land purchases estimates the value of Portugal. the reduction by the increase in land purchases. A 1 percent increase in land value (approximated as • Cost of sheltering and displacement avoided is housing value) in fire-prone areas is assumed. Also estimated by the cost of rental per day, the number considered in this conservative estimate is the of people requiring shelter is based on damaged likelihood that people tend not to buy land at typical housing at a rate of 0.65 houses per kHa. It is market value in areas where tragic accidents have assumed that 50 percent of people stayed with occurred, such as lives lost in the 2017 fires, relatives and therefore no additional cost was borne, especially in a short time following the event. and the remaining 50 percent stayed in rentals. The average time to recovery is estimated at six months. Triple dividend 3 (co-benefits): In addition, the loss to productivity by displaced persons is calculated as a GDP per capita reduction • Fixed fire suppression costs are those that are per working person per day and assuming that related to the existing fire service structure persons staying in rentals/hotels or with family have regardless of whether there is a fire or not. It 50 percent productivity. includes fire brigade costs, administration, aerial rentals with basic contracts, and so on. Fire • Soil erosion due to the wildfires is estimated based suppression costs are evaluated using data from on the cost of soil lost in 2008 at €5.82 per ha the AGIF. These costs have been scaled to the (US$7.03 per ha) over 12 years (Pinheiro, 2015). Central Region of Portugal to estimate the reduction Hectares burned in Pedrógão Grande are quantified in yearly fixed costs due to enhanced fuel in COS2018. The discount rate of soil erosion losses management (AGIF, 2020). The justification is that over the time horizon is 5 percent. with yearly reduction in fire losses due to improved fuel management, fixed costs could be reduced to • Fire suppression costs avoided are operational a reasonable degree without compromising fire costs based on the AGIF that provides national cost services. The implementation of DRM measures values. These costs have been scaled to the Central will reduce the costs of suppression over time. Region of Portugal to estimate that reduction in Initially, it will reduce variable costs such as flight yearly operation costs due to enhanced WUI hours, fuel consumed by vehicles, and meals for management (AGIF, 2020). The operational costs fire services, and later, it may also reduce the fixed are those resulting from service needs during fire costs (less contracts with aerial means). Over the suppression, including equipment, hourly payment period of study, a discount rate of 5 percent has to firefighters, overtime payment for aerial means, been used. meals in the field of operations, and so on. Over the period of study, a discount rate of 5 percent has • In the area of the fuel break, the planting of other been used. trees can profit without impairing the risk reduction. For example, olive trees (olive oil), arbutus unedo Triple dividend 2 (unlocking economic potential): (alcoholic beverage), oak trees (cork), and paulownia biomass can all be planted in fuel breaks • The economic value added to Portuguese economy areas. The study considers the use of oak trees in from the sale of cork from (TD3) the fuel break areas the fuel break. Carbon sequestration is from the is multiplier of 2.032 based on solid wood product plantation of cork trees in the fuel break area that production in California (2020) and scaled to will promote carbon sequestration at a rate of 0.1 Portuguese consumer price indices (University of kg carbon per ha. This will correspond to 25 kg of California, 2020). carbon sequestration per year. Case studies Wildfires 165 Æ Results of the analysis by Dividends and overall • Sale of cork trees is calculated with data from the Overall, the analysis shows a high BCR greater than Portuguese Industry of Cork, one hectare of cork 1, which indicates a positive economic rationale plantation can produce a revenue of €388 every for undertaking this preventive investment (see nine years, with the required tree separation on a Table 64). The highest benefits appear to be those fuel. Given the area of the fuel break of 250 Ha and from avoided losses, but the second order economic the period of 30 years, this corresponds to a effects (dividend 2) and economic co-benefits revenue of €0.291 million. It is considered that the (dividend 3) are likely to be underestimated due to cost of plantation and maintenance of the stand is lack of data. Direct losses are likely higher due to 40 percent of this value, so the net income would the losses avoided to infrastructure (roads, bridges, be €0.194 million. and so on) for which the study did not have data to capture (see Table 65). Table 64: BCR of fuel management for wildfire risk reduction in the Central Region, Portugal (in million €) BCR: 12.3 BENEFITS (€) COSTS (€) Dividend 1 23.32 Dividend 2 2.63 Dividend 3 0.35 Total 26.31 2.21 Source: World Bank analysis based on external data and information Table 65: Expanded triple dividend BCR calculation of fuel management for wildfire risk reduction in the Central Region, Portugal (in 100000 €) FUEL MANAGEMENT FIRST DIVIDEND (€) Reduction of lives 50 Reduction of injuries 5.51 Fire damage prevented (industries) 2.26 Losses of timber production (trees not planted in the fuel break) -8.75 Reduction of losses to forestry 87.5 Reduction in deaths related to cardiorespiratory problems 25.79 Reduction in treatment costs related to cardiorespiratory problems 0.32 Cost of CO2 avoided 8.68 Avoided loss of property values 6.25 Avoided loss of tourism income 27.88 Cost of sheltering/displacement avoided - lodging 0.03 Cost of sheltering/displacement avoided - productivity 0.04 Soil erosion costs avoided 0.35 Case studies Wildfires 166 Fire suppression, operational costs, lowered with fuel breaks 27.37 Total first dividend 233.23 SECOND DIVIDEND (€) Economic value add from sale of cork (indirect/induced) 0.88 Security/reduced volatility from mitigation/risk perception 24.18 Increase in land purchases 1.25 Total second dividend 26.31 THIRD DIVIDEND (€) Economic co-benefits Fire suppression, fixed costs, lowered with WUI management 0.49 Carbon sequestration 1.08 Sale of cork 1.94 Total third dividend 3.51 TOTAL DIVIDEND 263.06 Total cost 22.12 BCR 11.9 Source: World Bank analysis based on external data and information Æ Challenges faced and lessons learned and indirect fire suppression costs avoided, and other triple dividend 2 and 3 benefits factors could be Data that could not be ascertained from Portuguese valuable to an expansion of this study. More research sources, including soil erosion from fires, should be is needed on the effectiveness of fuel breaks in general. investigated for the Portuguese and/or European While the data used in this case study is based on context since fires are becoming more prevalent and expert judgement from Portugal fires, it is important broader understanding of long-term costs are not to note that this may not be translatable to other always evaluated. In addition, accurate estimations of countries because it is both a technical management land and property value increase from reduced and a service-related (fire crews) solution. volatility in the area due to lessened fire starts, direct 3.5.4. DECISION SUPPORT TOOLS FOR CLIMATE CHANGE ADAPTATION AND ALERTING FOR WILDFIRE RISK REDUCTION DECISION SUPPORT TOOLS FOR CLIMATE CHANGE ADAPTATION This case study is a new ex post analysis under this making for various objectives. Existing decision project that involves innovative ways to quantify support tools usually take the forms of web based, impacts. software, or customized for specific regions or countries (Ernst & Blaha, 2015).In recent years, there Æ Introduction and background has been an increase in decision support tools for climate change planning and adaptation, which • Decision support tools are based on computers and allows authorities and scientists to make decisions data that are used during the process of decision- that address both short-term risks and long-term Case studies Wildfires 167 effects of climate change. These tools promote Major assumptions and factors include the following: effective and efficient adaptations and resilience to climate changes, allow better decision-making for • Value added to broader economy of Austria for risk reduction, and promote sustainable management forestry from R&D is 10 percent of total forestry in areas such as land and forestry. output based on initial investment. This is the value of information to the economy, which has been • In recent years, web-based decision support tools are found in a simulation by Khabarov, Moltchanova, becoming the most popular and frequently used in and Obersteiner (2008), analysing the benefit of the context of climate change adaptation and information that resulted in avoided costs from communication. To examine the efficiency and forest burns of up to 21 percent (Khabarov, et al., effectiveness of these tools, EU projects like 2008). IMPRESSIONS were launched (European Commission, 2020). These projects enable the • Maintenance cost of the decision support tool is 5 decision makers to see to what extent decision percent of total cost, annually. support tools help them in modelling and dealing with climate change scenarios and their uncertainties and • A 50–90 percent uptake of the tool by private impacts (Lourenço, et al., 2019). owners is gradually realized in the last 10 years of the 30-year horizon. This is an uptake value • When using decision support tools, it is essential to considering the time it would take for a forest to have specific, locally relevant data for the tools to grow and the buy-in of the tool users. produce the most accurate and efficient outcomes. It is also important to consider and analyse the costs • A 1–1.5 percent increase in GDP from forestry in and benefits of such resilience strategies, especially the area is realized within the last 10 years of the for green infrastructures (Ernst & Blaha, 2015). 30-year horizon. This is considering the time it would take for efficient and sustainable forestry to Æ Description grow and for benefits to be realized. This is a conservative estimate. Forest DSS (2013) organizes knowledge about the construction and use of forest DSS for promoting • Discount rate of 3 percent is used. sustainable forest management. The collaborative developed a decision support tool for forestry extension Æ Results of the analysis by dividends services for small-scale private landowners to improve and overall silviculture in southern forest areas in Austria, not only to reduce the impacts of climate change leading to Triple dividend 1 (costs avoided): forest fires in the region but also for efficient and productive ecosystem services from forestry. • Avoided direct and indirect forest fire costs are obtained from the 2020 white paper on forest fires The methodology includes the start-up and assumed in the Alps (Mayer, et al., 2020) maintenance cost of the decision-support tool over the horizon of 30 years and compares to forest fire direct Triple dividend 3 (co-benefits): and indirect costs to the region as well as improved GDP with efficient silviculture. The methodology • The value of improved silviculture that includes an references a study from Ireland that was used to increasing uptake by small forest owners and estimate the overall GDP improvement (Dhubháin, provides more efficient harvests for forestry over 2009) as well as studies on Austria forest management time. This is estimated as a 1.5 percent increase in that were used to estimate the costs and benefits of the last 10 years of the horizon studied (years 20 to the decision support tool (Lexer, et al., 2005). The data 30), after the new growths are ready for harvest. gathered for the cost of the tool and the estimated users were provided by a senior researcher who In the long term, informed decision-making by private developed the decision support tool. forest owners for improved silviculture shows a great benefit compared to the cost of creating the decision Case studies Wildfires 168 support tool (see Table 66 and Table 67). This implies broader economic costs. The higher limit includes that with effective information and communication, greater GDP per year from improved silviculture (up to along with incentives to apply the tool in evaluation of 3 percent based on information on the economy of economic output of silviculture, more fire-resilient Finland showing 3 percent improved harvest per year forests could be created and provide better economic (Wikipedia, 2020)). The low- and high-range BCR is output through forestry. 3.3 and 10.6, respectively, with a median BCR of 5.8, as detailed below. The NPV for the median case is In performing sensitivity analyses for this study, the €994,000, which is positive, indicating that this is a lower bound of BCRs are based on higher annual costs good investment. over time (10 percent of total cost) with no inclusion of Table 66: BCR of climate change adaptation decision support tool in Austria (in 100000 €) BCR: 5.8 BENEFITS (€) COSTS (€) Dividend 1 1.85 Dividend 2 Dividend 3 9.01 Total 10.86 1.88 Source: World Bank analysis based on external data and information Table 67: Expanded triple dividend BCR calculation for the climate change adaptation decision support tool in Austria (in 100000 €) DECISION-SUPPORT TOOL FOR FORESTRY FIRST DIVIDEND (€) Direct and indirect cost of fires avoided 1.85 Total first dividend 1.85 THIRD DIVIDEND (€) GDP increase due to improved silviculture 9.01 Total third dividend 9.01 TOTAL DIVIDEND 10.86 Total cost 1.88 NPV (30-year time horizon) 9.94 BCR 5.8 Source: World Bank analysis based on external data and information Case studies Wildfires 169 Æ Challenges faced and lessons learned increase over time due to improved silviculture must be further researched and validated based on existing Many estimations, assumptions, and simplifications data of this retrospective project. were made for this study, largely because of a lack of data for this project. Because the tool was developed The study could also be enhanced by analysing in 2005, it would be of value to explore the monitoring specifically the economic benefit of improved and evaluation of the forest owners who employed the silviculture can have on the economy, both micro- and tool. The data might be held by the Carinthia macro in the Carinthia region of Austria, which can be government agency that employed the tool. extended to the whole country. More research on the socio-psychological factors and incentives to private It is important to note that without the inclusion of forest owners should be explored to enhance and GDP benefits as part of this study, the BCR would be further specify values for this BCA, which is currently less than 1. This means that the assumptions on GDP conservative. ALERTING AND PREPAREDNESS FOR WILDFIRES IN PORTUGAL This case study is a new ex ante analysis under Æ Description this project that involves innovative ways to quantify impacts. A hypothetical investment for alerting and preparedness along with local fuel management Æ Introduction and background surrounding homes in the Central Region of Portugal is appraised in this case study. The composite costs of As a recurrent hazard in Europe, wildfires cause developing an alerting system, undertaking evacuation fatalities, injuries, and displacements of civilians and planning, as well as localized fuel management near generate great social and economic losses. Therefore, it homes in the greater region (approximately 50,000 is important to provide alerting with emergency planning homes) are compared to the benefits of such and increase preparedness before the actual occurrence interventions to the municipality of Pedrógão Grande. of a fire to reduce its negative impacts. This kind of intervention requires first step planning and preparedness by the government through the Some alerting and monitoring systems have been creation of evacuation plans and alerting systems for created in Europe to improve wildfire prevention and risk the fire-prone region as well as independent fuel reduction. The EFFIS29 developed by JRC is an online management by homeowners as a minimum to geographic system that provides a database of real-time creating defensible space. Pedrógão Grande faced information on fire events in Europe, early warnings, immense damage and loss during the 2017 fire season active fire detections, and damage assessments after and has therefore been selected for analysis using the occurrence of a fire (EFFIS, 2021). Studies for actual loss values. See Wildland-urban interface: hydrometeorological alerting systems have averaged Improvements to homes in Portugal case study for BCR between 5:1 and 10:1 but have seen BCRs of up to more information. 2,500:1. Tiesberg and Weiher (2009) find that examples do not suggest that an overall factor indicates that there The alerting and evacuation would require regional is a great deal of uncertainty about the true (weighted government investment, while fuel management average) ratio of benefits to costs. Therefore, studies could be a combination of private financing and such as the below attempt to enumerate fire alerting government funding or subsidy. These actions present benefits which are considered mostly for life safety and the minimum that would significantly reduce the loss injury avoidance, especially in rapidly spreading fires. of life and the chance for injuries and are therefore focused on in this case study. 29 These examples do not suggest that an overall factor of 5:1 or 10:1 is unreasonable, but they do indicate that there is a great deal of uncertainty about the true (weighted average) ratio of benefits to costs. (Tiesberg and Weiher 2009). Case studies Wildfires 170 Æ Methodology on reducing deaths rather than injuries. On the other hand, it is assumed that life protection measures could Considering the fire risk mitigation activities mainly as save lives but not so much for the occurrence of contributing to reduce the number of causalities, three injuries. For the high hazard cases, it is assumed that scenarios are assessed for fire risk outcomes: extreme, the probabilities are half of extreme hazard. For the very high, or moderate. Based on existing outcomes moderate hazard cases, it is assumed that the from fires in Portugal as well as expert judgement and probabilities are one-sixth of the extreme hazard evaluation, a set of probabilities for casualties are scenario. As mentioned earlier, these values are based determined given the level of implementation of the on expert judgement and study of consequences of following activities: fire hazards in Portugal. The recurrence period for extreme hazard is about 29 years while the return • Fire danger assessment period for very high hazard is about 10 years based on • Alerting historical events. In practice, the most relevant • Evacuation or shelter plans scenario is that of extreme or very high Hazard, as • Fuel management normally in the average hazard condition fatalities are not expected but injuries may be. Table 68 and Table 69 indicate estimated probabilities of injuries and lives lost as a function of fire hazard and In this retrospective study, the benefits are assumed to investment in various DRM activities. The tables are accrue over the period of one year and are not developed based on assessment of the past fires in discounted, whereas the costs are incurred each year Portugal and validated with ex post data on non- and are therefore discounted. existent DRM measures for extreme hazard events in Pedrógão Grande, Mati, and Rafina cities in Greece Expanded DRM activities for wildfire risk reduction are (see Alerting and preparedness in Greece). For all risk described as follows:30 management and risk reduction activities, it is assumed that if no action is taken by the government • Community work: Training community members to and authorities, 20 percent of the people affected will, avoid behaviours that could cause ignition on average, have the capacity to overcome situations • Education and sensibilization: Educating to avoid injuries and mortality. This assessment was community members on fire risk management evaluated in fire events in which the team observed • Fire danger assessment: Daily fire risk assessment that the probability of having fatalities or injured by authorities persons was lower than the estimated maximum value. • Alerting: Informing community when fire activity is This means that more than 20 percent of the persons occurring in the vicinity and actions to take have the capacity to avoid injuries and mortalities • Evacuation and/or shelter plans: Advanced planning without any DRM activities taking place. However, for of evacuation or stay-in-place reasons of conservativism, a value of 20 percent is maintained for people who could successfully protect • House planning: Land use planning to avoid building themselves even without any DRM measures being homes near WUI implemented. • House construction: Building with non-flammable materials and avoiding weak spots in homes The probability for each DRM activity described is • Fuel management: Clearing of fuel around homes based on expert judgement of the impact of the activity • Fire protection: Presence and capacity of firefighter and the relevance in reducing fatalities or injuries in services varying degrees of investment in DRM activities. It is • Life protection: Medical protection, ambulances, considered that the existence of evacuation and and medical support. shelter plans, for example, would have a higher effect 30 Note that these are comprehensive DRM activities for wildfire risk reduction; only four of these activities have been included and analysed in this case study. Case studies Wildfires 171 Considering that all mitigation activities are independent the implementation of the set of activities will be given of each other, the probability of having an accident given by the product of the probabilities of each activity. Table 68: Probabilities of injuries with risk reduction actions taken in moderate to extreme hazard fires Source: World Bank analysis based on external data and information Table 69: Probabilities of fatalities with risk reduction actions taken in moderate to extreme hazard fires Source: World Bank analysis based on external data and information The study estimates the cost of alerting and evacuation Portugal Health Regulatory Authority (INFARMED, planning in the Central Region of Portugal as well as 2020). The cost of alerting has been obtained by private home preparedness through creation of telephone company data interpolated for Pedrógão defensible space and evaluates the benefits of Grande. The cost of fuel management in the Central casualties avoided in the municipality of Pedrógão Region is an average of €300 per home with 50,000 Grande in the extreme hazard case. Pedrógão Grande homes. It is assumed that all homeowners will is approximately one-fifth of the Central Region by undertake fuel management in this case study, but the area. Since alerting would not occur at a city level but reality is that this will be a slow-onset preparedness rather a regional level, the benefits of such a system measure. This is because the quality and quantity of would be larger than what are stated here. Any defensible space created by homeowners surrounding municipality within the Central Region with fire risk their property is not guaranteed if not mandated and would be a potential beneficiary from alerting and could be non-uniform. preparedness. However, since loss estimates are based on Pedrógão Grande from the 2017 fires and for The study looks at a one-year horizon for BCA but sake of this hypothetical investment to be constrained computes the five-year costs of communication to real values as much as possible, the analysts have activities with a 5 percent discount rate. only looked at the triple dividend 1 benefits to Pedrógão Grande. The Triple Dividend Framework includes the following benefits: Costs of injuries to Pedrógão Grande are based on the Case studies Wildfires 172 Triple dividend 1 (costs avoided): Table 70 and Table 71). This can be expected as the costs of alerting are generally much lower than the As this assessment largely evaluates loss of lives and cost of lives lost or injured. Note also that the benefits injuries avoided due to fire danger assessment, are likely underestimated as we are comparing the alerting, evacuation plans, and fuel management, the benefits to the municipality of Pedrógão Grande to the benefits are classified as triple dividend 1. The alerting costs of alerting, evacuation, and fuel management of and evacuation planning does not necessarily intend homes to the Central Region of Portugal. There are not to reduce damage to homes and other assets, as some enough data to quantify unlocked economic potential evacuation plans also encourage sheltering in place if or co-benefits in this case study, but they may exist housing is qualified appropriate to do so. and could be included in future studies. Importantly, the cost of frequent and effective education of alert Æ Results of the analysis by dividends receivers is not included due to data limitations. This and overall would be an added cost of intervention which would reduce the BCR. Overall, however, the BCR would be The benefits are high when comparing the cost of greater than 1 which would make this investment a alerting in the Centro Region of Portugal to the losses positive ROI. avoided from casualties in Pedrógão Grande (see Table 70: BCR calculation of alerting and preparedness for fires in Portugal (in million €) BCR: 11 BENEFITS (€) COSTS (€) Dividend 1 200.29 Dividend 2 Dividend 3 Total 200.29 19 Source: World Bank analysis based on external data and information Table 71: Expanded triple dividend BCR calculation for alerting and preparedness for fires in Portugal (in million €) ALERTING AND PREPAREDNESS FIRST DIVIDEND (€, million) Reduction of lives 198 Reduction of injuries 2.29 Total first dividend 200.29 TOTAL DIVIDEND 200.29 Total cost 19 BCR 11 Source: World Bank analysis based on external data and information Case studies Wildfires 173 Æ Challenges faced and lessons learned that may unlock additional investment in the area (Dividend 2) or co-benefits like awareness of fire risk Future studies should further assess the realizable and tools available to homeowners and residents to benefits of employing any or all of the DRM activities in reduce their risk (Dividend 3), which could be other municipalities in the Centro region. Often, ‘soft’ qualitatively captured in further studies. In addition, investments like capacity building and awareness are frequent, uniform, and effective communication to the understudied but a large factor in emergency and community on understanding alerts and actions to recovery contexts and should be included in future take is essential but was not included in this study due BCA analyses. In general, sparse literature exists on to lack of data. Future studies must consider the the value of awareness for fire and other hazards, and element of education and behaviour related to should be evaluated more thoroughly as often they are receiving and understanding alerting and fuel ‘no regret’ options in risk communication and risk management to fully capture the costs of employing reduction capacity building. There may be other triple this intervention. dividend benefits of alerting, like the sense of safety ALERTING AND PREPAREDNESS IN GREECE This case study is a new ex ante analysis under systems for the fire-prone region as well as independent this project that involves innovative ways to fuel management by homeowners as a minimum to quantify impacts. creating defensible space. Mati and Rafina faced great damage and loss during the 2018 fires in Attica caused Æ Introduction and background by heatwave and have therefore been selected for analysis using actual loss values. In 2018, the seaside village of Mati in the Attica region of Greece faced fires that caused tremendous loss to life The alerting and evacuation would require regional and property. These fires were considered the second- government investment, while the fuel management deadliest event in the 21st century. Over 700 residents could be a combination of private financing and were evacuated or rescued. Over 100 people lost their government funding or subsidy. These actions present lives and more than 1,000 buildings were damaged or the minimum that would significantly reduce the loss destroyed (BBC, 2018). While multiple factors led to the of life and the chance for injuries and are therefore outcome of this event, this case study aims to focused on in this case study. enumerate potential benefits from fire alerting, emergency planning, and basic fuel management by Æ Methodology homeowners to their properties, which are considered primary mitigation and preparedness measures for life Considering the above fire risk mitigation activities safety and injury avoidance, especially in rapidly mainly as contributing to reduce the number of spreading fires like in Mati. causalities, three scenarios are assessed for fire risk outcomes: extreme, very high, or moderate. Based on Æ Description existing outcomes from fires in Greece as well as expert judgement and evaluation, a set of probabilities for A hypothetical investment for alerting and casualties are determined given the level of preparedness along with fuel management in the implementation of the following activities undertaken: Attica region of Greece is appraised in this case study. The composite costs of developing an alerting system, • Fire danger assessment undertaking evacuation planning, as well as localized • Alert fuel management near homes in the villages of Mati • Evacuation or shelter plans and Rafina (approximately 20,000 homes) are • Fuel management compared to the benefits of such interventions to the Attica region. This kind of intervention requires first Table 72 and Table 73 include estimated probabilities step planning and preparedness by the government of injuries and lives lost as a function of fire hazard and through the creation of evacuation plans and alerting investment in various DRM activities. The tables are Case studies Wildfires 174 developed based on assessment of the past fires in In this retrospective study, the benefits are assumed to Portugal and validated with ex post data on non- accrue over the time period of one year and are not existent DRM measures for extreme hazard events in discounted, whereas the costs are incurred each year Pedrógão Grande, Mati, and Rafina. For all risk and are therefore discounted. management and risk reduction activities, it is assumed that if no action is taken by the government Expanded DRM activities for wildfire risk reduction are and authorities, 20 percent of the people affected will, described as follows:31 on average, have the capacity to overcome situations to avoid injuries and mortality. This assessment was 1. Community work: Training community members evaluated in fire events in which the team observed to avoid behaviours that could cause ignition that the probability of having fatalities or injured persons was lower than the estimated maximum value. 2. Education and sensibilization: Educating This means that more than 20 percent of the persons community members on fire risk management have the capacity to avoid injuries and mortalities without any DRM activities taking place. However, for 3. Fire danger assessment: Daily fire risk assessment reasons of conservativism, a value of 20 percent is by authorities maintained for people who could successfully protect themselves even without any DRM measures being 4. Alerting: Informing community when fire activity implemented. is occurring in the vicinity and actions to take The probability for each DRM activity described is 5. Evacuation and/or shelter plans: Advanced based on expert judgement of the impact of the activity planning of evacuation or stay-in-place and the relevance in reducing fatalities or injuries in varying degrees of investment in DRM activities. It is 6. House planning: Land use planning to avoid considered that the existence of evacuation and building homes near WUI shelter plans, for example, would have a higher effect on reducing deaths rather than injuries. On the other 7. House construction: Building with non-flammable hand, it is assumed that life protection measures could materials and avoiding weak spots in home save lives but not so much for the occurrence of injuries. For the high hazard cases, it is assumed that 8. Fuel management: Clearing of fuel around homes the probabilities are half of extreme hazard. For the moderate hazard cases, it is assumed that the 9. Fire protection: Presence and capacity of probabilities are one-sixth of the Extreme Hazard firefighter services scenario. As mentioned earlier, these values are based on expert judgement and study of consequences of 10. Life protection: Medical protection, ambulances, fire hazards in Portugal. The recurrence period for and medical support. Extreme Hazard is about 29 years while the return period for very high hazard is about 10 years based on Considering that all mitigation activities are historical events. In practice, the most relevant independent of each other, the probability of having an scenario is that of extreme or very high hazard, as accident given the implementation of the set of normally in the average hazard condition fatalities are activities will be given by the product of the probabilities not expected but injuries may be. of each activity. 31 Note that these are comprehensive DRM activities for wildfire risk reduction; only four of these activities have been included and analysed in this case study. Case studies Wildfires 175 Table 72: Probabilities of injuries with risk reduction actions taken in moderate to extreme hazard fires Source: World Bank analysis based on external data and information Table 73: Probabilities of fatalities with risk reduction actions taken in moderate to extreme hazard fires Source: World Bank analysis based on external data and information The study estimates the cost of alerting in the Attica population of Greece (2019 Eurostat), and the region of Greece and evaluates the benefits of estimated €2 million for the case study is casualties avoided in villages of Mati and Rafina. approximately 40 percent of the budget line item. These villages are approximately one-third of the Therefore, it is reasonable to estimate a cost of €2 Attica region by area. Since alerting would not occur million including maintenance costs for alerting and at a city level but rather a regional level, the benefits evacuation in the Attica region. Sensitivity analysis of of such a system would be larger than what are stated the costs between €1 million and €5 million yields here. Any municipality within the Attica region with similar BCRs. fire risk would be a potential benefactor from alerting and preparedness. However, since loss estimates are Costs of injuries in Mati are obtained with data from based on the 2018 fires and for sake of this consultations with Greek fire specialists and on the hypothetical investment to be constrained to real ground estimations following deployments to Greece. values as much as possible, the analysts have only Costs included are compensation for the deceased looked at the triple dividend 1 benefits to Mati and and injured, along with emergency health costs.[1] Rafina. The cost of alerting and development of The cost of alerting has been estimated as €250,000 evacuation plans in the region of Attica is estimated per year based on the calculations made for Portugal, to be €2 million, including €1 million for maintenance assuming similar costs for the regions affected that for five years. Information from the Greece Civil have areas of similar size. The cost of fuel management Protection Agency has apportioned €5 million for a in the Attica region is an average of €300 per home national-level multi-hazard forest monitoring and with 20,000 homes. The same cost in relation to that EWS (fires, floods, landslides, and so on) with a fire of Portugal was adopted to estimate the cost of fuel detection and alerting via SMS to surveillance centres management per house in the Attica region. It is and eventually to vulnerable populations. The Attica assumed that all homeowners will undertake fuel region is approximately 35 percent of the total management in this case study, but the reality is that Case studies Wildfires 176 this will be a slow-onset preparedness measure. This Æ Results of the analysis by dividends is because the quality and quantity of defensible and overall space created by homeowners surrounding their property is not guaranteed if not mandated and could The benefits are high when comparing the cost of be non-uniform. alerting in the Attica region of Greece to the losses avoided from casualties in Mati and Rafina (see The study looks at a one-year horizon for BCA but Table 74 and Table 75). This can be expected as computes the five-year costs of communication the costs of alerting are generally much lower than activities with a 5 percent discount rate. the cost of lives lost or injured. In this tragic event, many lives were lost than could have been The Triple Dividend Framework includes the following expected given the fire hazard, resulting in a large benefits: BCR. Note again that the benefits are likely underestimated as we are comparing the benefits Triple dividend 1 (costs avoided): to the villages of Mati and Rafina to the costs of alerting, evacuation, and fuel management of • As this assessment largely evaluates loss of lives homes to the Attica region of Greece. There are not and costs borne from casualties avoided due to enough data to quantify unlocked economic alerting, evacuation plans, and fuel management, potential or co-benefits in this case study. However, the benefits are classified as triple dividend 1. The they may exist and could be included in future alerting and evacuation planning does not studies. Importantly, the cost of frequent and necessarily intend to reduce damage to homes effective education of alert receivers is not included and other assets, as some evacuation plans also due to data limitations. This would be an added encourage sheltering in place if housing is qualified cost of intervention which would reduce the BCR. appropriate to do so. Overall, however, the BCR would be greater than 1 which would make this investment a positive ROI. Table 74: BCR calculation of alerting and preparedness for fires in Greece (in million €) BCR: 39.3 BENEFITS (€) COSTS (€) Dividend 1 314.04 Dividend 2 Dividend 3 Total 314.04 8 Source: World Bank analysis based on external data and information Table 75: Expanded triple dividend BCR calculation of alerting and preparedness in Greece (in million €) ALERTING AND PREPAREDNESS FIRST DIVIDEND (€) Reduction of lives 312 Compensation for the deceased 0.52 Compensation for the injured 0.09 Emergency health costs 1.43 Total first dividend 314.04 TOTAL DIVIDEND 314.04 Total cost 8 BCR 39.3 Source: World Bank analysis based on external data and information Case studies Wildfires 177 Æ Challenges faced and lessons learned unlock additional investment in the area (dividend 2) or co-benefits like awareness of fire risk and tools The high BCR is mainly due to the tragic events of the available to homeowners and residents to reduce 2018 Mati fires, considered the second-deadliest fire their risk (dividend 3), which could be qualitatively in the 21st century and upon which this scenario is captured in further studies. In addition, frequent, based. For a relatively small population affected in uniform, and effective communication to the Greece, a large number of injuries and high number of community on understanding alerts and actions to fatalities created one of the worst fire disasters in the take is essential but was not included in this study due country that was extremely politicized and sensitive for to lack of data. Future studies must consider the the Greek population. The BCRs for both Greece and element of education and behaviour related to Portugal exemplify the opportunity to save lives with receiving and understanding alerting and fuel relatively low-cost investments in alerting and management to fully capture the costs of employing evacuation planning. this intervention. Future studies should further assess the realizable 3.5.5. CROSS-BORDER SUPPORT, benefits of employing any or all of the DRM activities in COORDINATION MECHANISMS, other municipalities in the Attica region. Often, ‘soft’ AND CAPACITY BUILDING FOR investments like capacity building and awareness are WILDFIRES understudied but a large factor in emergency and recovery contexts and should be included in future The following analysis will focus on a specific BCAs. In general, sparse literature exists on the value investment SPITFIRE in Portugal as a hypothetical of awareness for fire and other hazards and should be investment, but numerous other investments have evaluated more thoroughly as often they are ‘no-regret’ been undertaken in capacity building for wildfire options in risk communication and risk reduction prevention in countries such as in the Czech Republic, capacity building. There may be other triple dividend Poland, or Spain. benefits of alerting, like the sense of safety that may CROSS-BORDER SUPPORT AND COORDINATION MECHANISMS FOR WILDFIRES This case study is a new ex ante analysis under 2020). The project aims at increasing cooperation this project that involves innovative ways to among nations so that resources such as rescuing quantify impacts. equipment and tools can be shared and utilized efficiently if disasters such as a large-scale fire occur. Æ Introduction and background The Federation of European Union Fire Officer Associations also offers a proposal (FEU Fire Officer Disasters and hazards are not bound by the borders of Associations, 2020) that encourages European countries. The impacts of disasters are consistent countries to increase communications and throughout Europe and generate negative social and collaborations, enhance shared legislative frameworks economic consequences for all countries affected. In in terms of infrastructure and community safety, and this context, it is essential for European countries to improve rescue equipment as well as the security and work collaboratively and share their resources and safety of firefighters. These efforts ensure the safety of good practices when a disaster strikes, especially in European citizens and reduce damages and economic cross-border areas that are vulnerable to disasters costs due to the occurrences of fires. such as forest fire and floods. When doing an economic analysis of cross-border Several EU projects have been launched to enhance services and coordination mechanisms, one must fully cooperation across borders in terms of responses to address the needs and demands as well as the cost disasters and emergencies. INTER’RED is an ongoing and benefits of such services. This is suggested by a project that improves rescue services in the cross- study (Tinholt, et al., 2013) for the European border Grande Région, which covers Luxembourg, Commission DG Communications Networks, Content, France, Germany and Belgium (European Commission, and Technology, which also indicates that Case studies Wildfires 178 interoperability is an essential factor that needs to be enhanced coordination and cooperation facilitated by considered. SPITFIRE. This is from anecdotal evidence by the principal investigator of the project receiving positive Æ Description responses from emergency services about the utility of the tool. It also provides conservativism as little data SPITFIRE is a project that was partially co-funded by exist in terms of cross-border fire consequence the European Commission (European Commission, reconciliation. Since there was no continued funding 2017). The main objective of this project was the in the platform, the life span of the tool was just over a improvement of information exchange on meteorology year, so only a one-year estimation of the BCA was and forest fire risk in the border area between Portugal undertaken. and Spain through the identification, design, and implementation of data interchange protocols and the Many relevant studies were considered for the development of a cross-border service on weather and evaluation of the BCA. Research shows that sparse fire-risk forecast (SPITFIRE platform). The tool offers literature is available in terms of overall benefits that a high-resolution meteorological and forest weather decision support or emergency coordination tool can forecasts. The information is presented in a GIS provide during its lifetime of utility. environment, to allow its joint management with other information used daily by users of the service like fire The cost of the tool was provided by the project managers and firefighters. Information presented manager and developer of SPITFIRE. The losses includes protected spaces, surveillance posts, roads, avoided (direct and indirect forest fire losses) were water points, distribution of material and human estimated from an existing report on the 2017 fires resources, and so on). The tool is not only applied in (Comissao Tecnica Independente, 2017). Direct costs cases of urgent response but also in planning and are losses from burned areas (forests and shrublands). preparation activities. Consequently, not only the The direct costs were obtained from data provided by firefighters but the entire fire management structure the Portuguese Institute for Nature and Forest benefit. Besides the immediate positive effects of the Conservation and by the Polytechnic University of tool for Portugal and Spain, this approach can be Valencia (ICNF, 2017; Gomez, 2014). Indirect costs replicated to other cross-border regions in Europe are related to fire prevention, firefighting, recovery, which are at high risk and suffer greatly from forest fire. and losses in services and goods due to the fire. Indirect costs were calculated through a ratio between This case study evaluates the cost of developing a direct and indirect costs based on a report providing cross-border information tool for emergency fire historical data on wildfire costs. The direct and indirect services and firefighters at the Portugal-Spain border costs were scaled to the cross-border area covered by and the estimated losses avoided from improved the SPITFIRE project. information and coordination of countries and agencies. Due to the limited data on expanded benefits, this study estimates the costs of forest fire management Æ Methodology and suppression in the cross-border regions of Spain and Portugal. The methodology considers the cost of creating the SPITFIRE tool by the consortium coordinated by ADAI Triple dividend 1 (costs avoided): at the University of Coimbra in Portugal32 and the avoided direct and indirect losses from forest fires. The Based on actual annual costs to Portugal and Spain, study is focused on triple dividend 1 losses avoided in the ratio of cross-border forests to total forests in the the cross-border region of Spain and Portugal. The respective countries to determine scaled costs of major assumption in this study is that only 0.5 percent forest fires. of direct and indirect fire losses would be avoided with 32 Note that four other partner organizations supported development of the tool, with coordination from ADAI. Only the costs from ADAI are considered in this case study. Case studies Wildfires 179 Æ Results of the analysis by dividends focused on the first dividend of direct and indirect and overall costs avoided, the full benefits are likely underestimated as dividends 2 and 3 could not be The overall BCR is greater than 1 over the period of a included due to lack of data. year in which this evaluation is considered (see Table 76 and Table 77). The direct and indirect costs In addition, the costs of the SPITFIRE platform tend to of fire damage losses avoided considering a be diluted over time, while the benefits tend to conservative value of penetration and utility of tool increase. Thus, one would expect that a longer still offers a high benefit compared to the cost and platform lifetime should drive to a much more maintenance of the tool. While the assessment significant BCR. Table 76: BCR calculation of the SPITFIRE project (in million €) BCR: 1.6 BENEFITS (€) COSTS (€) Dividend 1 1.15 Dividend 2 Dividend 3 Total 1.15 0.7 Source: World Bank analysis based on external data and information Table 77: Expanded triple dividend BCR calculation for the SPITFIRE project (in million €) CROSS-BORDER COORDINATION FIRST DIVIDEND (€) Direct costs of forest fires avoided, Spain 0.06 Indirect costs of forest fires avoided, Spain 0.08 Direct costs of forest fires avoided, Portugal 0.44 Indirect costs of forest fires avoided, Portugal 0.57 Total first dividend 1.15 TOTAL DIVIDEND 1.15 Total cost 0.7 BCR 1.6 Source: World Bank analysis based on external data and information Case studies Wildfires 180 Æ Challenges faced and lessons learned decision support tools with a longer lifetime than the SPITFIRE platform is evident in this case study. Lack of data for this particular case and lack of research generally on the topic of cross-border CAPACITY BUILDING FOR WILDFIRE PREVENTION collaboration for fire suppression and emergency services limited the opportunity to expand to a triple In addition to coordination mechanisms, a number of dividend analysis. Future studies should investigate initiatives have aimed to enhance capacity and the actual deployments, fire response rates, enhanced provide training for enhanced preparedness of coordination, and improved containment afforded by populations and emergency response units across the platform. In addition, more research and evaluation Europe. These initiatives, in combination with EWS, on the benefits to the entire fire service structure aim to shorten response times and ensure that should be explored. This type of study could greatly effective disaster response can be support with inform other such information platforms, especially in human and material resources. A number of initiatives cross-border areas where cooperation between fire are presented in Box 11 below. services is critical. Moreover, the advantage of having Box 11: Investments in capacity for enhanced wildfire response across Europe A review of investments in capacity building for wildfire countries’ emergency response service providers. This prevention and response across Europe provided several helps to ensure that there is cohesion between the different lessons learned and inspiring achievements outlined below. countries during fires, floods, and other disasters, especially A common theme is that a combination of equipment, given the possibility for these to occur more frequently due coordinated trainings and peer learning as well as centres to to climate change. combine human resources to address a number of different disasters, including fires, seem to ensure the greatest The EU supported the establishment of a defence centre benefits in terms of effectiveness of response during against forest fires in Andalusia, Spain (European disasters. Commission, 2016b), a region with high fire risk. This centre now covers 11 municipalities and 150,000 residents and In the Czech Republic, wildfires caused 155 injuries and 12 has resulted in improved equipment and cooperation in fatalities for the past decade (Velinger, 2015) and economic projects that improve forest management, training, and costs could be substantial given that 34 percent of the awareness raising. Moreover, the Interreg España-Portugal country is covered by forests (Baranovskiy, 2019). An EU- project (Interreg España-Portugal, 2019) represents financed project of €58 million total investment (€50 million collaboration between the cross-border regions of Spain financed by the EU) from 2007 to 2013, “Fire and rescue and Portugal, along with over 15 institutions, through services receive major investments in equipment”, aimed at exchanges of knowledge and good practices. Both Spain enhancing the capacity of the Fire Services so it can also and Portugal are highly vulnerable to wildlife hazards, and engage in overlapping activities for flooding situations – there is a long history of institutions fighting forest fires intervention management, rescue operations, emergency along the cross-border area. Therefore, the implement of survival for the population, and salvage operations – the project leads to effective training and execution of identically throughout all of the country’s regions. infrastructures and technological innovation for the extinction and prevention of forest fires. One result of the Moreover, a project Safe Borderlands aimed to strengthen project is the establishment of the “Iberian Centre for the cooperation between fire and rescue services or other Research and Fight Against Forest Fires” (CLIFO), which emergency response units (police, medical rescue, public aims to serve as a regional and international benchmark in health authorities, and so on) on the shared border of Czech the fight against forest fires, increase response capacity to Republic and Poland with more than 7 million inhabitants forest fires, and reduce the economic cost of fires. While it (European Union, 2020). Firefighters and other emergency may be difficult to measure the impacts of this investment response personnel hold organized conferences and using a BCA, it’s important to reference qualitatively trainings, take language-learning courses, purchase special because this case study exemplifies the impacts of equipment, and exchange data with each other in order to improving capacity. maintain smooth lines of communication between the two Case studies Wildfires 181 3.6. Mass movement / landslides 3.6.1. SUMMARY OF FINDINGS FOR MASS of landslide prevention efforts against the cost of post- MOVEMENT (LANDSLIDES) event emergency actions. They found that it was more economically convenient to carry out a drainage trench, Investments in landslide risk reduction can take a form of water removal intervention, to improve slope various forms, such as engineered and natural slope stability before the landslide event, and if this was done, stabilization, control of flooding or run-off that there would be a savings of 30 percent in relation to the destabilizes slopes, and debris capture or diversion. remedial works’ total costs (Salbego, et al., 2015a). Engineered retaining structures may include gabion walls, reinforced concrete wall, and retention nets. In this section, we have presented benefit-cost Modification of slope geometry may be achieved by assessments for interventions for landslide prevention introducing a stepped-slope embankment. Internal through enhancing the resilience of roads, land use slope reinforcement requires rock bolts, micro piles, planning investments (for example, drainage trench), soil nailing, and grouting. Drainage can be improved, and information and cooperation systems (for example, or slopes can be re-vegetated to provide soil stability. meteorological forecasting system). Benefits for the different types of interventions are presented, including Investing in landslide prevention is socio-economically a World Bank ex-ante quantitative analysis, past beneficial because it is far cheaper to implement benefit-cost analysis undertaken in Europe, and proactive remedial investments versus undertaking an qualitative reviews of existing EU projects. The array of reactive projects in response to a landslide landslide risk in most case studies is earth or debris disaster. For example, after torrential rain provoked a flow resulting from erosion or heavy rainfalls. The risk landslide in the northeastern Italian pre-Alps, researchers of avalanches is also considered in some of the at the University of Padova conducted a series of examples. Table 78 summarizes main data and quantitative modelling to compare the economic benefits information sources. Table 78: Overview of data and information sources for mass movement / landslides analysis INVESTMENT CASE STUDY DATA SOURCE NAME AND REFERENCE Preventive investments in Resilient road assets in Albania World Bank ex-ante report Climate Resilient the resilience of roads Road Assets in Albania Source: World Bank based on external data and information Models need to be adapted to type of investment. adaptation, assessment consists of both risk analysis BCAs are effective when examining traditional and mitigation measures and BCA is necessary to fully landslide management and remediation approaches present its benefit in both climate and seismic and can help identify the most cost-effective measure improvements. in terms of landslide risk reduction. However, for landslide prevention investments with climate change BCRs can be used to reflect the cost-effectiveness of Case studies Mass movement / landslides 182 investments in landslides preventions and prove that seem to be quite effective. Although BCRs found were these preventive investments with relatively low costs small or close to 1, societal benefits may have been can have considerable net benefits. Therefore, it is underestimated, and this could also explain why considered socio-economically beneficial to invest in landslide preventive investments are often undertaken landslide prevention as it is far cheaper to implement in combination with flood preventive investments to proactive remedial investments versus undertaking an ensure efficiency of interventions. More details are array of reactive projects in response to a landslide included in Figure 37. disaster. Figure 37 presents a boxplot that displays the Results of the BCA indicate possible benefits from distribution of BCRs for investments in landslides preventive investments. Prioritization of infrastructure based on a five-number summary: minimum (shown in such as roads assets seems to be crucial for those to orange), first quartile, median (shown in red), third arise, but low-cost land management solutions also quartile, and maximum (shown in orange). Figure 37: Findings CA for mass movement/landslides (BCRs) Source: World Bank analysis based on external data and information; presenting results from literature based on external reports (1 preventive investments in the resilience of roads result from (Xiong & Alegre, 2019) One example of a preventive investment against technical expertise on road resilience of the country landslides is upgrading infrastructure to enhance the and promote the resilient transport agenda on a resilience of roads. Enhancing the resilience of roads is national and global scale. viewed as a crucial way to reduce the impact of landslides on the transportation network, as landslides • Case study 25 (World Bank analysis (Xiong & can cause severe damage to roads and highways that Alegre, 2019), ex ante): The analysis of im- can be either direct (a road or part of a road being plementing retrofitting landslide risk mitigation destroyed) or indirect (closure or traffic restriction in measures on the road network in Albania yielded the affected area) (Bordoni, et al., 2018). Projects positive net benefits only for one section. It would have been launched in the EU to enhance resilience of be important to do the analysis if preventive roads against landslides. A World Bank project (World measures had been implemented, that is, integrated Bank, 2020c) in Serbia has made accomplishment in into the design of roads, as this may potentially have terms of improving the physical infrastructure and yielded higher net benefits for more road sections. Case studies Mass movement / landslides 183 3.6.2. PREVENTIVE INVESTMENTS IN THE indirect consequential economic impacts on the RESILIENCE OF ROADS nearby area and its transport-dependent activities. The study examines four Scottish landslide events and Landslides cause severe damage to roads and presents the huge economic losses associated with highways, which can be either direct (a road or part of these events: the direct repairmen of the infrastructure a road being destroyed) or indirect (closure or traffic costs between €295,000 and €1,253,000, while direct restriction in the affected area) (Bordoni, et al., 2018). consequential costs in the transportation sector range Such damage disturbs the transportation network and from €133,000 to €1,032,000. negatively affects the safety of vehicles and passengers. Enhancing the resilience of roads is viewed as a crucial Economic assessments have been undertaken to way to reduce the impact of landslides on the examine and quantify the socio-economic impact of transportation network. In Serbia, a World Bank project landslides on the road network. A study (Winter, et al., (World Bank, 2020c) was launched with the goal of 2016) conducted in Scotland divides such impacts increasing resilience against landslides and other into three categories: (1) direct economic impacts climate risks in the country’s roads and transportation resulted from clean-up and repairmen costs of the sector. The project is designed to improve physical damaged infrastructure, (2) direct consequential infrastructure and technical expertise on road economic impacts due to disturbance or decreased resilience and promote the resilient transport agenda efficiency in the transportation network, and (3) at a national and a global scale. RESILIENT ROAD ASSETS IN ALBANIA – PROTECTION AGAINST LANDSLIDES This case study is an external analysis that was Roads are crucial to the functioning of any society, and undertaken with ex ante quantitative for transportation plays a vital role in building climate- prioritization of interventions resilient communities. With roads being unavailable and/or unreliable, Albania will experience significant Æ Introduction and background negative effects to their economic growth. Already, natural hazards pose a great risk to the roads and the Albania is the most threatened country in Europe from roads’ users, and therefore it is important to understand multiple hazards (Xiong & Alegre, 2019), being prone how hydro-meteorological and geological hazards to a flurry of hydro-meteorological hazards (for affect the national road network of Albania. This will example, floods, drought, heavy snowfalls, and extreme enable the country to build roads that are able to temperatures) and geological hazards (that is, weather the coming effects of climate change, further earthquakes and landslides). About 88.5 percent of helping Albania achieve sustainable, economic growth generated GDP, 86.4 percent of the total area, and (see also Figure 50 in Annex 3). 88.6 percent of the population are exposed to two or more types of hazards. The results of a major natural Æ Description hazard can have catastrophic consequences. In December 2017, a major flood event in Albania caused The main objective of this prospective study is to assist 1,575 people to be evacuated, 3,500 houses to flood, Albanian stakeholders in the prioritization of current 65 bridges to collapse, 56 public schools to be and future climate and seismic resilient investments damaged, and 15,000 ha of land to submerge (Xiong & in road assets. The road network under consideration Alegre, 2019). With the possibility of climate change for this study (see Figure 38) encompasses 1,494 km leading to more intense and more frequent natural of roads - 1,370 km are primary roads with some hazards in the future, coupled with Albania’s risks for extensions to the remaining secondary roads on river flooding (that is, fluvial flooding), coastal flooding, request of the Albanian Road Authority (ARA). landslides, and earthquakes already rated high, there Researchers analysed the value of roads, bridges, has been more attention shifted to investigating the culverts, and tunnels. While the potential effects of possibilities for DRM in Albania and the broader flooding (both pluvial and coastal) and seismic events Western Balkan area. were examined, for the scope of this case study, we will primarily focus on how landslides, specifically Case studies Mass movement / landslides 184 precipitation and seismic-induced landslides, affect five Albanian road corridors: 01 Milot - Morine New; 05 roads in the primary road network. During this project, Durres – Vlore; 06 Tirana - Elbasan – Pogradec; 13 a BCA on landslide measures was implemented for Milot - Peshkopi; and 14 Vlore - Sarande. Figure 38: Map showing the primary network under consideration of this project Source: Xiong & Alegre, (2019) Note: The colours indicate the various corridors within the primary road network. Æ Methodology Retrofitting mitigation measures to protect against landslides come at a relatively high cost compared to To achieve the case study’s objective, a climate and their effectiveness levels, but there are economic and seismic vulnerability assessment was applied to the social impact reasons as to why these measures are Albanian national road network and mitigation essential (see Table 79). In high-volume road sections, measures to improve climate and seismic resilience of such as Corridor 5 Durres to Vlore and Corridor 6 national roads were proposed to stakeholders. Thus, Tirana to Pogradec, these mitigation measures the project can be divided into two parts: risk analysis become economically viable. Implementing stabilizing and mitigation measures and BCA. There were 13 measures in these areas, such as retaining walls, actions taken among the two parts that were illustrated gabions, and soil nailing, would cost €13.8 million. Yet, in a flowchart (see Annex 4). mitigation measures are still necessary in low-volume road sections because villages may become isolated Æ Results of the analysis by Dividends from the outside world without intervention. The and overall benefits reported would all be considered dividend 1 in the Triple Dividend Framework. Case studies Mass movement / landslides 185 Table 79: BCR for landslide measures implemented by corridor CORRIDOR INVESTMENT (€, MILLIONS) BENEFITS (€, MILLIONS) BCR 01 Milot - Morine New 15.0 4.2 0.3 05 Durres - Vlore 6.3 6.7 1.1 06 Tirana - Elbasan - Pogradec 7.4 6.0 0.8 13 Milot - Peshkopi 32.1 2.6 0.1 14 Vlore - Sarande 11.0 2.3 0.2 Source: Xiong & Alegre (2019) The analysis yields a BCR ranging between 0.1 and who use that roadway. Also, it is still important to 1.1. For the road corridor between Durres and Vlore implement these measures for roads with a lower (05), there was evidence that the protective landslide volume of users, even if it is not as economically measures were economically beneficial (that is, beneficial because the demolition of this stretch of BCR >1) over a period of 25 years with a net discount roadway could physically and socially disconnect a rate of 4 percent. Per 10 m of road, it costs €11 specific area from the rest of country. thousand for retaining walls, €14 thousand for shotcrete and drainage, €42 thousand for steeped- 3.6.3. LAND USE PLANNING INVESTMENTS slope embankment, and €121 thousand for rock anchors and wire mesh. While the BCRs of the other Implementing prevention and preparedness measures corridors was under 1, protective landslide measures during land use planning is considered as a crucial are still socially important because regions of the way to reduce the negative impact of landslides. Many country can become disconnected and isolated in naturally occurred landslides are recurrent and thus case of a landslide disaster. can be easily observed or forecasted by experts. Therefore, preventive measures can be implemented Æ Challenges faced and lessons learned in the areas at risk after their geological and land use characteristics as well as the type and location of The analysis of implementing retrofitting landslide risk landslide that may potentially occur have been mitigation measures on the road network in Albania carefully identified. Such measures can be effective in yielded positive net benefits only for one section. It terms of avoiding human and economic losses. In would be important to do the analysis if preventive 2000, the Stoze landslide and the Predelica torrent measures had been implemented, that is, integrated debris flow of Slovenia caused seven deaths and an into the design of roads, as this may potentially have economic loss of €36 million. Lessons learned from yielded higher net benefits for more road sections. For the event suggest a need for reviewing Slovenia’s land this study’s BCA, a number of measures, including use plans and adopting hazard zoning as the best preventative measures, reforestation of slopes, erosion prevention measure for future landslide risk reduction protection, and more, were not taken into account due (JRC, 2003). to a lack of information and/or a lack of the required information to determine the amount of the measure BCAs have been undertaken to examine the needed. However, these measures should be further effectiveness of several European investments in investigated, especially when examining the road landslide prevention and remediation and identify the profiles, geomorphological conditions of the areas most cost-effective measure in terms of landslide risk adjacent to the road, and specific characteristics of reduction. Outcomes and inspirations from two studies the catchment areas draining to road assets, such as include a BCA of landslide management approaches culverts and bridges. Given the connectivity of Albania’s in Vicenza, Italy and an economic analysis of avalanche road system, applying landslide mitigation measures to risk reduction interventions in Switzerland are even one segment of road would have a distributional showcased in Box 12 below. effect because it will benefit both the people who live in that community and others outside of that community Case studies Mass movement / landslides 186 Box 12: Cost-effectiveness of landslide prevention vs. response investments A number of studies have analysed the cost-effectiveness of years would have saved 30 percent of the remediation cost, landslides prevention investments compared to remediation leading to a benefit of €17 thousand (Salbego, et al., 2015). investments or also other types of investments. These studies show that some low cost interventions can have As a country in the Alpine region, Switzerland is highly considerable net benefits and therefore provide arguments vulnerable to avalanches and landslides due to climate for enhanced investments in prevention for these disasters. change and other factors, such as geology and rainfall In the case of the Italy case study, the authors also provide persistence (Climate Change Post, 2020). Since 1936, 24 methodologies that can be utilized for local governments to people on average have died in avalanches annually (WSL assess the net benefits of preventive vs. remediation Institute for Snow and Avalanche Research SLF, 2020). In investments without having to undertake a full probabilistic/ this context, Several cost-effectiveness analysis on landslide risk-based assessment. prevention have been conducted, with the best interventions in terms of net benefits being identified. In Davos, an A study on the cost-benefit of landslide management economic analysis was carried out for different mainstream approaches was conducted at detailed-scale and large- interventions that attempt to reduce the risk of avalanches scale for a case of rotational/translational slides and earth in Switzerland, such as technical, organizational, and land flows that occurred in Vicenza, Veneto Region, Italy in 2010 use planning measures (Fuchs, et al., 2007). The study (Salbego, et al., 2015a). A detailed numerical model found shows that the most cost-effective risk reduction measures that incorporating a drainage trench (aiming to reduce the are interventions with snow fences and land use planning, in water table, therefore slope instability) prior to 2010 would terms of direct costs - though for avalanche mitigation the have been effective in preventing the landslide. BCA showed scale of benefit is highly dependent on the amount of snow that compared to €57 thousand in remediation costs, fences deployed. installing a drainage channel and maintaining it over 20 3.6.4. INFORMATION AND COOPERATION Bulgarian project “riverbanks and seashores protection SYSTEMS FOR LANDSLIDE from water abrasion and erosion and from the landslide PREVENTION processes resulted from them” with the British Information sharing and cooperation between nations engineering company “Atkins” as the advisor. Such play an essential role in terms of improving the efforts allow these countries to adopt innovative effectiveness and efficiency of landslide prevention. measures for landslide prevention and mitigation that are International cooperation enables EU members to share both effective and cost-efficient (JRC, 2003). There are knowledge and expertise on landslide prevention, which several examples of European Commission funding allows them to plan, set up, and improve anti-landslide aimed at managing the impacts of slope instability. activities within nations and across borders. Some Although no assessment of benefits could be obtained countries have launched landslide prevention projects to compare against project costs, the investments with guidance and support from international experts presented in more detail in below can provide interesting and companies specializing in the field, such as the insights (see Box 13 below). Case studies Mass movement / landslides 187 Box 13: Investments in information systems and cooperation mechanisms for landslide prevention A review of investments in information systems and Pyrenees. PyrMove addresses: 1) Large landslides involving cooperation mechanisms across Europe provided several complete slopes that can include towns, infrastructures and lessons learned and inspiring achievements outlined below. activities on their surface and that are susceptible to A common theme is that alongside information and accelerate and end into catastrophic failures; 2) Multiple forecasting systems, all the projects also supported landslides caused by episodes of intense rainfalls that equipment and investments in road conditions to protect simultaneously affect large areas of the territory (MORLEs assets. crisis). It seeks to better assess, forecast and manage these risks, presently hindered by a lack of knowledge on the On the French-Spain border, a project co-financed by the temporal and spatial occurrence and their evolution, and EU supported enhanced preparedness. Co-financed by the aims to install alerts systems and scenarios simulators for ERDF, the SECURUS project (Bielsa-aragnouet, 2018) Civil Protection activities. ‘Safety from natural risks on the Bielsa-Aragnouet and Espacio Portalet road links’ on the France-Spain border Co-financed by Interreg, the main objective of the cross- (budget €4.22 million) combines investment in information border project safEarth (European Commission, 2019) is to sharing on road conditions and technical support for identify areas vulnerable to landslide hazards in parts of improved local meteorological forecasting, with Croatia, Bosnia and Herzegovina and Montenegro. The goal implementing measures to protect roads from landslide and is accomplished through the development of by an online erosion risk. landslide susceptibility mapping (LSM) system, which enables the mapping of any potential or ongoing disasters in Another project supported mapping and forecasting of real time, and development of guidelines for susceptibility landslides in the Pyrenees in France. Also 65 percent co- mapping. As a part of the project, rehabilitation of financed by ERDF, PyrMove (Institut Cartogràfic i Geològic infrastructures and equipment in reducing landslide risks de Catalunya, 2020) focuses on the prevention and have also been undertaken to decrease the negative impact management of risks associated with landslides, that cause of landslides in the area. most damage on roads, dams, towns and activities in the Case studies Mass movement / landslides 188 3.7. Volcanic Eruption 3.7.1. SUMMARY OF FINDINGS FOR such as time to eruption onset, time required for VOLCANOES evacuation, spontaneous evacuation or return, the possible eruption size, and political pressures. Volcanic eruptions, which occur when magma and other volcanic materials reach the surface of the Earth, are one BCRs from economic assessments have been used as of the devastating natural disasters that cause losses of a quantitative and auditable method to assist life and massive destructions. There are two common authorities to make key decisions that reduce the risks types of volcanic eruptions: (1) explosive eruption, which and impact of volcanic eruptions. BCA serves an expels fragmented materials (such as volcanic ash, important role in decision-making for volcanic crisis pyroclastic deposits, and assorted gases) into the air; and management, specifically taking decisions on when to (2) effusive eruption, which involves the production of order evacuation of a population or not, given the flowing lava (Self, 2006). threat of eruption—balancing the cost of evacuation with the inherently uncertain likelihood of eruption In this section, we have demonstrated economic even when there are signs of volcanic unrest. Such assessments of decision-making tools for evacuation assessment can be used to ‘segment’ populations and during a volcanic eruption (for example, enhancing assess their BCR of an evacuation, which may vary preparedness through early warning and monitoring depending on their circumstances (Woo, 2015). systems) and infrastructure for evacuation and response (for example, evacuation and escape routes). Benefits of preventive investments can be substantial Benefits of the investments are presented by a in terms of decision-making mechanisms for qualitative review of the cost-effectiveness of existing evacuation in the case of eruption. An example is the EU projects. In these case studies, volcanic eruptions EWS for volcanic eruptions and earthquakes often pose a risk on urban areas as well as national undertaken in the Canary Islands, Spain (VOLRISKMAC roads, which thus presents a challenge for large-scale project (European Commission, 2018)). Moreover, evacuations. infrastructure for evacuation and response can substantially reduce negative impacts from volcanic Models need to be adapted to the type of eruptions. For examples, investments in resilient investment. For volcanic activities, BCA has been escape routes that were undertaken in Italy (project focusing on the substantial net benefits of investments financed by the EU ‘Redeveloped road to upgrade in volcano monitoring and eruption forecasting and volcano escape route’) achieved benefits in terms of evacuation. When an economic assessment is enhanced connectivity and at the same time disaster undertaken, it is necessary to include uncertain factors risk reduction. that depend on the type of eruption and investment, Case studies Volcanic Eruption 189 3.7.2. DECISION MAKING FOR EVACUATION approach, Marzocchi & Wood (2009) determined a IN THE CASE OF ERUPTIONS probability threshold of 0.01 per month at which point an evacuation should be declared for a defined BCA for volcanic risk is focused on informing volcanic 1kmx1km area, for Campi Flegrei; Sandri et al. (Sandri, crisis management, specifically taking decisions on et al., 2012) using the same methods determined the when to order evacuation of a population or not, given threshold to be 0.014 per month for the Auckland the threat of eruption—balancing the cost of Volcanic Field, New Zealand. The modelled cost of evacuation with the inherently uncertain likelihood of eruption depends on the probability of eruption given eruption even when there are signs of volcanic unrest. the volcanic unrest (higher probability of eruption Several approaches have been proposed for this. yields higher expected cost) and is also influenced by Marzocchi & Woo (2007; 2009) and Woo (2008) use the time people would be required to evacuate for static parameters of number of evacuees average (longer period, higher costs), value assigned to a socio-economic loss per capita due to the evacuation, human life, and value of socio-economic activity in and the product of avoided fatalities social WTP to the area (for example, GDP per capita). Using dynamic save a human life (Woo, 2015) suggests BCA can be factors, Bebbington & Zitikis (2015) show a probability used to ‘segment’ populations and assess their BCR threshold is much lower for a case of Vesuvius erupting of an evacuation, which may vary depending on their (0.035 for a 30-day evacuation and 0.055 for 90-day circumstances. Bebbington & Zitikis (2015) note the evacuation) than using a static model (0.1 for a 90- need to account for dynamic and uncertain factors in day evacuation), with absolute costs of evacuation using BCA in, considering volcanic evacuation estimated at €8,000 per capita for a 90-day period in decisions. their case study. At eruptive probabilities greater than the thresholds, the cost of not declaring evacuation is Uncertain factors include time to eruption onset, time higher than €8,000 per capita. required for evacuation, spontaneous evacuation or return, the possible eruption size, and political In terms of international experience, preventive pressures. In the evacuation context, costs may be investments have been proven to yield substantial net the direct costs of evacuation (for example, opening benefits. The 2018 lava flow in Puna, Hawaii, that led shelters and transport to evacuate people), economic to the closure of one of the region’s major highways costs of evacuation (due to daily productive activities and disturbed the local transportation system reveals being disrupted), political cost to decision-makers of that there is a need for effective responses and timely evacuation being declared if no eruption occurs, and sharing of information between authorities, scientists, potential loss of life to people who do not evacuate. and community organizations after a volcanic hazard Benefits are the avoided loss of life due to successful occurs (Kim, et al., 2018). In addition, monitoring, evacuation. In addition to uncertainty around people’s forecasting, and response in advance of the 1991 behaviour (decision to evacuate or not and the time Pinatubo eruption in the Philippines is said to have taken to evacuate), uncertainty exists in the eventual saved at least €202 million of damage to property magnitude of eruption and the area affected by (including substantial amounts of moveable US eruptive material (lava, tephra, and so on) - therefore military equipment) and at least 5,000 lives. The total in the definition of area to be evacuated. Bebbington costs of forecasting and responding in this eruption & Zitikis (2015) propose a stochastic approach to are estimated at US$45.2 million—a BCR of around 4 account for these factors, whereas previously (USGS, 2005). There are several examples of proposed approaches treated this as a static analysis. European Commission and national funding aimed at enhancing preparedness and response in the case of By comparing the incurred costs of eruption with no volcanic eruptions. Some of these investments are evacuation, against those incurred when evacuation presented in more detail in Box 14 below. is declared, decision-makers can be given a probability-of-eruption threshold, above which an evacuation should be declared. Using the static Case studies Volcanic Eruption 190 Box 14: Investments in preparedness for volcanic eruptions A review of investments in early warning or general detrimental given its dense population. Therefore, the EU preparedness for volcanic eruptions in Spain provided VOLRISKMAC project (European Commission, 2018), several lessons learned and inspiring achievements outlined implemented from 2017 to 2019, aimed at strengthening below. A main lesson is that preventive investments in terms research, development, and innovation in the islands to of volcanoes can have a number of co-benefits and therefore bolster EWS for eruptions and earthquakes and design be relatively cost-efficient. enhanced crisis management capabilities using simulations and drills that help quantify the susceptibility of areas to An investment was undertaken in Spain that focused on direct and secondary environmental consequences. As a EWS both for volcanic eruptions and earthquakes. result of the project, the monitoring networks for 10 active Macaronesia, which is comprised of Portugal’s Azores and Macaronesian volcanoes were strengthened, 37 permanent Madeira archipelagos, the Canary Islands in Spain, and the volcano monitoring stations were being set up, and 5 new African nation of Cape Verde, is facing increased vulnerability portable volcano monitoring instruments have been to volcanic eruptions and earthquakes that can be extremely acquired. 3.7.3. INFRASTRUCTURE FOR EVACUATION et al., 2017). Hence, investments in road resilience AND RESPONSE improvement and escape routes planning in advance can enhance the efficiency of evacuation when an During a volcanic eruption, effective roads and eruption occurs, leading to less fatalities and injuries. In transportation network are crucial for rescuing and Europe, economic assessments have been undertaken evacuation. However, transportation networks are to quantify the impacts and losses due to volcanic vulnerable to volcanic activity, as they can be damaged eruptions and present the direct and indirect benefits of or blocked during eruptions and disturbed by the impact investing in evacuation and escape routes. An example of of volcanic ash, which includes road marking coverage such assessments with its inspiring outcome is presented and reduction in visibility and skid resistance (Blake, in Box 15 below: Box 15: Evacuation routes in volcanic areas A review of infrastructure investments in evacuation routes proximity with an estimated likelihood of medium-term in the case of volcanic eruptions in Italy provided interesting eruption. Because of the imminent -- and unpredictable -- messages in terms of potential large co-benefits as outlined threat, the Italian government has devised a plan to below. It also showed that engagement of the population for evacuation a defined ’red zone’ 72 hours ahead of an buy-in of solutions that can provide economic benefits can impending eruption and has proposed compensation for enhance effectiveness of interventions. people to relocate and creating a national park around the In Italy, investments have been made to establish resilient/ volcano to avoid illegal building (Pasha-Robinson, 2016). escape routes in the case of volcanic eruptions. Though However, this has received slow uptake and enthusiasm volcanic eruptions rarely occur, some Italian urban areas given that the region is a considerable touristic attraction are highly vulnerable to these destructive natural disasters with related economic opportunities. The project (European (European Commission, 2007). In the past few decades, Commission, 2007) financed by the EU “Redeveloped road vulnerability of populations has increased because of rising to upgrade volcano escape route” during the programming population density in cities and related complex period 2007-2013 aimed to undergo works on the national infrastructure. Scientists warn that the impacts of a Vesuvius road north of Mount Vesuvius to improve regional eruption could be catastrophic given the proximity of accessibility and create a better escape route for local Naples, with its population of 3 million people. A 2010 people in the event of a big volcanic eruption or earthquake. analysis estimated that €55 billion of residential property is Total investment was €53.4 million, of which €26.7 million exposed to the potential impacts of a Vesuvius eruption was financed by the EU. This could be seen as a “no regret (Hofmann, 2010). The highly active and dangerous volcano investment” as it both enhances connectivity and disaster Campi Flegrei (De Natale, et al., 2017) is also in close prevention. Case studies Volcanic Eruption 191 3.8. Epidemic and Disaster Health Preparedness 3.8.1. SUMMARY OF FINDINGS FOR threats. The lack of medical countermeasure EPIDEMIC/PANDEMIC RISKS stockpiles at the EU and MS levels and the vulnerability of EU supply chains for critical medical The COVID-19 pandemic has shown the countermeasures have been one of the main consequences of systematically underinvesting in challenges faced during the pandemic (European resilience. Climate change, DRR, and pandemic Commission, 2020c). The EU lacked effective impacts underline the systemic, cascading, and mechanisms and structures to have an overview of compounding nature of risks and the need to demand and supply of critical medical countermeasures strengthen resilience of societal systems (UNDRR, to monitor and support MS in addressing shortages. 2020). To strengthen the preparedness for infectious disease, it is important to learn from the experiences The Joint Procurement Agreement (JPA) for medical regarding preparedness for natural disasters countermeasures was approved by the European accumulated over the years (Wilson, et al., 2020). Commission, and as of April 2020, it has been signed by 37 countries (European Commission, 2020d). The Epidemic and disaster health should be considered in agreement provides a voluntary mechanism enabling tandem when developing, updating, strengthening, participating EU countries and the EU institutions to and funding preparedness planning for the health and jointly purchase medical countermeasures for different well-being of communities. Natural disasters are categories of cross-border health threats including increasing in their frequency and complexity. vaccines, antivirals, and other treatments. It lays down Understanding the cascading effects of disasters and common rules for practical organization and joint how they may lead to infectious disease outbreaks procurement procedures. While such agreements underscores the importance of developing cross- during the pandemic can help change the trajectory of sectoral preparedness strategies. Suk et al. (2020) supply shortages and unequal distribution of goods, found that the cascading effect of disasters, such as mechanisms could and should be strengthened before earthquakes and floods in the EU, has led to the the onset of health or other natural hazard crises. outbreak of infectious disease. The projection that climate change-related extreme weather events will In this section, we have presented benefit-cost increase in Europe in the coming century highlights assessments for the return on investment of national the importance of strengthening preparedness public health programs and equipment for health- planning and measures to mitigate and control related disasters (for example, PPE). BCRs for the outbreaks in post-disaster settings (Suk, et al., 2020). investments are obtained from a review of external BCA undertaken with ex post assessments. Other The COVID-19 public health crisis has highlighted that examples focus on risks from real and hypothetical all countries, including the EU MS, have to increase pandemics as well as the current COVID-19 crisis. efforts regarding preparedness and response planning Table 80 summarizes main data and information for epidemics and other serious cross-border health sources. Case studies Epidemic and Disaster Health Preparedness 192 Table 80: Overview of data and information sources for epidemics/pandemics analysis INVESTMENT CASE STUDY DATA SOURCE NAME AND REFERENCE Return on investment Return on investment of Ex post assessments based on the external study Return on of national public national public health Investment of Public Health Interventions: A Systematic Review health programs programs Equipment for health- Equipment for health- Ex-post assessments based on the US study The Case for related disasters related disasters Investing in Pandemic Preparedness, published in book The Neglected Dimension of Global Security: A Framework to Counter Infectious Disease Crises Source: World Bank based on external data and information Models need to be adapted to the types of The investments generally yield high positive results. investment. When modelling the impact of epidemic Local and national public health interventions in and disasters, it is necessary to include not only the Europe are highly cost saving, though the specific immediate impact on public health and the needs of BCRs vary according to the regions and the types the health system but also long-term impacts to mental of investments. The BCR for investments for health and well-being. For assessments that examine preparedness against pandemics is extremely high, the effectiveness of governance related to pandemic which reveal the benefits of enhancing the world’s preparedness, a conservative model is used to medical equipment and defense against epidemic estimate the risk of pandemic events, which suggests risks. More details are included in Figure 39. that the true risk may be underestimated (GHRF Commission 2016). Figure 39 presents boxplots that display the distribution of BCRs for different types of investments BCRs for investments in public health system and in epidemics/pandemics based on a five-number preparedness planning at local and national levels summary: minimum (shown in orange), first quartile, reveal that such investments are highly cost saving in median (shown in red), third quartile, and maximum reducing the negative outcomes of epidemic and (shown in orange). The outliers are shown as dots. natural hazards to health and well-being. Figure 39: Findings of BCA for epidemics/pandemics (BCRs) Source: World Bank analysis based on external data and information; presenting results from literature based on external reports (1 Equipment for health-related disaster result from (Masters, et al., 2017), 1 Return on investment of national public health programs result from (GHRF Commission, 2016)) Case studies Epidemic and Disaster Health Preparedness 193 The effectiveness of health prevention activities can undertaken to understand supply-chain mechanisms be assessed among others by a return on investment and constraints of PPE or other equipment for of national public health programs. As has been preparedness as well as benefits of pre-positioning evidenced during the COVID-19 crisis, epidemics and equipment. pandemics are inherently related to health and reliant on the robustness of public health systems. The OECD 3.8.2. RETURN ON INVESTMENT OF has found that most countries, regions, and cities were NATIONAL PUBLIC HEALTH not prepared well for this pandemic for several reasons, PROGRAMS including lack of crisis management plans for pandemics or lack of basic equipment (OECD, 2020). This case study is an external analysis that was Moreover, long-term impacts such as on mental health undertaken with ex-post assessments also have to be alleviated with the help from public services. Æ Introduction and background • Case study 25 (External analysis (Masters, et al., As has been evidenced during the COVID-19 crisis, 2017), ex post): A review of around 3,000 studies epidemics and pandemics are inherently related to (Masters et al. 2017) to determine the return on health and reliant on the robustness of public health investment of public health interventions in high- systems. Resilient health systems can meet the surge income countries as well as mental health impacts and demands of patient loads if planned in advance. (Tanielian & Jaycox, 2008) yielded interesting Additionally, disasters tend to have considerable insights into the benefits of public health impacts on health and the resilience of public health interventions (BCR of 8.3, ROI of 1–14.3) or systems can be a crucial factor to mitigate the costs preventive mental health care. Further research on and losses in the case of disasters. As described in the mental health impacts under a disaster could introduction, health programs and DRM must be provide relevant insights for this type of analysis. considered together when preparing for resilient societies, as they are highly interdependent. Sufficient investment in equipment is essential as part of preventive activities for health-related disasters. The OECD (2020) has found that most countries, Due to the demand surge and global supply-chain regions, and cities were not prepared well for this disruptions, panic buying has become a headline of pandemic for several reasons: the COVID-19 pandemic. Panic buying threatens the health systems’ ability to prevent and treat the a. They underestimated the risk when the outbreak coronavirus with shortages of hand sanitizers, masks, emerged. and pain relievers. Panic buying also depletes medicines for patients with chronic diseases. In b. Many did not have the crisis management plans addition, to understand the longer-term impacts of for pandemics (with the exception of Asian preparing or pre-positioning of equipment for countries that battled the SARs pandemic and pandemics, it is also important to consider the near- some others, such as the Nordic countries, where term implications of not pre-positioning, as in the case crisis management plans are required). of price surges for health equipment. Better preparedness can result in more streamlined efforts to c. They lacked basic, essential equipment, such as protect individuals and the EU has started to stockpile masks. medical equipment since March 2020 as part of the rescEU program (European Commission, 2020e), d. They absorbed reduced public expenditure and which provides support to member countries as part of investment in health care and hospitals. Since the EU Civil Protection Mechanism. the start of the ‘Great Recession’ launched by the 2008 financial crisis and up until 2018, the Case study 26 (External analysis (GHRF Commission, number of hospital beds per capita decreased in 2016), ex post): An analysis of preparedness almost all OECD countries, declining 0.7 percent investments compared to the negative consequences per year, on average (see Figure 40, with the color of a pandemic would indicate highly positive net representing the number of hospital beds per benefits. However, more research would have to be 1,000 inhabitants). Case studies Epidemic and Disaster Health Preparedness 194 Figure 40: Hospital beds per 1,000 inhabitants by region, 2018 Source: OECD (2021) The impact of natural hazards on the public’s health surgery and care above the baseline of medical can be divided into four categories: (a) direct impact emergency. After a week or so (phase 2), emergency on the health of the population; (b) direct impact on needs subside but the hospital deals with handling the health care system; (c) indirect effects on the trauma complications. Simultaneously (phase 3) populations health; and (d) indirect effects on the non-trauma emergencies (for example, infectious health care system (Shoaf & Rotiman, 2000). disease and treatment of chronic diseases) increase; they are related to destruction of infrastructure or Figure 41 provides a schematic of these impacts as disruption of health care system. Finally in phase 4, well as need and use of hospital resources after a there is an increase of elective care needs that have time-point disaster such as an earthquake. been postponed due to the disaster (Louis, et al., Immediately after the event (phase 1), there is 2008). immediate and high demand for trauma-related Case studies Epidemic and Disaster Health Preparedness 195 Figure 41: Schematic phases of natural hazards’ effects on public health resources Source: Louis, et al. (2008) It is necessary to address not only the immediate natural disasters as a chronic mental issue stressor. needs of the health system required for epidemics and The most common disaster-induced mental health disasters but also long-term impacts to mental health issues are post-traumatic stress disorder (PTSD), and well-being. There is a correlation between the depression, and anxiety (Public Health Emergency, occurrence of a disaster and a decrease in mental 2020). The total costs of mental health problems are health shortly after someone has experienced it more than 4 percent of the GDP across EU countries, (Makwana, 2019). This is because the unpredictable and more than one in six people in EU countries have a nature of disasters disrupts a victim’s fully functioning mental health problem in any given year (OECD, life, leaving them disoriented from a loss of identity, a 2018b). Mental health issues affect the unemployed daily routine, and a lack of control over their own and elderly disproportionately and have been found to possessions. Psychological symptoms associated with reduce worker productivity by 6 percent, amounting to these feelings include severe and uncontrollable €600 billion throughout Europe per year (OCED, stress, prolonged feelings of grief or sadness, and 2019a) (see also Figure 42).33 The WHO has reported substance dependency, which can translate into that the COVID-19 pandemic has caused elevated maladaptive physiological reactions. A study of a 2018 rates of stress or anxiety, and as levels of quarantine Camp Fire in Northern California reveal that many are introduced, levels of loneliness, depression, victims to the fire presented symptoms of mental harmful alcohol and drug use, and self-harm or health disorders, especially PTSD and depression suicidal behaviour are also expected to rise (WHO, (LaFee, 2021). This presents climate change and 2020). 33 The €600 billion value in the EU or more than 4 percent of the GDP includes direct care cost, social security programs, and indirect public expenses related to unemployment and the reduced productivity of people affected by mental illness. Case studies Epidemic and Disaster Health Preparedness 196 Figure 42: Estimated direct and indirect costs related to mental health problems across the EU as a % of GDP, 2015 Source: OECD (2018b) It is imperative for investments in resilient health care servicemembers, family members, and society in systems to be coordinated with DRR efforts. Evaluation general. All three conditions affect mood, thoughts, of existing health systems in the EU during the short and behaviour; yet these wounds often go un­ and long term is required as more natural and climate- recognized and unacknowledged (Tanielian & Jaycox, related disasters disrupt communities, further 2008). The mental health implications of disasters burdening the health care system. This is made often include war and natural disasters and can cause evermore necessary due to the current pandemic. horror, anger, fear, sleep problems, increased Studies on existing systems can offer insight into substance abuse, and social isolation along with PTSD systemic gaps of health services and infrastructure (Hamaoka, et al., 2010). with and without disasters influencing needs and demands, better preparing nations for health Æ Methodology emergencies and natural disasters. This is a literature review on existing studies regarding Æ Description pandemic preparedness and health-related needs following disasters. Masters et al. (2017) undertook In a study conducted by Masters et al. (2017) , the systematic searches on all relevant databases authors reviewed nearly 3,000 studies to determine (including MEDLINE; EMBASE; CINAHL; AMED; the return on investment of public health interventions PubMed, Cochrane and Scopus) to identify studies in high-income countries. The study conducted a that calculated an ROI or BCR for public health literature review and undertook a qualitative interventions in high-income countries. assessment on the return of investment in European countries on public health programs. Data collection for the study on mental health by RAND began in April 2007 and concluded in January 2008. In another study in 2008, Tanielian & Jaycox (2008) Specific activities included a critical review of the conducted a comprehensive analysis of the post- extant literature on the prevalence of PTSD, major deployment health-related needs associated with the depression, and traumatic brain injury and their short- three conditions among veterans: the health care and long-term consequences; a population-based system in place to meet those needs, gaps in the care survey of servicemembers and veterans who served in system, and the costs associated with these conditions Afghanistan or Iraq to assess health status and and with providing quality health care to all those in symptoms, as well as utilization of and barriers to care; need. The study focuses on PTSD, major depression, a review of existing programs to treat servicemembers and traumatic brain injury, not only because of current and veterans with PTSD, major depression, and high-level policy interest but also because, unlike the traumatic brain injury; focus groups with military physical wounds of war, these conditions are often servicemembers and their spouses; and the invisible to the eye, remaining invisible to other development of a microsimulation model to forecast Case studies Epidemic and Disaster Health Preparedness 197 the economic costs of these conditions over time. productivity, and pain and suffering). After a two-year Interviews with senior Office of the Secretary of study, RAND found that, in 2008, it cost between Defence (OSD) and Service (Army, Navy, Air Force, €4,450 and €7,837 to treat PTSD in military Marine Corps) staff within the Department of Defence personnel.34 However, with co-morbidities like and within the Veterans Health Administration depression, this cost can increase as high as €12,740. informed efforts to document the treatment and The National Hazard Mitigation Saves Report uses the support programs available to this population. Note, RAND study and estimates €6,789 to indicate direct however, that while the focus on mental health on this treatment costs, and because direct treatment costs particular population is not related to pandemics or are only 10 percent of the total cost of mental health epidemics, it does highlight the impacts of prolonged treatment, it would take €67,889 of treatment over chronic stresses and catalogues experiences through one’s life to avoid a statistical incidence of PTSD interviews that can be applicable to health emergency (Tanielian & Jaycox, 2008; Multi-Hazard Mitigation and disaster health impacts on populations. Council, 2019). Æ Results of the studies In populations heavily affected by COVID-19, such as Lombardy in Italy, the issues of service access and Masters et al. (2017) concluded that local and national continuity for people with developing or existing mental public health interventions are highly cost-saving, and health conditions are also a current major concern, cuts to public health budgets in high income countries along with the mental health and well-being of frontline are likely to generate billions of pounds of additional workers (WHO, 2020). Often, mental health issues are costs to health services and the wider economy. considered secondary to physiological impacts on Quantitatively speaking, the research found that the humans but can have prolonged or generational median ROI for public health interventions was 14.3 to impacts. It is pertinent to consider the BCAs of both 1 and median BCR was 8.3. existing public health interventions and long-duration, mental health illnesses for holistic public health and For interventions in Europe, the study found the test the systems that can provide the needed services. following BCRs: Æ Challenges faced and lessons learned • Development of 20 mph zones in London, United Kingdom, resulted in a BCR of 0.66–2.19. Future studies should employ similar studies on the costs of physical health and mental health following • UK parenting programs for the prevention of small- and large- scale disasters. Mental health persistent conduct disorders in the resulted in a following disasters is understudied and underreported 7.89 BCR. but can have lifelong implications. Therefore, the focus on young persons affected by large-scale or frequency • HIB vaccination program in Sweden resulted in a disasters should be carefully studied for all-hazards 1.59 BCR. throughout Europe. • Family planning services in the United Kingdom In addition, investing in preparedness for detecting resulted in a BCR of between 11.09 and 29.39. and treating cases, reinforcing governance and oversight, building local diagnostic capacity, and There is a clear advantage of having health intervention strengthening systems for treatment and infection programs in overall public health, which could serve as control are needed. Designing public health measures a litmus test of robust health systems in a country to prevent the spread of disease in the community when faced with epidemics or natural disasters. (quarantining, social distancing, handwashing, limiting travel and trade, and eventually vaccinating) and According to the study measuring the costs of mental establishing contingency plans to maintain essential health treatment for military personnel, researchers services and supplies are all areas of evaluation for found that the direct cost of mental health treatment is COVID-19 or any future health emergencies (World 10 percent of the overall incidence cost and other Bank, 2020b). costs incurred (for example, lost wages, lost household 34 Original values in US dollars. Case studies Epidemic and Disaster Health Preparedness 198 3.8.3. EQUIPMENT FOR HEALTH-RELATED and pain relievers. Panic buying also depletes DISASTERS medicines for patients with chronic diseases. The suppliers’ market that has been created has allowed This case study is an external analysis that was suppliers and distributors to establish new terms and undertaken with ex-post analysis. conditions for buyers. The 2014 West Africa Ebola outbreak was exacerbated by the lack of medical Æ Introduction and background supplies and PPE which led to an increased rate of infections and poor control of the epidemic. Panic The global community has greatly underestimated the buying also leads to health scams. For example, in risks that pandemics present to human life and early March, Europol law enforcement confiscated livelihoods which have affected the policies needed to 34,000 counterfeit surgical masks in one coordinated safeguard lives. At the time of writing, there were more operation. than 59 million confirmed cases in 190 countries and more than 1.4 million deaths (BBC News, The Visual In addition, to understand the longer-term impacts of and Data Journalism Team, 2020). To combat the preparing or pre-positioning of equipment for spread of the COVID-19 by vaccinating and assisting pandemics, it is also important to consider the near- those who have been severely stricken with the term implications of not pre-positioning, as in the case disease, medical equipment like masks and ventilators of price surges for health equipment. The information is extremely important to have on hand at all times. below lists the market prices and markups of essential PPE and equipment following the COVID-19 pandemic. Due to the demand surge and global supply-chain It is found that the cost of PPE supplies increased by disruptions, panic buying has become a headline of over 1,000 percent, according to the Society for the COVID-19 pandemic. Panic buying threatens the Healthcare Organization Procurement Professionals health systems’ ability to prevent and treat the (SHOPP) (2020).35 coronavirus with shortages of hand sanitizers, masks Table 81: Cost of PPE supplies in the United States pre-COVID19 and during COVID-19 ITEM PRE COST DURING PRICE MARKUP PERCENTAGE COVID-19 COST COVID-19 MARKUP Vinyl exam gloves (€) €0.02 €0.05 €0.04 300% Latex gloves (US$) 0.03 0.07 0.05 267% Nitryl gloves (US$) 0.05 0.09 0.05 200% 3ply masks (US$) 0.05 0.68 0.63 1500% K95 masks (US$) Not applicable 3.60 Not applicable Not applicable N95 masks (US$) 0.34 5.18 4.83 1513% 3M N95 masks (US$) 0.10 6.08 5.98 6136% Hand sanitizer (US$) 0.23 0.50 0.27 215% Isolation gowns (US$) 0.23 4.50 4.28 2000% Face shields (US$) 0.45 4.05 3.60 900% Soap (US$) 0.17 0.32 0.14 188% Source: SHOPP (2020), values as of April 7, 2020. Original values in US dollars 35 Original values in US dollars. Case studies Epidemic and Disaster Health Preparedness 199 For these reasons and more, the EU has started to The study by Turabi & Saynisch (2016)simulates the stockpile medical equipment since March 2020 as distribution of expected pandemic events per century. part of the rescEU program (European Commission, The study is referred to in the Case of Pandemic 2020e),36 which provides support to member Preparedness and runs 10,000 simulations of random countries as part of the EU Civil Protection Mechanism. draws from a binomial distribution to simulate the Medical equipment as part of the stockpile will include losses that might occur in 10,000 centuries and intensive care medical equipment such as ventilators, aggregating the results to show how likely it is that we PPE such as reusable masks, vaccines and see different numbers of events per century, on therapeutics, and laboratory supplies. In addition average. The model represents a conservative estimate under the JPA, MS are in the process of purchasing of the risk of pandemic events, which is to say that the PPE, respiratory ventilators, and items necessary for true risk could be higher. coronavirus testing. This coordinated approach gives MS a strong position when negotiating with the industry Æ Results of the analysis by dividends on availability and price of medical products. and overall While efforts are being made to obtain and distribute The following findings have been noted by the GHRF pandemic equipment to those countries that require it Commission (2016)37 in its study of investments for most, it is clear that better preparedness could have preparedness against the negative consequences of a resulted in more streamlined efforts to protect pandemic: individuals from the novel coronavirus through unified mechanisms. • The Commission on a Global Health Risk Framework for the Future (GHRF Commission) believes that Æ Description commitment of an incremental US$4.5 billion (€4.07 billion in 2016) per year would make the This case study is an external analysis that was world much safer and better prepared for undertaken with ex-post assessments. pandemics. €4.07 billion equates to 65 cents per person in the world.38 This figure includes This study on the Case of Pandemic Preparedness expenditures for strengthening national public (GHRF Commission, 2016) assesses the mechanisms health systems, funding R&D, and financing global and governance related to pandemic preparedness. It coordination and contingency efforts. aims to analyse the resources devoted to preventing and responding to threat of pandemics. The study • The 1918 influenza killed 50 million people and compares various diseases in the world and the arguably as high as 100 million in 1918–1920. The national policy, preparedness through pre-positioning, consensus among leading epidemiologists and and affording time for procurement that influenced public health experts is that the threat from infection the management of pandemics. Given the large scale diseases is growing. Emerging infections disease of risk for human and economic losses associated with events are increasingly significantly over time, with the COVID-19 pandemic, it is easy to demonstrate a an ever-increasing global population. compelling case for greater investment. Understanding the importance of supply and distribution of medical • The World Bank has estimated the economic impact equipment and the costs of developing preparedness of a severe pandemic (that is, one on the scale of plans can situate the EU to better prepare for another the influenza pandemic of 1918–1919) at nearly 5 pandemic or health emergency by promoting greater percent of global GDP or roughly €2.26 trillion investment in PPE and other medical necessities, (Jonas, 2014), but according to some recent which will in turn prevent potential supply chain estimates, the current coronavirus pandemic could interruptions and surge pricing. mean economic costs in the order of €2.6–4.4 trillion (US$3–5 trillion)39 in the United States alone Æ Methodology (Walmsley, et al., 2020). Some might see this as an 36 Original values in US dollars. 37 Original values in US dollars. 38 Original values in US dollars. 39 Original values in US dollars. Case studies Epidemic and Disaster Health Preparedness 200 exaggeration, but it could also be an underestimate. Æ Challenges faced and lessons learned Aggregate cumulative GDP losses for Guinea, Liberia, and Sierra Leone in 2014 and 2015 are In the future, more research relevant to the COVID-19 estimated to amount to more than 10 percent pandemic must be undertaken to understand the (UNDP, 2015; World Bank, 2014). This huge cost is supply-chain mechanisms and constraints of PPE and the result of an epidemic that, for all its horror, other COVID-19-related equipment to inform infected only about 0.25 percent of the population pandemic and health emergency preparedness. In of Liberia, roughly 0.25 percent of the population of addition, analysing the costs and benefits of pandemic Sierra Leone, and less than 0.05 percent of the pre-positioning in terms of ready use equipment population of Guinea (WHO, 2016), with reserved for crisis situations will be important in future approximately 11,300 total deaths in these studies. Potential case studies for investigation can countries (CDC, 2016). The Commission’s own include: scenario modelling, based on the World Bank parameters, suggests that during the 21st-century • Analysing the impacts to public health when global pandemics could cost in excess of €4.52 equipment is single sourced versus multi-sourced, trillion, with an expected loss of more than €45.2 billion per year.40 • Evaluating outcomes on export bans for equipment and the impact on health, • The BCR that can be estimated from the report is €45.2 billion/€3.39 billion = 13.3 • Assessing the outcomes on repurposing facilities for PPE and other equipment development, Overall, there is a clear case for the benefits of significantly upgrading the world’s defences against • Quantifying the benefit of preidentified health pandemics. While they may be substantial, they are facilities versus no centralized information on not out of reach. The flaws in defences costs thousands hospital/pharmacy/health clinic equipment and of lives, and the ultimate cost of a pandemic is always capacities, and higher than what could be projected. The study finds how relatively little countries are investing to protect • Examining the COVID-19 impacts based on the world from the threat of infectious diseases. It is countries that have emergency plans and also found that prevention is far more cost-effective distribution arrangements versus those that do not. than response and that the most effective response is a well-prepared response. 40 Original values in US dollars. Case studies Epidemic and Disaster Health Preparedness 201 3.9. Oil spills 3.9.1. SUMMARY OF FINDINGS as it depends on many factors, such as the type of oil FOR OIL SPILLS spilled and the type of environment and ecosystem involved (Holleman, 2004). An oil spill is a technical incident that causes tremendous damages to the environment and the In this section, we have presented a benefit-cost ecosystem, especially in marine and coastal areas as assessment for preventive investments in vessels and an oil spill often occurs on the sea. Oil spills lead to the equipment in coastal areas. BCR for the case study is immediate consequence of fire hazards and negatively shown by a review of external ex ante BCA of the affect wildlife by disturbing the habitats and threating preventive investment. The impacts mostly considered the lives of the species, especially for those living in in the case study is the damages from vessel-source oil these ecosystems (Bautista & Rahman, 2016). Clean- spills and marine pollution. Table 82 summarizes ups and assessments after an oil spill are challenging, main data and information sources. Table 82: Overview of data and information sources for oil spills analysis INVESTMENT CASE STUDY DATA SOURCE NAME AND REFERENCE Preventive A multi- Ex-ante assessment Commission Staff Working Document Evaluation: Ex Post investments functional Evaluation of Major Projects in Environment Financed by the European Regional in vessels and ship to Development Fund and the Cohesion Fund between 2000 and 2013, published by equipment in tackle Secretary-General of the European Commission coastal areas marine pollution Consultation with the Ministry of the Environment of Estonia (Head of Marine Environment Department), Police and Border Guard Board (Police Captain) Source: World Bank based on external data and information Modelling of the effect of a catastrophic oil spill is not have common standards and thus difficult to useful in terms of revealing the benefits of oil spill quantify (BOEM, 2016). preventions. In an economic assessment, the frequency and spill size volume of a hypothesized oil The result of the investment shows a small BCR higher spill are viewed as essential factors that can affect the than 1 due to a conservative estimation of the net modelling and the result. benefits. Nevertheless, preventive investments are still considered as highly beneficial as such investments, When calculating BCRs for investments that prevent or among others, require significantly lower mitigate the impact of oil spills, the quantification of implementation costs and thus yield higher net the avoided costs is crucial yet challenging. While it is benefits compared to post-disaster remediation. More easy to calculate the response and clean-up costs, the details are included in Figure 43. The figure presents a risked social and environmental costs such as the graph that displays the BCR for investments in oil spills. losses in commercial fishing and ecosystem usually do Case studies Oil spills 202 Figure 43: Findings of BCA for Oil Spills (BCR) Source: World Bank analysis based on external data and information; presenting results from literature based on external reports (1 Preventive investment result from (European Commission, 2020a)) Preventive investments against oil spills can constitute, 3.9.2. PREVENTIVE INVESTMENTS IN among others, the deployment of vessels and VESSELS AND EQUIPMENT IN equipment in coastal areas. In recent decades, the EU COASTAL AREAS has become more proactive in preventing vessel- source pollution through the adoption of new, It is far less expensive to prevent an oil spill than to prevention-oriented regulations. The European clean one up. That is why preventive investments, such Commission has provided a range of services and tools as spill prevention programs and legislation, play an to support coastal countries in prevention, such as a important role in reducing the frequency of major toolbox for effectiveness of response (EMSA, 2021b), spills. An international example of robust oil spill focusing on equipped oil spill response vessels. Also, prevention, preparedness, and response is in the European Maritime Safety Agency (EMSA) was Washington, United States. In the wake of the 1988 established to provide technical and scientific advice Washington State ‘Netsucca’ and 1989 Alaskan ‘Exxon on maritime safety and the prevention of pollution by Valdez’ oil spills, the state of Washington established a ship (EMSA, 2021a). comprehensive spill preparedness and response program in July 1990 and a spill prevention program in • Case study 27 (external analysis (European 1991. Actions for these programs include 24-hour oil Commission, 2011b), ex ante): An analysis of a and hazardous material spill response capability preventive investment against oil spills in Estonia, statewide; oil spill contingency plans drafted for namely, a multi-functional ship to deal with incidents vessels over 300 gross register tonnage (GRT); of marine pollution, yielded a BCR of 1, although net required tank vessel spill prevention plans, cargo and benefits were not estimated, particularly the passenger vessel inspections, and vessel bunkering quantification of benefits of potential oil spills being checklists and inspections that were enforced; and a reduced. These benefits could be substantial as oil natural resource damage assessment. These proactive spills have impacts beyond borders and can cause efforts put Washington significantly ahead of the rest considerable disruptions to ecosystems. of the United States in terms of the reduction of the number of oil spills and rates of oil spills by tonnage transport and transit. Case studies Oil spills 203 For the EU, the prevention of vessel-source pollution is Regulation 724/2004 considerably expanded EMSA’s a cross-sectoral issue that involves the protection of role to include an increased emphasis on maritime the marine environment and maritime transport. After security alongside the response to pollution by ships the ‘Erika’ oil spill disaster off the coast of France in (Liu & Maes, 2010). 1999 and the ‘Prestige’ oil spill off the coast of Galicia, Spain, in 2002, the EU became more proactive in The European Commission has provided a range of preventing vessel-source pollution through the services and tools to help coastal countries to prevent adoption of new, prevention-oriented regulations. This or reduce oil spills and marine pollution incidents. is mainly dealt with by the Directorate General of EMSA offered a ‘toolbox’ that can respond to oil spill Energy and Transport. Moreover, EMSA was established incidents at the request of EU MS quickly and by Regulation (EC) 1406/2002 as part of the Erika II effectively (see Figure 44 for EMSA’s network of Oil package (EMSA, 2021a). EMSA provides the European Spill Response Vessels) (EMSA, 2021b). The service is Commission with technical and scientific advice on accomplished by the operation of fully equipped oil maritime safety and the prevention of pollution by spill response vessels, which has to respond to an ships to develop new legislation and evaluate the incident and set sail within a limitation of 24 hours. effectiveness of already-implemented measures. Figure 44: EMSA’s Operational Oil Spill Response Services Source: EMSA (2021b) Case studies Oil spills 204 PREVENTION OF OIL SPILL IMPACTS IN ESTONIA: A MULTI-FUNCTIONAL SHIP TO TACKLE MARINE POLLUTION This case study is an external analysis that was Estonian authorities have stated that an oil spill can be undertaken with ex ante assessments that included considered as an environmental emergency that is quantitative estimations of benefits. the most expensive and most probable to happen. A study based on historical spill data found that the Æ Introduction and background average per-unit clean-up cost of marine oil spill in Estonia is €7,616 (US$6,820.62) per tonne (Dagmar, The Gulf of Finland and the Baltic Sea are at high risk 2001). Also, because fish eggs and larvae are of marine pollution and oil spills as they are frequently vulnerable to high oil concentration in water, oil spills involved in the shipping of oil and oil products. Every negatively affect the marine and coastal ecosystem year, over 160 million tonnes of chemicals are and thus generate economic losses in commercial transported across the Gulf of Finland (European fishing, tourism, and local recreation (Dagmar, 2004). Commission, 2020a). As a result, the Baltic Sea The per-unit socio-economic and environmental cost receives 30–60 metric tonnes of oil annually, and it is of an oil spill is shown in Table 83 below, according to estimated that 2.87 oil spill accidents take place in the the EPA Basic Oil Spill Cost Estimation Model. Baltic Sea every year (Elin, et al., 2001). Table 83: Socioeconomic and Environmental Base Per-Gallon Costs for Oil Spills Source: Dagmar (2004) Case studies Oil spills 205 Æ Description Æ Methodology During an EU project (European Commission, 2011b), A BCA has been carried out for the project, based on a multifunctional ship has been procured for Estonia to guidance materials developed by the European deal with incidents of marine pollution in Estonian Commission, such as the ‘Guide to Benefit-Cost waters and other parts of Baltic Sea. During the Analysis Investments Projects’ and ‘Guidelines for programming period from 2007 to 2013, the EU Benefit-Cost Analysis Methodology’ (European contributed €29.8 million to the total investment of Commission, 2014; European Commission, 2007). €33.1 million. The analysis is based on the cash flow analysis method, while a uniform discount rate of 6 percent (real rate) Expected results are that in the event of an alert, the (Flood, 2014) was used for determining the present ship will be ready to leave from the harbour to the value of long-term receivables and liabilities when marine pollution area within 2 hours, be at the pollution assessing the financial profitability of the investment. area within six hours, and start remediation works within 12 hours. This means that under normal Æ Results of the analysis by Dividends conditions the marine pollution should be removed and overall within 48 hours. As the ship is multi-functional, it can also take a ‘supervisory’ role, carrying out prevention The result of the analysis (European Commission, and monitoring duties at sea. The mere sight of this 2020a) shows a BCR of 1 for the project, with the low highly visible ship will encourage vessels to adhere to ratio due to a conservative estimation of the net environmental regulations and wilful marine pollution benefits. Because of the unavailability of data, the will decrease. The purchase of the ship will see ship’s impact in terms of the number of deliberate oil Estonia’s capacity to tackle marine pollution rise to 26 spills being reduced is not quantified. The analysis percent of HELCOM requirements. shows that the ship achieved its goal of reducing damages from marine pollution and oil spills. The ship The ship will help also prevent and respond rapidly to supports an effective response to pollution pollution incidents to avoid contamination and emergencies, which helps reduce the spread of marine disturbance of habitats and maintain their favourable contamination and decreases the risk of marine status, ensure functioning of critical areas, and reduce pollution to the environment and human health. Such risk to human health and life. The project achieved the reduction in oil pollution and marine contamination objectives based on HELCOM recommendations benefits not only Estonia but also all the countries (removing marine pollution within 48 hours). It surrounding the Baltic Sea, including non-EU countries achieved its main target of improving offshore sea such as Russia. pollution control capacity and reduced the risk of damage from maritime pollution. This is a great Æ Challenges faced and lessons learned improvement as at the time of the project application, the Police and Border Guard Board had only one The project itself is not an ordinary direct investment pollution control ship, which had been donated by for profit but a preventive one that helps reduce Sweden in 2002 and accounted for only 13 percent of environmental pollutions. As a result, it does not have the HELCOM recommendation. a direct investment effect. Therefore, no ex post analysis has been done for the project, and the impact of the ship in terms of the number of oil spills being reduced has not been quantified (European Commission, 2011b; European Commission, 2020a). Case studies Oil spills 206 3.10. Nuclear 3.10.1. SUMMARY OF FINDINGS improving the sustainability and safety of nuclear FOR NUCLEAR RISKS power plants in Europe, no studies could be found undertaking a full BCA for such projects. This is In this section, we have presented the benefits of probably because impacts of nuclear can be sustained investments in nuclear security and remediation over millennia, which would indicate precautionary programmes for uranium production. Most investments criteria rather than analysis based on mostly economic focus on preventing risks from potential nuclear efficiency criteria. disasters in the future while enhancing sustainable energy production. One example considers the long- A number of countries have been investing in the lasting risk from chemical leaching of uranium. security of their nuclear power plants. Examples are the large-scale long-term investment in France that When conducting analysis for nuclear accident aimed to enhance the safety and security of plants or prevention, it is essential to carefully quantify the risk the comprehensive research programme centre in the of nuclear accidents by addressing the frequency for a Czech Republic (SUSEN sustainable energy project) nuclear disaster to occur. One of the standard tools to (European Commission, 2012; European Commission, quantify such accidents is the Farmer Curve, which 2011) that aims to enhance the sustainability of energy defines the risk of a nuclear power plant as ‘probability production. Moreover, the Czech Republic, as one of × consequences’ (Wheatley, et al., 2016). A Farmer the top uranium-producing countries in the world plot shows the annual frequency of fatalities or since the 1960s, has been implementing a large-scale damages from a nuclear accident, which can be used environmental programme for the past 30 years to in an economic analysis that determines the avoided close the uranium mines and a specific project co- losses of investments in nuclear risk reduction. funded by the EU supported the decontamination of Moreover, the decommissioning of chemical leaching sites (European Commission, 2011). of uranium to prevent environmental disasters and health hazards is a complex process that needs to be Although no formal BCA was conducted for the constantly evaluated and specified to achieve the investments, qualitative analyses have shown benefits environmentally and economically most effective in nuclear risk prevention and remediation of risks measures in a step-by-step process. related to uranium leakage. Investments in nuclear safety tend to be highly beneficial from a long-term BCRs analysis is rare for nuclear investments. While perspective as the potential impacts of unsafe nuclear costs on installation, maintenance, and waste plants can be major. management can be quantified for investments in Case studies Nuclear 207 3.10.2. SECURITY OF NUCLEAR POWER sources of electrical power and supplies of water, PLANTS strengthening the protection of plants against extreme external events, and devising changes and reforms of Because the possibility of a nuclear accident can never organizational and regulatory systems (Jawerth, be ruled out, there is no room for complacency in the 2016). implementation of nuclear safety practices and concepts (Nuclear Energy Agency & Organisation for To improve the safety level of nuclear power plants, the Economic Co-operation and Development, 2013). The European Commission requires the establishment of nuclear power plant accident at the Fukushima Daiichi general standards of nuclear safety monitoring Power Plant, which was catalysed by a 9.0 magnitude mechanisms. This allows the public and workers to be earthquake off the coast of Tōhoku, Japan, is protected from radiations from nuclear installations considered to be the worst nuclear disaster since and nuclear accidents. At the same time, the JRC Chernobyl in 1986. The Japanese government conducted research that ensures safe operations of estimated clean-up costs to be €64.1 billion of the Western and Russian type nuclear power plants, and it overall Fukushima disaster price tag of €171.5 billion. also analyses the effectiveness of existing mitigation However, the Japan Centre for Economic Research mechanisms based on models of hypothetical nuclear claims that the clean-up costs can intensify anywhere accidents (EU Science Hub, 2016). Countries also between €398 billion and €559 billion (Hornyak, invest in the safety of their nuclear facilities. For 2018). This event demonstrated the need for safety instance, in France, the Nuclear Safety Authority is precautions for nuclear power plants in technologically established to regulate and monitor nuclear safety and advanced countries, especially in the context of protect workers and the public from potential radiation multiple hazards. In September 2011, three months risks. after the accident, the MS of the International Atomic Energy Agency (IAEA) unanimously endorsed the IAEA A number of investments were found that provide Action Plan on Nuclear Safety, which intends to foster insights on how European countries manage nuclear international collaboration towards strengthening power plants in a safe and sustainable way. The global nuclear safety. Moreover, IAEA MS have also examples include France’s investment in nuclear comprehensively analysed its causes and con- plants security and the Czech Republic’s sustainable sequences by carrying out ‘stress tests’ to reassess the energy projects. Highlights of the projects are design of nuclear power plants against site-specific presented in Box 16 below. extreme natural hazards, installing additional backup Box 16: Investments in the security of nuclear power plants across Europe The two cases reveal in practice investments in improving nuclear power reactors to 50-60 years beyond 40 years of nuclear power plants generate potential co-benefits for the operation and improve security of nuclear operations. society and sustainability for the future. As the second phase of the SUSEN sustainable energy A large-scale long-term investment program in France has project (European Commission, 2012) , Czech Republic has achieved success in terms of improving safety and extending conducted research and analysis on the sustainability of the lifetime of nuclear power. France (IAEA, 2020; World nuclear energy. The project emphasizes on installing Nuclear Association, 2021) derives around 75 percent of its technological instruments in a sustainable energy R&D electricity from nuclear plants, so it is essential to ensure centre, which is used for the study of materials and the safety of the country’s nuclear plants. From 2014 and components used in energy production, construction, and onwards (OCED, 2019a), the EDF (France’s state-backed the operation of energy facilities, and research into methods power utility) launched an investment project aimed at for the safe disposal of nuclear waste. The cost of the improving the safety of the country’s nuclear power plants. project is over €100 million, and the positive impact of the The overall cost of the project includes maintenance cost of project includes improving sustainability in energy roughly €4.2 billion per year and decommissioning and production for the future and enhancing employment as long-term waste management cost of €75 billion (Tillement, 185 new jobs were created. 2018). The project is expected to extend the lifetime of Case studies Nuclear 208 3.10.3. CLEANING UP URANIUM have invested systematically in decommissioning and environmental cleaning. Remediation programmes for uranium production facilities aim to establish long-term, stable conditions The Czech Republic has been one of the top uranium that enable the affected areas to return to previously producing countries in the world since 1960s, and existing environmental conditions or to a land use with their extensive production of uranium led to the long-standing sustainability. These activities contamination of groundwaters and widespread encompass the restoration of mines, mills, waste environmental impacts. After 1990, a large scale management facilities, tailings containment, and land environmental programme was set up to shut down and water resources (OECD, 2019b). By cleaning up these uranium mines, and the last mine in Europe, uranium through remediation programmes, there is located in Rožná, Czech Republic, was closed in 2017. peace of mind ensuring that both current and future The cost of all remediation activities are expected to generations will be able to use the site and its be in excess of €25 billion (IAFA, 2005). surrounding areas safely. Therefore, at all stages of the remediation process, it is crucial to consider the During the 2007 to 2013 programming period, the EU principles of environmental protection, sustainable invested €20,311,400 into a €23,895,700 project development, and intergenerational equity. aimed at decontaminating, sanitizing, and re- cultivating the former MAPE Mydlovary uranium Decommissioning of the chemical leaching in uranium processing site (European Commission, 2011). As a is a long-lasting and complex process that needs to be result of mining out 24,936 m3 of contaminated constantly evaluated and specified. This overall material and removing another 24,265 m3 of process is divided into five consecutive stages to demolished and decontaminated building structures accommodate the remediation’s long time frame and and technological equipment, the region was able to stringent technical and economic requirements. reduce radiation levels and contamination risks in Therefore, the process of decommissioning may not drinking water and surface water, allow for vegetation be standardized for each site. Yet, this stage-by-stage to be re-established, and meadows and pastures to progression allows researchers to verify the steps exist again. It is important to investigate these types of individually and ensure that the process is achieving investment because water contamination and other the environmentally and economically best solutions environmental risks can become cross-border issues if possible. Some countries such as the Czech Republic not treated promptly and correctly. Case studies Nuclear 209 3.11. Chemical 3.11.1. SUMMARY OF FINDINGS FOR Flagship actions of this strategy include banning the CHEMICAL RISKS most harmful chemicals in consumer products, phasing out the use of per- and polyfluoroalkyl Chemical incidents, especially those that are an act of substances (PFAS) in the EU unless they are for terrorism, can directly cause injury from fire, explosion, essential use, boosting the investment and innovation or toxicity and indirectly create fear and anxiety in capacity for production and the use of chemicals that populations. The WHO (2020) states that the adverse are safe and sustainable by design and throughout health outcomes to toxic chemical exposure may be their life cycle, establishing a simpler ‘one substance effects that are local or arise at the site of contact with one assessment’ process for the risk and hazard the chemical (for example, bronchoconstriction from assessment of chemicals, and playing a global climate respiratory irritants or irritation of the skin and eyes by leader role in championing the continent’s high gases, liquids, and solids); effects that are systemic or standards and not exporting chemicals banned in the affect organ systems remote from the site of absorption EU. This is in addition to the European Commission’s (for example, depression of the central nervous system Seveso Directive (European Commission, 2020g) and from inhalation of solvents or necrosis of the liver from international cooperation efforts, like the UNECE’s the inhalation of carbon tetrachloride); and effects on Convention on the Transboundary Effects of Industrial mental health arising from real or perceived realness, Accidents and the OECD’s Programme on Chemical which depends on psychosocial stress associated with Accidents. an incident. The development of symptoms can vary greatly, ranging from within a day to months or even In this section, we have demonstrated a benefit-cost years. assessment for chemical risk prevention and remediation. A BCA for the investment is undertaken In October 2020, the European Commission adopted with a detailed ex post case study analysis. The the EU Chemicals Strategy for Sustainability, which is chemical risk identified in the case study is the considered to be the first step towards the European sulphuric acid tar waste and other toxic pollutants Green Deal’s ambition for zero pollution and a toxic- from waste dumpsites. Table 84 summarizes main free environment (European Commission, 2020f). data and information sources. Case studies Chemical 210 Table 84: Overview of data and information sources for chemical analysis INVESTMENT CASE STUDY DATA SOURCE NAME AND REFERENCE Cleaning up Cleaning of Costs of the investment found from the EU programming funds and description hazardous hazardous waste waste in Cost of temporary treatment between Phase I and Phase II provided by Latvia’s Latvia State Environmental Services Assumption for lives saved based on data from a WHO report for the Slovak Republic Health costs avoided based on data from the European Public Health Alliance Cost of sick/affected livestock avoided based on a study for Ethiopia (Environmental and Health Impacts of Effluents from Textile Industries in Ethiopia: The Case of Gelan and Dukem, Oromia Regional State) Information on jobs created provided by Latvia’s State Environmental Services Source: World Bank based on external data and information Models need to be adapted to type of investment. be found undertaking a BCA that examines the When modelling the effectiveness of remediation remediation of chemical incidents and the cost- strategies of chemical incidents, it is crucial to consider effectiveness of it. the direct economic consequences such as property damage as well as costs of mitigating the health risks Results from BCA of remediation investments tend to related to the incident. For some investments, the yield net benefits. Complementary investments modelling can be non-time-sensitive and focus on the and comprehensive analysis to better understand overall costs and benefits in the lifetime of the capital historic losses due to chemical spills and other investment, while future costs or benefits per year are environmental hazards as well as land value not included. appreciation can be highly informative for investments to comprehensively address remediation as well as BCRs are essential for analysing the impact of chemical target socio-economic improvements. More details incidents, as such incidents often lead to a multitude are included in Figure 45, Figure 46 and Figure 47. The of domino effects and may spawn serious figures present graphs that display the BCR, NPV, and consequences of mass casualties, property losses, ERR for investments in chemical risks (shown in red). and environmental pollution. However, few studies can Figure 45: Findings of BCA for chemical risk (BCR) Source: World Bank analysis based on external data and information Case studies Chemical 211 Figure 46: Findings of BCA for chemical risk (NPV) Source: World Bank analysis based on external data and information Figure 47: Findings of BCA for chemical risk (IRR) Source: World Bank analysis based on external data and information Cleaning up hazardous waste is a preventive contaminated commercial site (Gamper-Rabindran & investment that can prevent chemical risks. Hazardous Timmins, 2013; Taylor, 2016). waste can permeate through and contaminate all types of environmental mediums—atmosphere, • Case study 28 (new analysis under this project, ex groundwater, surface waters, and soil—to cause post (European Commission, 2020g)): An analysis harmful or even fatal effects on human health. Such of a remediation investment in Latvia to clean up health effects includes narcosis, skin irritation, and sulphuric acid tar lagoons, once operated as waste respiratory diseases, or even chronic health effects, dumpsites, yielded positive net benefits (BCR 5.8, such as leukaemia, liver tumours, lymphomas, and NPV €151 million, ERR 480.17 percent). The birth defects. Hence, cleaning up hazardous waste is analysis included direct impacts (particularly on the crucial in terms of removing toxins that negatively environment) and economic potential unlocked impacts human health, while it also yields co-benefits that can increase land value, construction in increasing property value of homes near the investments, as well as linked jobs created. Future Case studies Chemical 212 case studies could further consider further, among Cleaning up hazardous waste can have positive others, the long-term impacts on human health, environmental, economic, health, and social benefits productivity losses from agriculture avoided, or CO2 for the community. Not only do communities benefit emissions avoided. from the lack of toxins in the air once ‘brownfield’ sites are remediated, but studies have shown that the 3.11.2. CLEANING UP HAZARDOUS WASTE property value of homes near the contaminated commercial site appreciates (Gamper-Rabindran & Hazardous waste can permeate through and Timmins, 2013; Taylor, 2016). For instance, using a contaminate all types of environmental mediums— hedonic method to estimate the residents’ WTP to atmosphere, groundwater, surface waters, and soil— clean up a Superfund site, Kiel and Zabel (Kiel & Zabel, to cause harmful or even fatal effects on human health. 2012) found that the economic benefits of cleaning up Prolonged exposure to toxic pollutants can instigate two Superfund sites in Woburn, Massachusetts, range acute health effects, such as narcosis, skin irritation, from €55.47 million to €94 million. and respiratory diseases, or even chronic health effects, such as leukaemia, liver tumours, lymphomas, and birth defects. REMEDIATION BY CLEANING OF HAZARDOUS WASTE IN LATVIA This case study is a new ex post analysis under this to compare the cost of the remediation project in each project that involved innovation of quantitative phase of this two-part remediation and foresting impacts. investment along with the temporary treatment between Phases I and II. Collectively, this project is the Æ Introduction and background only major environmental project occurring in Latvia and the other Baltic states. From the 1950s through the 1980s, the Southern and Northern sulphuric acid tar lagoons within the It is important to evaluate the remediating interventions Inčukalns civil parish in Latvia were established and and their holistic benefits to communities near toxic operated as waste dumpsites. Although the landfill areas. Health issues from such toxic can arise was closed in 1986, the pollution already infiltrated immediately but more often, they are exhibited over into the near-surface groundwater and artesian water time and unfortunately through generations. For this up to a depth of 70–90 m. The pollution has migrated reason, remediation impacts should be forward looking northwards towards the River Gauga, and currently, as in the below case study (losses avoided) and the polluted groundwater extends to 148 ha consider the morbidity and mortality as around the Northern lagoon and 149 ha around the comprehensively as possible. These BCAs could also Southern lagoon. inform health care services that might be needed in the areas with caustic sites such as the acid tar lagoons Æ Description in Latvia. Cascading impacts to land, assets, livestock, and livelihoods are inevitable from such environmental The objective of the project, ‘Historically contaminated hazards but often underreported. sites ‘Incukalns acid tar ponds’ remediation works’, is to prevent the further discharge and dispersal of The aim of the project is to prevent further discharge of sulphuric acid tar waste and other pollutants into the pollutants, especially the sulphuric acid tar waste, groundwater, near-surface ground water, surface into groundwater, as well as to prevent the further water (in ditches), and soil and subsoil that is adjacent dispersal of the pollutants into near-surface to polluted sites. Since this project is being implemented groundwater, surface water (in ditches), and soil and over two EU programming periods (EU Structural subsoil adjacent to the polluted site. This will happen Funds programming periods 2007–2013 and 2014– in two phases. Phase I uses EU Structural Funds for 2020), this project is also divided into two phases (that the programming period of 2007–2013 and the is, Phase I and Phase II). Our approach for this BCA is Phase II programming period is 2014–2020. Case studies Chemical 213 Remediation works started in Phase I included the emission impacts of sulphur also comprise the removal of two deep boreholes that were used for acid same harmful chemicals. Therefore, we found it tar and a temporary coverage of the pond was also sound to include the value in our analysis. An installed before the commencing of Phase II. As Phase additional assumption made is that 50 percent of II is currently under way and data for the results was the people in the region of Vidzeme will have health not available, this case study focuses on Phase I costs impacts (conservative as there is a lack of data). and benefits of the intervention. The approach for this BCA is to compare the cost of the remediation project • Cost of sick/affected livestock avoided is based on in Phase along with the temporary treatment between information in Ethiopia on the impacts of effluents Phase 1 and 2 of this EU-funded (European to cattle—price adjusted to Latvia (Dadi, et al., Commission, 2011b). 2017). The assumption is that the context in Ethiopia will be applicable to cattle in Latvia. In Æ Methodology addition, information on the number of livestock in Latvia is scaled to the regional level to obtain values The methodology evaluates the cost of remediation to for this factor (USDA, 2016). the tar lagoons in Phase 1 as well as the pre-treatment of contaminated water and deposit or utilization of • Environmental costs avoided due to the temporary sludge derived from the treatment between Phase 1 coverage installed between Phase I and Phase II and 2 to the overall estimated benefit of remediation prevent leachate concentration in the ponds and and environmental clean-up. The methodology is not surrounding areas. The amount of polluted water time sensitive and does not include future costs or would increase the amount of contaminated water benefits per year but overall costs and benefits in the in the pond and gradually infiltrate through the lifetime of the capital investment with the data sides of the pond to increase groundwater pollution currently available. if the coverage is not undertaken. The estimated costs of pollution avoided are provided by the State The costs of the investment are found from the EU Environmental Agency and amount to approximately programming funds and description, and the cost of €384,000 per year. temporary treatment between Phase I and Phase II are provided by Latvia’s State Environmental Services. All Triple dividend 2 (unlocking economic potential): costs and benefits are in 2013 euros because this was the final year of the programming period. • Cost of land value reduction avoided is based on existing and estimated housing and value of housing The Triple Dividend Framework includes the following in the Vidzeme region in Latvia with the assumption benefits: that 31 percent of the land value of housing will decrease due to proximity to the toxic site. The data Triple dividend 1 (costs avoided): are from a study in the United States on Assessing the True Costs of Landfills (Hirshfeld, et al., 1992). • Lives saved from exposure to PM10 and NO2 from The assumption is that the percentage decrease in landfills and incinerators over individuals’ lifetimes. land value would be constant in the Latvian case. The assumption is that data from the WHO for the The value used is adjusted for the Latvian consumer Slovak Republic over a 20-year period of exposure price index from the United States. to landfills/incinerators could be applied to Latvia as they are similar countries in GDP (Forastiere, et al., • Jobs added are considered a benefit to the economy 2011). over the project period. The information on the number and types of jobs was provided to the • Health costs avoided are based on data from the members of the team by Latvia’s State Environmental European Public Health Alliance that estimates the Services. Jobs added included the assumption that cost per capita per country of pollution exposure. there is full employment in the country. For Riga City (capital of Latvia) where the toxic site is near, the approximate cost per person is €1,384 • Value added in construction is the macro-economic per person (De Bruyn & De Vries, 2020) While this benefit of construction works in remediation over cost is due to transportation-related pollutants, the Phase 1 of the project. The multiplier for each euro Case studies Chemical 214 of input in the investment to the macro-economic Table 86). While co-benefits likely exist in this case and output is taken from Eurostat symmetric input- others of environmental clean-up, data were output tables for Latvia. This is the EU-level €0.47 unavailable to appropriately quantify for this study. to the broader economy for €1 of investment into Therefore, the true triple dividend is likely the construction sector. underestimated in the per-year context in which the values are assessed and especially in a longer horizon Æ Results of the analysis by dividends where health costs avoided along with other direct and overall costs would contribute to the triple dividend cumulative value. Sensitivity analyses of low and high values of Environmental clean-up of the acid tar lagoon in Phase losses avoided, including rates of health costs, lives 1 of the EU investment to Latvia yields a high BCR lost, affected land value, and cattle/livestock affected, when considering the unlocked economic potential as result in a range of BCRs of 2.8–10.5 with the median well as direct losses avoided. (see Table 85 and BCR of 5.8. Table 85: BCR of cleaning up hazardous waste in Latvia (in million €) BCR: 5.8 BENEFITS COSTS Dividend 1 (€) 119.75 Dividend 2 (€) 62.45 Dividend 3 (€) Total benefits 182.19 Total costs 31.4 BCR 5.80 NPV (€) 150.79 ERR (%) 480.17 Source: World Bank analysis based on external data and information Case studies Chemical 215 Table 86: Expanded triple dividend BCR calculation for cleaning up hazardous waste in Latvia (in million €) ACID TAR LAGOON CLEAN-UP FIRST DIVIDEND (€) Lives saved due to remediation of site (long-term estimation) €114.1 M Health costs avoided €5.54 M Livestock lost avoided €0.12 M Total first dividend €119.75 M SECOND DIVIDEND (€) Land value reduced €48.43 M Input-output to economy from construction investment €12.17 M Jobs added €1.46 M Environmental damage avoided €0.38 M Total second dividend €62.45 M TOTAL DIVIDEND €182.2 M Total cost €31.4 M BCR 5.8 NPV €150.79 M ERR (%) 480.17% Source: World Bank analysis based on external data and information Æ Challenges faced and lessons learned Much data were extrapolated from other countries • Understanding productivity losses from agriculture with research and study on topics of toxic site impacts and other ecosystem services near area, to the Latvian case. In the future, the study could expand on the following: • Studying and including the actual cost of real estate value losses, • Determining Phase 1 and Phase 2 costs over a time horizon, • Including the cost of CO2 or other emissions and costs due to tar lagoons, • Evaluating actual impacts on health of communities living near tar lagoons for decades, • Evaluating current and future benefits of forestry in the area (Phase 2). Case studies Chemical 216 3.12. Multi-hazard 3.12.1. SUMMARY OF FINDINGS FOR MethodS for Europe (MATRIX) project (Scolobig, et al., MULTI-HAZARD RISKS 2014) suggests creating forums at the local level to In terms of multi-hazard risks, a cross-cutting approach foster discussions with researchers, practitioners, and encompassing disaster risk reduction and climate local advisors. change adaptation is vital to ensuring a comprehensive and cohesive effort for early warning, rescue and In this section, we have qualitatively and quantitatively emergency response, and climate adaptation demonstrated the benefits of multi-hazard investments initiatives. By ensuring that these DRM strategies are for enhancing rescue and emergency response and capable of performing a wide variety of functions that community-based mitigation approaches for climate address a multitude of hazards and are able to be change adaptation. The BCRs for the different types of implemented across border territories, researchers interventions are shown by a combination of and front-line respondents are able to leverage this conducting detailed case study analysis and reviewing versatility to their advantage. To bridge the gap past BCA, including both prospective and retrospective between research and practice, a deliverable report types of assessments. Table 87 summarizes main data for the New Multi-HAzard and MulTi-RIsK Assessment and information sources. Table 87: Overview of data and information sources for multi-hazard analysis INVESTMENT CASE STUDY DATA SOURCE NAME AND REFERENCE Participatory Methodologies Participatory Methodologies for Ex post, semi-quantitative assessment based on for Climate Change Adaptation Climate Change Adaptation in the external study Benefit-Cost Analysis in Portugal Climate Change Adaptation: The Use of Participatory Methodologies Source: World Bank based on external data and information Quantification of the long-term benefits of investments benefits of multi-hazard investments. However, in multi-hazards prevention is essential to fully present evidence tends to be scarce and BCA may not be the the cost-effectiveness of such investments. No formal right tool to assess these types of complex investments. BCA can be conducted for the EU project ‘New vehicles Conducting a comprehensive analysis of the effects of for voluntary fire service units’ since available research multi-hazard investments to determine how effective and data are limited on the true benefits of adding new these functional investments are for disaster response vehicles. While it improves the demand and provides could help inform policy. upgraded equipment in the short term, it is difficult to capture long-term benefits of the investment when Enhancing rescue and emergency response undertaking an economic assessment. equipment can support the effectiveness of response. A project in Poland supported the provision of Generally, there seems to be some indication of net equipment (European Commission, 2020h), and Case studies Multi-hazard 217 qualitative insights showed that they enhanced construction norms, as well as surveillance systems effectiveness of response, although an in-depth (BCRs 4.755, 4.74, 4.34, respectively). This could quantitative analysis would have to be undertaken. serve as a model for other cases analysing Moreover, digital databases and tools can support investments yielding mostly intangible benefits and early warning and effectiveness of response. A number to differentiate while combining short- and long- of investments were undertaken in Poland (European term benefits. Commission, 2015), Greece (European Commission, 2020i), Malta (European Commission, 2020j), and 3.12.2. RESCUE AND EMERGENCY Spain (European Commission, 2020k) that supported RESPONSE EQUIPMENT better decision-making, coordination platforms for enhanced response and minimized impacts, and were Purchasing advanced equipment and technology for even qualitatively stated to have wider social and rescue and emergency response allows emergency economic impacts by creating jobs or enhancing well- respondents to be adequately prepared to protect being. Multi-purpose green investments, particularly human lives, property, and the environment. Investing in urban areas, have been shown to yield positive net in multi-purpose equipment that can be used when benefits including improved resource efficiency, responding to a multitude of hazards is not only cost- increased aesthetic values, enhanced recreational effective but also convenient for municipalities values improved physical and mental health and job because the versatility of its utility can be easily creation, as exemplified in an EU Horizon 2020 maximized by emergency authorities and responders. research project URBAN GreenUP (UrbanGreenUp, Several countries have invested in equipment for 2020), or the development of the Budapest City Park improved preparedness and response, such as in (Maksimovic, 2017). Poland. In the context of sustainability and climate change Between 2016 and 2018, a project called “New adaptation, participatory methodologies and Vehicles for voluntary fire service units” was launched community-based mitigation approaches serve in Poland’s Lubelskie region (European Commission, essential roles, as individuals and communities are 2020h). The EU supported the purchase of 43 vulnerable to the effect of climate change. Innovative firefighting and rescue vehicles for voluntary fire participatory methods assist communities to services and other equipment necessary for emergency understand the causes and impact of climate change, rescue and post-disaster clean-up operations in enhance local capacity, and enable the application of Poland. These vehicles provide a high level of technical adaptation measures at community levels (Reid, et al., support for 1,753 voluntary fire services spanning 2019). As a part of the EU research project ‘Bottom- 60,000 firefighters, which consequently improves the Up Climate Adaptation Strategies Towards a speed and efficiency of local rescue and firefighting Sustainable Europe’ (BASE) (2016), a study was operations in municipalities throughout Lubelskie. As undertaken to examine the effectiveness of a result, it is possible to significantly mitigate many participatory methods for 22 European cities, and it adverse effects related to fires, forest fires, floods, concludes that participation can enhance the process serious industrial accidents, and other incidents that of climate adaptation by improving economic threaten life and health. Such efforts bolster protection efficiency, community unity, and environmental of human life and property while enhancing safety and integration and evaluation (Clemmensen, et al., 2015). preventing the degradation of the natural environment, thus benefitting all 2.14 million inhabitants in the • Case study 29 (external analysis, ex post (Alves F., region. The total investment of the project is €7.51 2015)): An analysis of an urban-focused climate million, and €4.28 million was funded by EU. As a adaptation program in Cascais, Portugal, showed result of this investment, a population of 36,750 people interesting results from a study using participatory are benefitting from increased forest fire protection BCA (PBCA) methodologies. The emphasis of the measures and 289,818 people are benefitting from method is more on the process than the results, as other disaster recovery methods besides fire and it considers as beneficial the fact that populations flooding. have been engaged in the analysis. Highest BCRs were found for reforestation (particularly due to Since there is limited qualitative information provided long-term benefits), legislation towards bioclimatic by department contacts regarding the improvement of Case studies Multi-hazard 218 services due to the addition of the new vehicles, no no indication on how the 43 trucks were formal BCA has been conducted for the project. In distributed to the various stations, which is an general, research is limited on the true benefits of important aspect of the efficiency in reducing losses adding new vehicles; while it improves the demand based on the vulnerability to fires in areas in and provides upgraded equipment in the short-term, it Lubelskie region.  is difficult to capture long-term benefits using the triple-dividend methodology. To expand on this study 3.12.3. MULTI-HAZARD EARLY WARNING in the future, the following should be considered: SYSTEMS • Assess the improved response time due to new fire In the digital era, EWS often incorporate online databases vehicles, and digital tools that record available rescuing resources and provide real-time information on disasters. The use • Assess the number of fire starts reduced, or fire of digital tools increases the efficiency and effectiveness damage reduced along with casualties reduced of the authority’s response to disasters and public since the new vehicles were introduced in 2017, awareness. Some examples include the IT system for hazard protection in Poland, the Aegis Intelligent System • A more comprehensive solution would be to develop that improves Greece’s responses to disasters, Malta’s a radial plan based on the spatial fabric of the high-tech mapping equipment for disaster, and the cross- region. This includes identifying s emergency border early warning networks across Spain and Portugal. routes, critical facilities, dense and vulnerable More information on the use of digital tools for multi- buildings, as well as critical infrastructure. There is hazard EWS is included in Box 17 below. Box 17: The use of digital tools in the early warning of disasters The following examples showcase how the mplementation As a part of the country’s national digital strategy, an EU of digital tools supports the effectiveness of EWS and project (European Commission, 2020j) was implemented in generates additional benefits to the society. Malta with an emphasis on data management and the use of hi-tech mapping equipment. The project creates 3D maps Established in Poland, the project “IT system for protection of the nation’s geography and infrastructure, which provide against extraordinary hazards (ISOK)” (European not only valuable information on town planning to non- Commission, 2015) is an innovative system that decreases governmental, external users, but also important data for losses from floods, improves land development, and effective responses during a disaster, such as the strike of increases the public’s sense of security and the efficiency of an earthquake or tsunami. The project generates positive crisis management responses. The system was built at a social and economic impacts by boosting Malta’s economic cost of €75.54 million, and it allows Poland to meet the EU’S growth, creating new, specialized careers in the government requirements on flood prevention. It provides valuable and based on spatial qualifications, increasing sustainability, useful IT and communication resources for decision-making and improving the wellbeing of the citizens. when disasters and hazards occurs and also 40 new and permanent jobs. With the objective to manage and use resources efficiently during the occurrence of natural disasters such as forest The Aegis Intelligent System (European Commission, 2020i) fires, floods and erosion, the EU project ARIEM+ (European is an innovative tool that enables Greece’s North Aegean Commission, 2020k) was launched under the collaboration Region and Cyprus to have more efficient and effective between the Spanish regions of Galicia and Castile and Leon responses when a natural disaster strikes. The system was and those in northern Portugal. The project developed early built with a total investment of €0.92 million It provides a warning networks as part of its environmental monitoring database that records available resources and equipment systems that highlights risks in the region, which improves such as disaster vehicles and medicine and first aid supplies response coordination between nations and maintains so that they can be mobilized immediately in a disaster. At efficient communications in response to disasters. By doing the same time, it also provides a platform that allows so, they hope to shorten response times on both sides of the authorities, first responders, and the public to visualize the Portugal/Spain border to prevent forest fire or flood disasters location and impacts of the disaster. and minimize their impact on human lives, property, and the environment. Case studies Multi-hazard 219 3.12.4. PARTICIPATORY METHODOLOGIES community, which helps policy making and actions in FOR CLIMATE CHANGE ADAPTATION future climate adaptation (Ross, et al., 2015). Individuals and communities are vulnerable to the effect of climate change. As a result, it is crucial to As a part of the EU research project BASE (2016), a integrate participatory tools and community-based study was undertaken to examine the participatory mitigation approaches into DRR in the context of and methods and process for 22 European BASE case sustainability and climate change adaptation studies. The main goal of the study is to explore the (Laukkonen, et al., 2009). Innovative participatory significance and effectiveness of participation methods assist communities to understand the causes methods in the context of climate change adaptation. and impact of climate change, enhance local capacity, The study concludes that participation can and enable the application of adaptation measures at enhance the process of climate adaptation by community levels (Reid, et al., 2019). In addition, a improving economic efficiency, community unity, and study from Australia has also shown that participatory environmental integration and evaluation methods are effective and beneficial in terms of (Clemmensen, et al., 2015). creating shared knowledge and empathy in the PARTICIPATORY METHODOLOGIES FOR CLIMATE CHANGE ADAPTATION This case study is an external analysis that was and training and awareness campaigns would support undertaken with ex-post assessments and semi- the resilience of municipal staff and civil society. quantitative methods to estimate benefits from interventions. Æ Methodology Æ Introduction and background This is a literature review of an existing research looking at the inclusion of participatory processes in The municipality of Cascais in Portugal is highly conducting BCA for appraising projects as an dependent on climatic conditions for its economic alternative or supplement to traditional BCAs. It uses activities (particularly tourism) yet highly vulnerable to the PBCA to evaluate the benefits of climate change climate change impacts and disasters such as floods, activities in Cascais, Portugal. This case reviews the wildfires, droughts, and heatwaves (BASE, 2014). The following study on the BCA in climate change municipality became one of the first ones in the country adaptation with the use of participatory methodologies in 2010 to develop a local Strategic Plan for Climate (Alves, 2015). Change in consultation with experts that ranked adaptation measures according to vulnerability, risk Æ Results of the analysis by dividends assessments, and potential benefits. and overall Æ Description The study finds that climate change adaptation planning and intervention requires a holistic review of The BASE (2016) project from 2012 to 2016 focused the complex interdependencies in time and space. A on the development of ‘Green Corridors’ in the PBCA is an economic appraisal tool which has been municipality through the rehabilitation of the existing developed and tested by the centre for climate impact, riparian galleries and the unification of the parks, modelling and adaptation (CCIAM) from the university gardens, and florists, a connected and integrated of Lisbon, under FP7 Project BASE. PBCA aims to green infrastructure. This was supposed to reduce the combine the advantages and strengths of MCA with city vulnerability to floods as well as heatwaves while at the rationality of BCA. The PBCA as applied to the same time contributing to a greater quality of living investment measures in Cascais, Portugal, being and increased sustainability of the municipality. explored for climate change adaptation is listed in Moreover, the city wanted to enhance water savings in Table 88. distribution (water waste from 17 percent to 6 percent) Case studies Multi-hazard 220 Table 88: Value of various participatory climate adaption measures Source: Alves, et al. (2015) After running the PBCA tool in three separate represent a one-hour add-on to the program with workshops with more than 40 participants, the key minimum marginal costs. findings regarding the methodology were as follows: • It allows stakeholders to point in the right direction • The emphasis of this method is more about the regarding the most important effects of an action if process than the result itself as people engaged deeper BCA is needed for quantitative valuation. seriously in technical and also ethical/moral debates with great sharing but then disregard the final Æ Challenges faced and lessons learned present value. This unique methodology could be employed in other • It can lead to counter-literature, but intuitive, case studies where a WTP approach is assessed for results, such as the selection of negative discount long-term investments for mitigating the negative rates for some particular adaptation measures in consequences of climate change. The PBCA tool could some groups. be applied before a full data-based BCA to potentially rule out investments that participants (stakeholders) • Simple to use and understand, mainly if there is may evaluate as non-starters. More research should good facilitation/focalization of the debate. be conducted on the validity and usefulness of this approach, evaluating the possible beneficial outcomes • The introduction of the time factor and the inherent to such a study in lieu of or as a supplement to a use of a discount rate enriches the debate and traditional BCA. contributes significantly to the usefulness and maturation of the tool. 3.12.5. LOCAL MULTI-PURPOSE GREEN INVESTMENTS • The impact measurement scale (1 to 5) was considered too short to clearly distinguish between In the past few decades, urbanization has taken place in adaptation measures and a (1 to 10) scale has been Europe rapidly, causing environmental problems proposed for future workshops. including air and water pollutions and the loss of biodiversity. At the same time, cities are negatively • Inexpensive to use and implement as it can be affected by the effect of climate change, which applied in the context of an existing workshop and increases the severity and frequency of natural Case studies Multi-hazard 221 hazards such as droughts, floods, and extreme heat. climate change. Other benefits of such investments In this context, implementing nature-based, blue green include improving resource efficiency, increasing solutions in cities is viewed as an effective and promising aesthetic value for properties, creating areas for approach to offset the negative impacts of urbanization recreational purposes, and creating jobs (Maksimovic, and enhance sustainability as well as urban resilience to 2017) (see Figure 48 below). Figure 48: Benefits of NBS in urban environments Source: Maksimovic (2017) In Europe, investments in blue green measures have examples of such investments are showcased in more yielded promising results and inspirations. Some detail in Box 18 below. Box 18: Examples of investments in urban blue green infrastructure A review of investments in blue green infrastructure in cities Spain, Liverpool of the UK, and Izmir of Turkey) and will take across Europe provided several lessons learned and place across Europe, Latin America, and Asia in the future. inspiring achievements outlined below. A common theme is Covering about 100 hectares, the Budapest City Park of that the two investments improve the cities’ adaptation to Hungary is a multi-functional area redeveloped with the climate change while enhance their sustainability. goal to create a sustainable urban metabolism system (Maksimovic, 2017). To achieve the goal, a systematic Funded under the EU’s Horizon 2020 research and analysis of the water, energy and waste flow was conducted innovation programme, URBAN GreenUP (2020) is a project for the park by the design team of the project. The park is that promotes the use of NBS in urban areas to reduce the expected to mitigate the effect of urban heat and heavy negative impact of climate change and improve air and participation and is estimated to yield a 35 percent saving in water quality. It provides digital tools to assist policymakers energy and 95 percent saving in water and reduce waste by and city planners to choose the most effective NBS based 65 percent. The overall payback time of the project is less on a city’s capacity and the expected outcomes. The project than 6 years comparing to the cost of the infrastructure. is currently on-going in three European cities (Valladolid of Case studies Multi-hazard 222 4. Bibliography DPPI SEE, 2020. Post Disaster Needs Assessment and Disaster Recovery Framework Training Workshop. Sarajevo, Bosnia and Herzegovina, s.n. AGIF, 2020. Activities Report 2019 – Agency for the Management System for Rural Fires, Portugal, s.l.: s.n. Alberici, S. et al., 2014. Subsidies and costs of EU energy: final report Ecofys, by order of: European Commission., s.l.: European Commission. Alcik, H., Ozel, O., Apaydin, N. & Erdik, M., 2009. A study on warning algorithms for Istanbul earthquake early warning system.. Geophysical Research Letters, Volume 36(5). Alice Accelerate Innovation, 2018. ALICE project promoted in flood management campaign in Athens, Greece (15- 17/9/2018). [Online] Available at: https://www.alice-wastewater-project.eu/news/40-alice-project-promoted-in-flood-management- campaign-in-athens-greece-15-17-9-2018 Alves, F., 2015. Benefit-Cost Analysis in Climate Change Adaptation: The Use of Participatory Methodologies, s.l.: Universidade NOVA de Lisboa. Åström, C. et al., 2013. Heat-related respiratory hospital admissions in Europe in a changing climate: a health impact assessmen. BMJ open, Volume 3(1). Augusto, S. et al., 2020. Population exposure to particulate-matter and related mortality due to the Portuguese wildfires in October 2017 driven by storm Ophelia. Environment International, Volume 144, p. 106056. Baranovskiy, N. V., 2019. Predicting, Monitoring, and Assessing Forest Fire Dangers and Risks. Russia: National Research Tomsk Polytechnic University. Barbier, E., 2007. Valuing ecosystem services as productive inputs.. Economic Policy, Volume 49, pp. 178-229. BASE, 2014. Cities and Infrastructures - Case-study: Cascais Municipality (FFCUL, Portugal), s.l.: BASE. BASE, 2016. About BASE. [Online] Available at: https://base-adaptation.eu/about-base BASE, 2016. Participatory Review of the Strategic Adaptation Plan (Cascais, Portugal). [Online] Available at: https://base-adaptation.eu/participatory-review-strategic-adaptation-plan-cascais-portugal Bassil, K. & Cole, D., 2010. Effectiveness of public health interventions in reducing morbidity and mortality during heat episodes: a structured review. International journal of environmental research and public health, Volume 7(3), pp. 991-1001. Bautista, H. & Rahman, K. M. M., 2016. Review On the Sundarbans Delta Oil Spill: Effects On Wildlife and Habitats. International Research Journal, Volume 1 (43), p. 93–96. BBC News, The Visual and Data Journalism Team, 2020. Covid map: Coronavirus cases, deaths, vaccinations by country.. [Online] Available at: https://www.bbc.com/news/world-51235105 BBC, 2018. Greece Wildfires: Dozens dead in Attica region. [Online] Available at: https://www.bbc.co.uk/news/world-europe-44932366 Bebbington, M. & Zitikis, R., 2015. Dynamic Uncertainty in Benefit-Cost Analysis of Evacuation Prior to a Volcanic Eruption. Mathematical geosciences, Volume 48(2). Becker, J. et al., 2020. Scoping the potential for Earthquake Early Warning in Aotearoa New Zealand: a sectoral analysis of perceived benefits and challenges. International Journal of Disaster Risk Reduction, Volume 51, p. 101765. Bennett, M. et al., 2010. Reducing fire risk on your forest property. s.l.:Oregon State University. Berardi, U., GhaffarianHoseini, A. & GhaffarianHoseini, A., 2014. State-of-the-art analysis of the environmental benefits of green roofs. Applied Energy, Volume 115, pp. 411-428. Bianchini, F. & Hewage, K., 2012. Probabilistic social Benefit-Cost Analysis for green roofs: a lifecycle approach. Building and environment, Volume 58, pp. 152-162. Bibliography 223 Bielsa-aragnouet, 2018. SECURUS 1 European Project, s.l.: Bielsa-aragnouet. Bishop, A. & Burgess-Gamble, L., 2018. Working with Natural Processes – Evidence Directory: Case study 55. Sandwich Tidal Defence Scheme, s.l.: Environment Agency. BIZEE, 2020. Degree days, weather data for energy professionals. [Online] Available at: https://www.degreedays.net/ Blake, D. et al., 2017. Impact of Volcanic Ash on Road and Airfield Surface Skid Resistance, s.l.: Sustainability. 9. 1389. 10.3390/su9081389. Blumenschein, K. et al., 2008. Eliciting willingness to pay without bias: evidence from a field experiment. The Economic Journal, Volume 118(525), pp. 114-137. BOEM, 2016. Economic Analysis Methodology for the 2017-2022 Outer Continental Shelf Oil and Gas Leasing Program, s.l.: BOEM. Bordoni, M. et al., 2018. Estimation of the susceptibility of a road network to shallow landslides with the integration of the sediment connectivity. Natural Hazards and Earth System Sciences, Volume 18(6), pp. 1735-1758. Bos, F. & Zwaneveld, P., 2017. Cost-Benefit Analysis for Flood Risk Management and Water Governance in the Netherlands: An Overview of One Century. SSRN Electronic Journal. Botzen, W. J., Aerts, J. C. & van den Bergh, J. C., 2009. Willingness of homeowners to mitigate climate risk through insurance. Ecological Economics, Volume 68(8-9), pp. 2265-2277. Bouchama, A., 2004. The 2003 European heat wave. Intensive care medicine, Volume 30(1), pp. 1-3. Braathen, N. A., Lindhjem, H. & Navrud, S., 2009. Valuing Lives Saved from Environmental, Transport and Health Policies: A Meta-Analysis of Stated Preference Studies, Paris: OCED. Bretz, S. A. H. a. R. A., 1998. Practical issues for using solar-reflective materials to mitigate urban heat islands. Atmospheric environment, Volume 32(1), pp. 95-101. Brzev, S. et al., 2013. GEM Building Taxonomy, s.l.: GEM Technical Report. Bundesministerium für Nachhaltigkeit und Tourismus, 2018. Bundesministerium für Nachhaltig. [Online]. Burgess-Gamble, L. et al., 2018. Working with Natural Processes – Evidence Directory, s.l.: Environment Agency. Bux, K., 2006. Klima am Arbeitsplatz: Stand arbeitswissenschaftlicher Erkenntnisse; Bedarfsanalyse für weitere Forschungen; Forschung Projekt F 1987, s.l.: BAuA. Caballero, D., Beltran, I. & Velasco, A., 2007. orest Fires and Wildland-Urban Interface in Spain: Types and Risk Distribution. Caetano, M., Igreja, C. & Marcelino, F., 2010. Carta de Uso e Ocupação do Solo de Portugal Continental para 2018, s.l.: s.n. Cammalleri, C. et al., 2020. Global Warming and Drought Impacts in the EU, Luxembourg: Publications Office of the European Union. Cardone, D., Gesualdi, G. & Perrone, G., 2019. Benefit-Cost Analysis of alternative retrofit strategies for RC frame buildings. Journal of Earthquake Engineering, pp. 208-241. Carmona, M. et al., 2017. Assessing the effectiveness of Multi-Sector Partnerships to manage droughts: The case of the Jucar river basin. Earth’s Future, Volume 5, pp. 750-770. Casanueva, A. et al., 2019. Overview of existing heat-health warning systems in Europe. International journal of environmental research and public health, Volume 16(15), p. 2657. CCDRC, 2020. Comissão de Coordenacão e Desenvolvimento Regional do Centro. [Online] Available at: https://www.ccdrc.pt/ CDC, 2016. 2014-2016 Ebola Outbreak in West Africa, s.l.: s.n. Chiabai, A., Spadaro, J. & Neumann, M., 2018. Valuing deaths or years of life lost? Economic benefits of avoided mortality from early heat warning systems. Mitigation and adaptation strategies for global change, Volume 23(7), pp. 1159-1176. Clark, C., Adriaens, P. & Talbot, F., 2008. Green roof valuation: a probabilistic economic analysis of environmental benefits. Environmental science & technology, Volume 42(6), pp. 2155-2161. Clemmensen, A. H. et al., 2015. Participation in Climate Change Adaptation, s.l.: BASE Repot. Bibliography 224 Climate Change Post, 2020. Avalanches, Landslides and Rock fall Switzerland. [Online] Available at: https://www.climatechangepost.com/switzerland/avalanches-and-landslides/ Climate Change Post, 2021. Flash floods and urban flooding: European scale. [Online] Available at: https://www.climatechangepost.com/europe/flash-floods-and-urban-flooding/ Climate-ADAPT, 2018. Ceramic Sustainable Urban Drainage System (LIFE CERSUDS). [Online] Available at: https://climate-adapt.eea.europa.eu/metadata/projects/ceramic-sustainable-urban-drainage- system Clinton, J. Z. A. M. A. Z. C. a. P. S., 2016. State-of-the art and future of earthquake early warning in the European region. Bulletin of Earthquake Engineering, Volume 14(9), pp. 2441-2458. Comissao Tecnica Independente, 2017. Analysis of the facts relating to the fires which occurred in Pedrogao Grande, Castanheira de Pera, Ansião, Alvaiázere, Figueiró dos Vinhos, Arganil, Gois, Penela, Pampilhosa da Serra, Oleiros and Sertã between 17 and 24 June 2017, s.l.: Comissao Tecnica Independente. Copernicus, 2021. Climate Change. [Online] Available at: https://www.copernicus.eu/en/copernicus-services/climate-change CORDIS, 2020. Forest fire spread prevention and mitigation. [Online] Available at: https://cordis.europa.eu/project/id/EVG1-CT-2001-00043 Coreau, A., 2020. LIFE IP ARTISAN - ”Achieving Resiliency by Triggering Implementation of nature-based Solutions for climate Adaptation at a National Scale”, s.l.: s.n. Corrigan, J. R. E. K. J. &. D. J. A., 2009. Aesthetic values of lakes and rivers. In: Encyclopedia of Inland Waters. s.l.: Elsevier Inc, pp. 14-24. Covenant of Mayors, 2021. Technical annex to the SEAP template instructions document: The Emission Factors, s.l.: Covenant of Mayors. Cremen, G., Galasso, C. & Zuccolo, E., 2020. Towards earthquake early warning across Europe: Probabilistic quantification of available warning times and their risk-mitigation potential, s.l.: Earth and Space Science Open Archive ESSOAr. Crowley, H. et al., 2020. Exposure model for European seismic risk assessment. Earthquake Spectra, 36(1), p. 252–273. Crowley, H. et al., 2018. Towards a uniform earthquake risk model for Europe, Thessaloniki, Greece: 16th European Conference on Earthquake Engineering. CTCN, 2020. Early warning systems for droughts. [Online] Available at: https://www.ctc-n.org/technologies/early-warning-systems-droughts Currie, B. & Bass, B., 2010. Using green roofs to enhance biodiversity in the City of Toronto, Toronto: City of Toronto Commissioned Report: April. Dadi, D. et al., 2017. Environmental and health impacts of effluents from textile industries in Ethiopia: the case of Gelan and Dukem. Volume 189(1), p. 11. Dagmar, E., 2001. Comparative methodologies for estimating on-water Response costs for marine oil spills, s.l.: international Oil Spill Conference Proceedings. Dagmar, E., 2004. Modelling Oil Spill Response and Damage Costs, Cortlandt Manor, NY, USA: Environmental Research Consulting. Dang, T. et al., 2018. Green space and deaths attributable to the urban heat island effect in Ho Chi Minh City. American journal of public health, Volume 108(S2), pp. S137-S143. Database AT, 2021. Database for educational facilities Austria, s.l.: s.n. Database CY, 2021. Database of educational facilities in Cyprus, s.l.: s.n. Database IT, 2021. Database of educational facilities in Italy, s.l.: s.n. Database RO, 2021. Database of educational facilities in Romania, s.l.: s.n. Database SK, 2021. Database of educational facilities in Slovakia, s.l.: s.n. Database SL, 2021. Database of educational facilities in Slovenia, s.l.: s.n. David, P., 2000. Valuing risks to life and health in EU and Accession States, Brussels: European Commssion. De Bruyn, S. & De Vries, J., 2020. Health costs of air pollution in European cities and the linkage with transport, s.l.: CE Delft. Bibliography 225 De Natale, G. et al., 2017. Understanding volcanic hazard at the most populated caldera in the world: Campi Flegrei, Southern Italy.. Geochem. Geophys. Geosyst., Volume 18, p. 2004– 2008. De Rigo, D. et al., 2017. Forest fire danger extremes in Europe under climate change: variability and uncertainty. PESETA III project - Climate Impacts and Adaptation in Europe, focusing on, s.l.: Publications Office of the European Union. De’Donato, F. et al., 2015. Changes in the effect of heat on mortality in the last 20 years in nine European cities. Results from the PHASE project.. International journal of environmental research and public health, Volume 12(12), pp. 15567-15583. Dhubháin, Á. F. M. M. R. a. O. D., 2009. Assessing the value of forestry to the Irish economy—an input–output approach. Forest Policy and Economics, Volume 11(1), pp. 50-55. Dimitrova, L., Solakov, D., Simeonova, S. & Aleksandrova, I., 2015. System of Earthquakes Alert (SEA) in the Romania-Bulgaria cross border region. Bulg Chem Commun, Volume 47(B), pp. 390-396. Dolce, M., 2012. The Italian National Seismic Prevention Program, s.l.: 15 WCEE LISBOA 2012. Dolce, M., Bramerini, S. C. & Naso, G., 2019a. The Italian policy for Seismic Microzonation, Rome, Italy: 7th lnternational Conference on Earthquake Geotechnical Engineering (VII ICEGE). Dolce, M. et al., 2019. Attuazione del Piano nazionale italiano per la prevenzione del rischio sismico: l’adeguamento degli edifici strategici e rilevanti, Ascoli Piceno: XVIII Convegno ANIDIS “l’Ingegneria Sismica in Italia”. Donaldson, G., Kovats, R., Keatinge, W. & McMichael, A., 2001. Heat-and cold-related mortality and morbidity and climate change. Health effects of climate change in the UK, pp. 70-80. Dutch Water Management, 2020. Delta Works. [Online] Available at: https://www.dutchwatermanagement.com/delta-works-1997-netherlands ECHO, 2014. H2020 – Prevention and Preparedness in Civil Protection: Deliverable D.4: Cost-benefit analysis of mitigation measures to pilot firms/infrastructures in Italy, s.l.: ECHO. Ecker, M. & Hrebik, F., 2012. Machland Dam - Structure of the Century in Record Construction Completion Time, s.l.: World of PORR. ECONADAPT, 2015. The costs and benefits of adaptation: Results from the ECONADAPT project., s.l.: ECONADAPT consortium. EEA, 2004. Impacts of Europe’s Changing Climate: An Indicator-based Assessment (No. 2-2004), s.l.: European Communities. EEA, 2017. Green Infrastructure and Flood Management: Promoting cost-efficient flood risk reduction via green infrastructure solutions, s.l.: Publications Office of the European Union, European Environment Agency. EEA, 2017. Urban areas at risk of river flooding. [Online] Available at: https://www.eea.europa.eu/data-and-maps/figures/share-of-the-citys-urban-1 EEA, 2019. Floodplains: a natural system to preserve and restore. EEA report No 24/2019. https://www.eea.europa.eu/ publications/floodplains-a-natural-system-to-preserve-and-restore#:~:text=Floodplains%20are%20part%20 of%20Europe’s,floodplains%20have%20been%20environmentally%20degraded. EEA, 2020b. Urban Adaptation in Europe: How Cities and Towns Respond to Climate Change, Luxembourg: Urban Adaptation in Europe: How Cities and Towns Respond to Climate Change. EEA, 2020. Deaths related to flooding in Europe. [Online] Available at: https://www.eea.europa.eu/data-and-maps/figures/people-per-million-population-affected-4 EEA, 2020. Forest Fire. [Online] Available at: https://www.eea.europa.eu/data-and-maps/indicators/forest-fire-danger-3/assessment EFFIS, 2021. EFFIS - Welcome to EFFIS. [Online] Available at: https://effis.jrc.ec.europa.eu/ Elin, A., Stoica, D. & Iversen, K., 2001. Oil Pollution in the Baltic Sea and the Effects on Fish and Fisheries., s.l.: Environmental Studies, Aarhus University. Emerton, R. et al., 2016. Continental and global scale flood forecasting systems. Volume 3. EMSA, 2021a. Legal Foundation. [Online] Available at: http://www.emsa.europa.eu/about/legal-basis.html Bibliography 226 EMSA, 2021b. Operational Pollution Response Services.. [Online] Available at: http://www.emsa.europa.eu/we-do/sustainability/pollution-response-services.html EPA, 2020. What is Green Infrastructure. [Online] Available at: https://www.epa.gov/green-infrastructure/what-green-infrastructure EPRS, 2020. Attica Region. [Online] Available at: https://what-europe-does-for-me.eu/en/portal/1/EL3 Erma, A. et al., 2020. From Poverty to Disaster and Back: A Review of the Literature. Economics of Disasters and Climate Change, Volume 4, p. 171–193. Ernst, C. & Blaha, K., 2015. Decision support tools for climate change planning, s.l.: The Trust for Public Land. EU Science Hub, 2016. Nuclear Safety. [Online] Available at: https://ec.europa.eu/jrc/en/research-topic/nuclear-safety European Commission, 2007. Guidelines for Benefit-Cost Analysis methodology. New programming period 2007-2013, s.l.: European Commission. European Commission, 2007. Redeveloped road to upgrade volcano escape route. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/major/italy/redeveloped-road-to-upgrade- volcano-escape-route European Commission, 2011b. A multifunctional ship to tackle marine pollution in Estonia. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/major/estonia/a-multifunctional-ship-to-tackle- marine-pollution-in-estonia European Commission, 2011. Capturing River Flows to Improve Water Supplies. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/major/portugal/capturing-river-flows-to-improve- water-supplies. European Commission, 2011. Clean-up at uranium processing plant. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/major/czechia/clean-up-at-uranium-processing- plant European Commission, 2012. Testing the future of sustainable nuclear energy. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/major/czechia/testing-the-future-of-sustainable- nuclear-energy European Commission, 2013a. Fighting floods in Malta. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/major/malta/fighting-floods-in-malta European Commission, 2013b. Stopping Athens Floods. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/greece/stopping-athens-floods European Commission, 2014. Guide to Benefit-Cost Analysis of Investment Projects. Economic appraisal tool for Cohesion Policy 2014-2020, s.l.: European Commission. European Commission, 2015. A high speed earthquake response system in the Romania-Bulgaria border region. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/romania/a-high-speed-earthquake-response- system-in-the-romania-bulgaria-border-region European Commission, 2015. Protection from extraordinary hazards in Poland. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/major/poland/protection-from-extraordinary- hazards-in-poland European Commission, 2016b. Funding Opportunities to Support Disaster Risk Prevention in the Cohesion Policy 2014–2020 Period, s.l.: European Commission. European Commission, 2017. Long-term renovation strategies - Energy, s.l.: s.n. European Commission, 2017. Spanish-Portuguese Meterological information system for trans-boundary operations in forest fires (SPITFIRE). [Online] Available at: https://nam03.safelinks.protection.outlook.com/GetUrlReputation%22https:/nam03.safelinks. protection.outlook.com/GetUrlReputation European Commission, 2018. Climate change adaptation of major infrastructure projects - A stock-taking of available resources to assist the development of climate resilient infrastructure. [Online] Bibliography 227 Available at: https://ec.europa.eu/regional_policy/en/information/publications/studies/2018/climate-change- adaptation-of-major-infrastructure-projects European Commission, 2018. Enhanced monitoring of volcanic activity across Macaronesia. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/Portugal/enhanced-monitoring-of-volcanic- activity-across-macaronesia European Commission, 2019b. Comprehensive study of building energy renovation activities and the uptake of nearly zero-energy buildings in the EU - Final Report, s.l.: s.n. European Commission, 2019c. Basilica of St. Benedict in Norcia, Italy to be rebuilt following earthquake damage.. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/Italy/basilica-of-st-benedict-in-norcia- italy-to-be-rebuilt-following-earthquake-damage European Commission, 2019. iRESIST+ - innovative seismic and energy retrofitting of the existing building stock. [Online] Available at: https://ec.europa.eu/jrc/en/research-topic/improving-safety-construction/i-resist-plus European Commission, 2019. New flood-prevention infrastructure helps keep Malta safe and dry. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/malta/new-flood-prevention-infrastructure-helps- keep-malta-safe-and-dry European Commission, 2019. safEarth: Improving risk prevention from landslides and flash floods. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/Croatia/safearth-improving-risk-prevention-from- landslides-and-flash-floods European Commission, 2020a. Commission Staff Working Document Evaluation: Ex post evaluation of major projects in environment financed by the European Regional Development Fund and the Cohesion Fund between 2000 and 2013, s.l.: European Commission. European Commission, 2020c. Communication from the commission to the European Parliament, the Council, the European Economic and Social Committee and the Committee of the Regions. [Online] Available at: https://ec.europa.eu/info/sites/info/files/communication-european-health-union-resilience_en.pdf European Commission, 2020. Cross-border ‘Grande Région’ builds coordinated response to emergencies. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/France/cross-border-grande-region-builds- coordinated-response-to-emergencies European Commission, 2020d. Integrated techniques for the seismic strengthening and energy efficiency of existing buildings. [Online] Available at: https://ec.europa.eu/jrc/en/event/webinar/integrated-techniques-seismic-strengthening-and- energy-efficiency-existing-buildings European Commission, 2020d. Preparedness and Response Planning: Health security and infectious diseases. [Online] Available at: https://ec.europa.eu/health/security/preparedness_response_en European Commission, 2020e. COVID-19: Commission creates first ever rescEU stockpile of medical equipment. [Online] Available at: https://ec.europa.eu/commission/presscorner/detail/en/ip_20_476 European Commission, 2020. EU Buildings Database - Energy, s.l.: s.n. European Commission, 2020f. Chemicals strategy for sustainability. [Online] Available at: https://ec.europa.eu/environment/strategy/chemicals-strategy_en European Commission, 2020g. Major accident hazards. [Online] Available at: https://ec.europa.eu/environment/seveso/ European Commission, 2020h. New vehicles for voluntary fire service units in Poland’s Lubelskie region. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/Poland/new-vehicles-for-voluntary-fire-service- units-in-polands-lubelskie-region European Commission, 2020i. Greek project develops intelligent system for better disaster responses. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/Greece/greek-project-develops-intelligent- system-for-better-disaster-response European Commission, 2020. Impacts and Risk from High-end Scenarios: Strategies for Innovative Solution. [Online] Available at: http://www.impressions-project.eu/ European Commission, 2020j. Updating Malta’s maps and spatial data: a cutting-edge tool for government and citizens. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/Malta/updating-maltas-maps-and- spatial-data-a-cutting-edge-tool-for-government-and-citizens Bibliography 228 European Commission, 2020k. Interregional mutual assistance in emergencies and cross-border risks. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/Portugal/interregional-mutual-assistance-in- emergencies-and-cross-border-risks European Commission, 2020l. Integrated flood services and climate change awareness for eastern Mediterranean islands. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/Cyprus/integrated-flood-services-and-climate- change-awareness-for-eastern-mediterranean-islands European Commission, 2021. Building a dynamic EU response to earthquakes. [Online] Available at: https://cordis.europa.eu/project/id/821046 European Commission, 2021. Energy efficiency directive | Energy (europa.eu). [Online] Available at: https://ec.europa.eu/energy/topics/energy-efficiency/targets-directive-and-rules/energy-efficiency- directive_en European Commission, 2021. LIFE programme. [Online] Available at: https://ec.europa.eu/easme/en/life European Commission, 2021. Overview - Eurostat. [Online] Available at: https:/ec.europa.eu/eurostat/web/esa-supply-use-input-tables/overview European Commission, n.d. Acid waste lagoons to be cleaned for good. [Online] Available at: https://ec.europa.eu/regional_policy/en/projects/major/latvia/acid-waste-lagoons-to-be-cleaned- for-good%22https:/ec.europa.eu/regional_policy/en/projects/major/latvia/acid-waste-lagoons-to-be-cleaned- for-good European Union, 2013a. EU Countries 2013 Cost-optimal reports, Part 1, s.l.: s.n. European Union, 2013b. EU Countries 2013 Cost-optimal reports, Part 2, s.l.: s.n. European Union, 2018. EU Countries 2018 Cost-optimal Reports - Energy, s.l.: s.n. European Union, 2019. GRETA - GReen infrastructure: Enhancing biodiversity and ecosysTem services for territoriAl development. Final Report 08/08/2019. https://www.espon.eu/green-infrastructure European Union, 2020. Danube Cross-border System for Earthquake Alerts. [Online] Available at: https://keep.eu/projects/6026/ European Union, 2020. Keeping cool: How Europe is using natural solutions to fight heatwaves. [Online] Available at: https://europa.eu/euprotects/our-health/keeping-cool-how-europe-using-natural-solutions-fight- heatwaves_en European Union, 2020. Safe Borderland. [Online] Available at: https://keep.eu/projects/21999/ European Union, 2021. Danube Cross-border System for Earthquakes Alert. [Online] Available at: https://keep.eu/projects/6026/ European Union, 2021. European Association of Earthquake Engineering (EAEE). [Online] Available at: https://www.preventionweb.net/organizations/3415 European Union, 2021. Eurostat Database, s.l.: s.n. Fabozzi, S., Bilotta, E., Picozzi, M. & Zollo, A., 2018. Feasibility study of a loss-driven earthquake early warning and rapid response systems for tunnels of the Italian high-speed railway network. oil Dynamics and Earthquake Engineering, Volume 112, pp. 232-242. FEMA, 2020. Building Codes Save: A Nationwide Study - Losses Avoided as a Result of Adopting Hazard-Resistant Building Codes, Washington, D.C.: U.S. Department of Homeland Security.. FEU Fire Officer Associations, 2020. Pan European Fire Strategy 2020: A safer Europe for all, s.l.: FEU Fire Officer Associations. Flood, J., 2014. ASC 105 Generally Accepted Accounting Principles. In: Wiley Gaap 2015: Interpretation and Application of Generally Accepted Accounting Principles 2015. s.l.:s.n. Forastiere, F. et al., 2011. Health impact assessment of waste management facilities in three European countries. Environmental Health, Volume 10(1), p. 53. Forest DSS, 2013. Austria-Improving forestry extension services for small-scale private landowners. [Online] Bibliography 229 Available at: http://www.forestdss.org/wiki/index.php?title=Austria-Improving_forestry_extension_services_ for_small-scale_private_landowners Fouillet, A. et al., 2008. Has the impact of heat waves on mortality changed in France since the European heat wave of summer 2003? A study of the 2006 heat wave. International journal of Epidemiology, Volume 37(2), pp. 309- 317. Fuchs, S., Thoeni, M. & McAlpin, M., 2007. Avalanche hazard mitigation strategies assessed by cost effectiveness analyses and cost benefit analyses—evidence from Davos, Switzerland. Nat Hazards, Volume 41, p. 113–129. Gamper-Rabindran, S. & Timmins, C., 2013. Does cleanup of hazardous waste sites raise housing values? Evidence of spatially localized benefits. Journal of Environmental Economics and Management, Volume 65(3), pp. 345- 360. Gasparrini, A. & Armstrong, B., 2011. The impact of heat waves on mortality. Epidemiology, Volume 22(1), p. 68. Gasparrini, A., Armstrong, B. & Kenward, M., 2010. Distributed lag non-linear models. Statistics in medicine, Volume 29(21), pp. 2224-2234. Gasparrini, A. et al., 2017. Projections of temperature-related excess mortality under climate change scenarios. The Lancet Planetary Health, Volume 1(9), pp. e360-e367. Gasparrini, A. & Leone, M., 2014. Attributable risk from distributed lag models. BMC medical research methodology, Volume 14(1), p. 55. Gauderis, J., De Nocker, L. & Bulckaen, D., 2005. Sigma plan Social-cultural Benefit-Cost Analysis, Synthesis report (Sigmaplan Maatschappelijke Kosten-Baten Analyse), s.l.: s.n. Gerber, F. & Mirzabaev, A., 2017. Benefits of action and costs of inaction: Drought mitigation, s.l.: World Meteorological Organization and and Global Water Partnership. Getter, K. et al., 2009. Carbon sequestration potential of extensive green roofs. Environmental science & technology, Volume 43(19), pp. 7564-7570. Ghesquiere, F., Mahul, O. & Jamin, L., 2006. Earthquake Vulnerability Reduction Program in Colombia: A Probabilistic Benefit-Cost Analysis. Policy Research Working Paper., Washington DC: World Bank. GHRF Commission, 2016. The Case for Investing in Pandemic Preparedness. In: The Neglected Dimension of Global Security: A Framework to Counter Infectious Disease Crises. Washington, DC: National Academies Press. Global Water Partnership Central and Easter Europe, 2015. Guidelines for the preparation of Drought Management Plans. Development and implementation in the context of the EU Water Framework Directive, s.l.: Global Water Partnership Central and Easter Europe. Gollier, C. & Hammitt, J., 2014. The Long-Run Discount Rate Controversy. Annual Review of Resource Economics, Volume 6, pp. 273-295. Gomez, A. F., 2014. Análisis Socioeconómico De Los Incendios Forestales Españoles Y Propuesta De Rediseño De La Estrategia De Prevención-concienciación, s.l.: Trabajo Fin de Máster, Máster en Ingeniería de Diseño. GOV/PGC/HLRF, 2015. Progress and Challenges in Fostering Risk Prevention And Mitigation In A Cross-country Comparative Perspective - Draft Case Study Report Of Austria, s.l.: High Level Risk Forum. Grossmann, M. & Hartje, V., 2012. Strategic Benefit-Cost Analysis of an integrated flood plain management policy for the River Elbe.. Economic valuation of wetland ecosystem services: Case studies from the Elbe River Basin. Guerreiro, S., Glenis, V., Dawson, R. & Kilsby, C., 2017. Pluvial Flooding in European Cities—A Continental Approach to Urban Flood Modelling. Water, Volume 9(4), p. 296. Guiomar, N. & Fernandes, J., 2011. Manual of good practices in the management of forest spaces in the drainage basin of the Castelo do Bode reservoir, s.l.: Springs for Life Project - Volume V. Hajat, S., Armstrong, B., Gouveia, N. & Wilkinson, P., 2005. Mortality displacement of heat-related deaths: a comparison of Delhi, Sao Paulo, and London. Epidemiology, pp. 613-620. Hallegatte, S., 2012. A Cost Effective Solution to Reduce Disaster Losses in Developing Countries: Hydro-Meteorological Services, Early Warning, and Evacuation. Policy Research Working Paper, Volume No. 6058. Hallegatte, S. et al., 2012. Investment Decision Making under Deep Uncertainty - Application to Climate Change, Washington D.C.: World Bank . Bibliography 230 Hamaoka, D. et al., 2010. Military and civilian disaster response and resilience: From gene to policy. Military medicine, Volume 175(suppl_7), pp. 32-36. Hamburger, R. O., Rojahn, C., Heintz, J. & Mahoney, M., 2012. FEMA P58: Next-generation building seismic performance assessment methodology, s.l.: 15th world conference on earthquake engineering. Hayes, M., Svoboda, M., Comte, L. & Redmond, D., 2005. Drought monitoring: new tools for the 21st century. In: Drought and Water Crises: Science, Technology, and Management Issues. Boca Raton, Florida, USA: CRC Press, pp. 53-69. Heidrich, R., 2016. Applied flood-risk-management in the Machland-Nord, Upper Austria. EMERGENCY MANAGEMENT (EMERGENCY PLANNING, EARLY WARNING, INTERVENTION, RECOVERY). Hirshfeld, S., Vesilind, P. & Pas, E., 1992. Assessing the True Cost of Landfills. Waste Management & Research, Volume 10, pp. 471-484. Hofmann, M. A., 2010. Mount Vesuvius Europe’s most dangerous volcano: Study. [Online] Available at: https://www.businessinsurance.com/article/00010101/STORY/100419950/Mount-Vesuvius- Europes-most-dangerous-volcano-Study Holland, M., Spadaro, J., Misra, A. & Pearson, B., 2014. Costs of Air Pollution from European Industrial Facilities 2008– 2012—An Updated Assessment, s.l.: EEA. Holleman, M. A., 2004. Lingering Lessons of the Exxon Valdez Oil Spill, Seattle, WA: Seattle Times. Hölzinger, O. & Haysom, K., 2017. Chimney Meadows Ecosystem Services Assessment - An assessment of how the new management of Chimney Meadows Nature Reserve by Berks, Bucks and Oxon Wildlife Trust impacts on the value of ecosystem services, Oxford: Berks, Bucks and Oxon Wildlife Trust. Hornyak, T., 2018. Clearing the Radioactive Rubble Heap That Was Fukushima Daiichi, 7 Years On. [Online] Available at: https://www.scientificamerican.com/article/clearing-the-radioactive-rubble-heap-that-was- fukushima-daiichi-7-years-on/ Hübler, M., Klepper, G. & Peterson, S., 2018. Costs of climate change: the effects of rising temperatures on health and productivity in Germany. Ecological Economics, Volume 68(1-2), pp. 381-393. Hunt, A. et al., 2017. Climate and weather service provision: Economic appraisal of adaptation to health impacts. Climate services, Volume 7, pp. 78-86. Hunt, A. et al., 2017. Climate and weather service provision: Economic appraisal of adaptation to health impacts. Climate services, Volume 7, pp. 78-86. IAEA, 2020. Country Nuclear Power Profiles – France.. [Online] Available at: https://www.iaea.org/newscenter/news/five-years-after-fukushima-making-nuclear-power-safer IAFA, 2005. Paper 12 - Uranium Mining and Remediation of the Straz Deposit in the Czech Republic, Environmental Contamination from Uranium Production Facilities and their Remediation, Vienna: s.n. IBS, 2013. June floods of 2013 along the Australian Danube, s.l.: s.n. ICNF, 2017. Defesa da Floresta Contra Incêndios. [Online] Available at: http://www2.icnf.pt/portal/florestas/dfci/ ICNF, 2020. ICNF -Instituto da Conservacao de Natureza e das Florestas. [Online] Available at: https://www.icnf.pt/ Independent Evaluation Group, 2010. Benefit-Cost Analysis in World Bank Projects, Washington, D.C.: World Bank. INFARMED, 2020. Autoridade Nacional do Medicamento e Produtos de Saúde. [Online] Available at: https://www.infarmed.pt/web/infarmed-en/human-medicines Institut Cartogràfic i Geològic de Catalunya, 2020. Pyrmove. [Online] Available at: https://www.icgc.cat/en/Innovation/R-D-i-projects/PYRMOVE Instituto Nacional De Estatistica, 2020. Statistics Portugal - Web Portal. [Online] Available at: https://www.ine.pt/xportal/xmain?xpgid=ine_main&xpid=INE Interreg Danube, 2020. DRIDANUBE - Drought Risk in the Danube Region. [Online] Available at: http://www.interreg-danube.eu/approved-projects/dridanube Interreg España-Portugal, 2019. Iberian Centre for Forest Fire Research and Control (CILIFO). [Online] Available at: https://cilifo.eu/ Bibliography 231 Interreg Greece-Bulgaria, 2021. Cross Border Planning and Infrastructure Measures for Flood Protection. [Online] Available at: http://www.greece-bulgaria.eu/approved-projects/?axis=0&partner=0&call=0&acronym=47 Jawerth, N., 2016. Five Years After Fukushima: Making Nuclear Power Safer, s.l.: IAEA Office of Public Information and Communication. JBA Risk Management , 2021. Flood Risk Analysis for EU Member States, Method Report. JBA, 2013. Investigation into the flooding at Tattenhall, Cheshire, Yorkshire: JBA Consulting. Johnson, D. et al., 2020. A cost–benefit analysis of implementing urban heat island adaptation measures in small-and medium-sized cities in Austria, s.l.: Environment and Planning B: Urban Analytics and City Science.. JRC, 2003. Lessons learnt from Landslide Disasters in Europe, Italy: The European Commission, Joint Research Centre. Kalkstein, A. & Sheridan, S., 2007. The social impacts of the heat–health watch/warning system in Phoenix, Arizona: assessing the perceived risk and response of the public. International journal of biometeorology, Volume 52(1), pp. 43-55. Karlsson, M. & Ziebarth, N., 2018. Population health effects and health-related costs of extreme temperatures: Comprehensive evidence from Germany. Journal of Environmental Economics and Management, Volume 91, pp. 93-117. Khabarov, N., Moltchanova, E. & Obersteiner, M., 2008. Valuing weather observation systems for forest fire management. IEEE Systems Journal, Volume 2(3), pp. 349-357. Kibirige, D. & Tan, X., 2013. Evaluation of Open Stormwater Solutions in Augustenborg, Sweden, s.l.: Master’s thesis, Lund University. Kiel, K. & Zabel, J., 2012. Estimating the Economic Benefits of Cleaning Up Superfund Sites: The Case of Woburn, Massachusetts. The Journal of Real Estate Finance and Economics, Volume 22, p. 163–184. Kimio, T., 2013. Japan’s Experience for DRR & Linking DRR to Sustainable Development by DR 2AD Model. [Online] Available at: https://www.unescap.org/sites/default/files/S3-1_DR2AD_model_ver1.pdf Kim, K., Pant, P. & Yamashita, E., 2018. Managing uncertainty: Lessons from volcanic lava disruption of transportation infrastructure in Puna, Hawaii. J Emerg Manag, Volume 16(1), pp. 29-40. Kind, J., 2014. Economically efficient flood protection standards for the Netherlands. J Flood Risk Management. Kircher, C. A., Whitman, R. V. & Holmes, W. T., 2006. HAZUS earthquake loss estimation methods. Natural Hazards Review, pp. 45-59. Kjellstrom, T. et al., 2019. Working on a warmer planet: The impact of heat stress on labour productivity and decent work. Publications Production Unit, International Labour Organization. Kull, D., Mechler, R. & Hochrainer-Stigler, S., 2013. Disasters. In: Probabilistic cost-benefit analysis of disaster risk management in a development context. Washington DC: World Bank, pp. 374-400. LaFee, S., 2021. Poorer Mental Health Smolders After Deadly, Devastating Wildfire. [Online]. Laukkonen, J. et al., 2009. Combining climate change adaptation and mitigation measures at the local level. Habitat International, Volume 33(3), pp. 287-292. Le Guenan, T., Smai, F., Loschetter, A. & al., e., 2016. Accounting for end-user preferences in earthquake early warning systems. Bull. Earthq. Eng, Volume 14, pp. 297-319. Lexer, M., Vacik, H., Palmetzhofer, D. & Oitzinger, G., 2005. A decision support tool to improve forestry extension services for small private landowners in southern Austria. Computers and electronics in agriculture, Volume 49(1), pp. 81-102. Liel, A. B. & Deierlein, G. G., 2013. Cost-benefit evaluation of seismic risk mitigation alternatives for older concrete frame buildings. Earthquake Spectra, pp. 1391-1411. LIFE, 2020. LIFE+ Climate-Proofing Social Housing Landscapes, s.l.: LIFE. Liu, N. & Maes, F., 2010. The European Union’s Role in the Prevention of Vessel-Source Pollution and its Internal Influence. Journal of International Maritime Law, Volume 15. Liu, T. et al., 2019. Valuation of Drought Information: Understanding the Value of the US Drought Monitor in Land Management, the United States: National Integrated Drought Information System. Louis, V. et al., 2008. The health and health care system impacts of earthquakes, windstorms and floods–a systematic review. MICRODIS paper series, p. 1Á62. Bibliography 232 Loureiro, M. L., 2006. Estimated costs and admissible claims linked to the Prestige oil spill. Ecological Economics, Volume 59(1), pp. 48-63. Lourenço, T. C. et al., 2019. Climate Adaptation Platforms and Decision Support Tools in the Context of High-end Climate Change, s.l.: ECCA 2019 Conference. Lowe, R. et al., 2016. Evaluation of an early-warning system for heat wave-related mortality in Europe: Implications for sub-seasonal to seasonal forecasting and climate services. International journal of environmental research and public health, Volume 13(2), p. 206. MacDonald, M., 2020. Integrating natural capital into flood risk management appraisal Study Report, s.l.: Tweed Forum. MacMullan, E., Reich, S., Puttman, T. & Rodgers, K., 2009. Cost-benefit evaluation of ecoroofs. In Low Impact Development for Urban Ecosystem and Habitat Protection, pp. 1-10. Madajewicz, M., Tsegay, A. & Norton, M., 2013. Managing risks to agricultural livelihoods: impact evaluation of the Harita program in Tigray, Ethiopia, 2009–2012, London: Oxfam. Maksimovic, C., 2017. Blue Green Solution: A Systems Approach to Sustainable, Resilent, and Cost-Efficient Urban Development, s.l.: Climate-KIC. Makwana, N., 2019. Disaster and its impact on mental health: A narrative review. Journal of family medicine and primary care, Volume 8(10), p. 2090. Manson, S., 2018. Working with Natural Processes – Evidence Directory: Case study 54. Alkborough Flats Managed Realignment Scheme, s.l.: Environment Agency. Marchau, W. B. P., 2019. Decision Making Under Deep Uncertainty. From Theory to Practice, s.l.: Springer International Publishing. Mărmureanu, A., Ionescu, C. & Cioflan, C., 2011. Advanced real-time acquisition of the Vrancea earthquake early warning system. Soil Dynamics and Earthquake Engineering, Volume 31(2), pp. 163-169. Marzocchi W & G., W., 2009. Principles of volcanic risk metrics: Theory and the case study of MountVesuvius and Campi Flegrei, Italy. J Geophys Res, Volume 114:B03213. Marzocchi, W. & Woo, G., 2007. Probabilistic eruption forecasting and the call for an evacuation. Geophys ResLett, Volume 34:L22310. Masters, R. et al., 2017. Return on Investment of Public Health Interventions: A Systematic Review. Journal of Epidemiological Community Health, Volume 71, pp. 827-34. Mayer, C., Vilardell, L., Vacik, H. & Muller, M., 2020. Forest fires in the Alps –State of Knowledge, Future Challenges and Options for an Integrated Fire Management, s.l.: EUSALP Action Group 8. McIlwrath, C., 2018. Working with Natural Processes – Evidence Directory: Case study 10. Padgate Brook River Restoration part of the Warrington FRM Scheme, s.l.: Environment Agency. Mechler, R., 2016. Reviewing estimates of the economic efficiency of disaster risk management: opportunities and limitations of using risk-based cost-benefit analysis, s.l.: s.n. Mechler, R., 2016. Reviewing Estimates of the Economic Efficiency of Disaster Risk Management: Opportunities and Limitations of Using Risk-Based Cost-Benefit Analysis. Natural Hazards, Volume 81, p. 2121–47. Mechler, R. & Hochrainer-Stigler, S., 2019. Generating Multiple Resilience Dividends from Managing Unnatural Disasters in Asia: Opportunities for Measurement and Policy. ADB Economics Working Paper Series, Volume No.601.10.22617/WPS190573-2. Meyer, V., Priest, S. & Kuhlicke, C., 2012. Economic evaluation of structural and non-structural flood risk management measures: examples from the Mulde River. Nat Hazards, Volume 62, p. 301–324. Michelozzi, P. et al., 2009. High temperature and hospitalizations for cardiovascular and respiratory causes in 12 European cities. American journal of respiratory and critical care medicine, Volume 179(5), pp. 383-389.. Mills, D. & Kalkstein, L., 2012. Estimating reduced heat-attributable mortality for an urban revegetation project. Journal of Heat Island Institute International, Volume 7(2), pp. 18-24. Morabito, M. et al., 2019. An Occupational Heat–Health Warning System for Europe: The HEAT-SHIELD Platform. International journal of environmental research and public health, Volume 16(16), p. 2890. Mora, T. et al., 2018. Renovation of a School Building: Energy Retrofit and Seismic Upgrade in a School Building in Motta Di Livenza. Sustainability. Bibliography 233 Moscatelli, M., Albarello, D., Scarascia Mugnozza, G. & Dolce, M., 2020. The Italian approach to seismic microzonation. Bulletin of Earthquake Engineering. S.I.: Seismic Microzonation of Central Italy. Multi-Hazard Mitigation Council, 2019. Natural Hazard Mitigation Saves: 2019 Report, Washington D.C.: National Institute of Building Sciences. Murray, V. & Ebi, K., 2012. IPCC Special Report on Managing the Risks of Extreme Events and Disasters to Advance Climate Change Adaptation (SREX). J Epidemiol Community Health, Volume 66(9), pp. 759-760. Natural Resources Conservation Services, 2011. Fuel and Fire Breaks: Small Scale Solutions for your Farm, s.l.: NRCS. Natuurmonumenten, 2020. English summary - LIFE Floodplain Development. [Online] Available at: https://www.natuurmonumenten.nl/projecten/rivierklimaatpark-ijsselpoort/english Naumann, G. et al., 2020. Global warming and human impacts of heat and cold extremes in the EU, Luxembourg: Publications Office of the European Union. Neagoe, C., 2016. Romanian Seismic Network, Dubrovnik, Croatia: National Institute for Earth Physics (NIEP) Romania, Presentation 25-28 October, 2016. NIBS, 2019. Natural Hazard Mitigation Saves: 2019 Report, National Institute of Building Sciences (NIBS), Washington DC: National Institute of Building Sciences. Nisbet, T. e. a., 2018. Working with Natural Processes – Evidence Directory: Case study 12. Slowing the Flow at Pickering, s.l.: Environment Agency. Nogueira, H.I.S. & Walraven, M. 2018. Overview Storm Surge Barriers. Deltares. http://www.masterpiece.dk/ UploadetFiles/10852/25/Deltares_2018_Overview_storm_surge_barriers_komprimeret.pdf Nuclear Energy Agency & Organisation for Economic Co-operation and Development, 2013. The Fukushima Daiichi Nuclear Power Plant Accident: OECD/NEA Nuclear Safety Response and Lessons Learnt, s.l.: OECD. OCED, 2019a. OECD Economic Surveys: France 2019, s.l.: OCED Publishing. OECD, 2018b. Health at Glance Europe. [Online] Available at: https://www.oecd.org/health/health-systems/Health-at-a-Glance-Europe-2018-CHARTSET.pdf OECD, 2019b. Environmental Remediation of Uranium Production Facilities, s.l.: OECD. OECD, 2020. The territorial impact of COVID-19: Managing the crisis across levels of government. [Online] Available at: https://www.oecd.org/coronavirus/policy-responses/the-territorial-impact-of-covid-19-managing- the-crisis-across-levels-of-government-d3e314e1 OECD, 2021. Regional Statistics. [Online] Available at: https://www.oecd.org/regional/regional-statistics/ Oke, T., 1973. City size and the urban heat island. Atmospheric Environment, Volume 7(8), pp. 769-779. Oke, T., 1982. The energetic basis of the urban heat island. Quarterly Journal of the Royal Meteorological Society, Volume 108(455), pp. 1-24. ONERC, 2009. Climate change: costs of impacts and lines of adaptation. Observatoire National sur les Effets du Réchauffement Climatique (National Observatory for the Impacts of Global Warming), s.l.: Report to the Prime Minister and Parliament. OPERAs, 2020. Barcelona’s Hybrid Dunes. [Online] Available at: https://operas-project.eu/node/318 Paci, D., 2014. Human health impacts of climate change in Europe report for the PESETA II project, Luxembourg: JRC Technical Reports, Publications Office. Pappenberger, F. et al., 2015. The monetary benefit of early flood warnings in Europe. Environmental Science & Policy, Volume 51, pp. 278-291. Parker, D., Priest, S. & Tapsell, S., 2008. Modelling the damage reducing effects of flood warnings, s.l.: s.n. Parker, D., Tapsell, S. & Mccarthy, S., 2007. Enhancing the human benefits of flood warning. Natural Hazards, Volume 43(3), pp. 397-414. Pasha-Robinson, L., 2016. Mount Vesuvius eruption risk: Emergency plans to evacuate 700,000 finalised. [Online] Available at: Pasha-Robinson, Lucy. 2016. Mount Vesuvius eruption risk: Emergency plans to evacuate 700,000 finalised. Independent. https://www.independent.co.uk/news/world/europe/mount-vesuvius- emergency-evacuation-eruption-plans-finalised-a7360686.html Bibliography 234 Pastor, E., Muñoz, J., Caballero, D. & al, e., 2020. Wildland–Urban Interface Fires in Spain: Summary of the Policy Framework and Recommendations for Improvement, s.l.: Fire Technol 56. Perera, D. et al., 2019. Flood Early Warning Systems: A Review Of Benefits, Challenges And Prospects. UNU-INWEH Report Series, Volume 8. Perini, K. & Rosasco, P., 2016. Is greening the building envelope economically sustainable? An analysis to evaluate the advantages of economy of scope of vertical greening systems and green roofs. Urban Forestry & Urban Greening, Volume 20, pp. 328-337. Perry, R. W., 2004. Disaster Exercise Outcomes for Professional Emergency Personnel and Citizen Volunteers. Journal of Contingencies and Crisis Management, Volume 12(2), pp. 64-75. Peter, M., Emonson, P., Jones, B. & Davies, A., 2014. Post-Installation Effectiveness of Property Level Flood Protection Final report FD2668, London: Water and Floods. Department for Environment, Food and Rural Affairs. Pinheiro, A., 2015. Economic value of the soil: public and private perspectives. Revista de Ciências Agrárias, Volume 38 (4), pp. 612-620. Pohoryles, D., Maduta, C., Bournas, D. & Kouris, L., 2020. Energy performance of existing residential buildings in Europe: A novel approach combining energy with seismic retrofitting. Energy and Buildings, Volume 223. PORDATA, 2020a. Analysis of hotel occupancies in area between 2014-2018. [Online] Available at: https://www.pordata.pt/ PORDATA, 2020b. Base de Dados Portugal Contemporâneo. [Online] Available at: https://www.pordata.pt/Portugal Porter, K., 2016. How Many Injuries can be Avoided through Earthquake Early Warning and Drop, Cover, and Hold On?, Colorado: Structural Engineering and Structural Mechanics Program, University of Colorado. Portugal Wildfire, 2018. What is a Fuel Break. [Online] Available at: https://www.portugalwildfires.com/what-is-a-fuel-break/ Povoledo, E., 2016. Powerful Earthquake in Italy Kills at Least 241 and Shatters Towns2016.. [Online] Available at: https://www.nytimes.com/2016/08/25/world/europe/italy-earthquake.html Priest, S. J., Parker, D. J. & Tapsell, S. M., 2011. Modelling the potential damage-reducing benefits of flood warnings using European cases. Environmental Hazards, Volume 10:2, pp. 101-120. Public Health Emergency, 2020. Disaster Behavioral Health. [Online] Available at: https://www.phe.gov/Preparedness/planning/abc/Pages/disaster-behavioral.aspx Pulwarty, R. S. & Sivakumar, M. V., 2014. Information systems in a changing climate: Early warnings and drought risk management. Weather and Climate Extremes, Volume 3, pp. 14-21. PWIB Wohnungs-Infobörse GmbH, 2020. Immobilienpreisentwicklung und Preistrend in Österreich: aktuelle Immobilienspiegel, s.l.: s.n. Reid, H. et al., 2019. PLA 60: Community-based adaptation to climate change, s.l.: International Institute for Environment and Development. ResCult, 2021. ResCult: Increasing Resilience of Cultural heritage: a Supporting Decision Tool for the Safeguarding of Cultural Assets. [Online] Available at: https://www.rescult-project.eu/ Restorerivers.eu, 2014. Restorerivers.eu. [Online] Available at: https://restorerivers.eu/wiki/index.php?title=Case_ study%3AMayesbrook_Climate_Change_Park_restoration_project Revell, D. e. a., 2018. Working with Natural Processes – Evidence Directory: Case study 7. Mill Brook Tattenhall, Cheshire, s.l.: Environment Agency. Rey, G. et al., 2007. The impact of major heat waves on all-cause and cause-specific mortality in France from 1971 to 2003. International archives of occupational and environmental health, Volume 80(7), pp. 615-626. RISE, 2021. RISE - Home. [Online] Available at: http://www.rise-eu.org/home/ Rose, A. et al., 2007. Benefit-cost analysis of FEMA hazard mitigation grants. Natural hazards review, Volume 8(4), pp. 97-111. Ross, H. et al., 2015. A participatory systems approach to understanding climate adaptation needs. Climatic Change, Volume 129, p. 27–42. Bibliography 235 Rozenberg, J. et al., 2019. From A Rocky Road to Smooth Sailing: Building Transport Resilience to Natural Disasters, Washington DC: World Bank. RRC, 2013. Manual of River Restoration Techniques. , Cranfield, Bedfordshire: River Restoration Centre. Salbego, G., Floris, M., Busnardo, E. & Toaldo, M., 2015. A Multi-scale Approach to Cost/benefit Analyses of Landslide Prevention. Natural Hazards and Earth System Sciences, Volume 3, pp. 1329-1355. Salbego, G. et al., 2015a. Detailed and large-scale cost/benefit analyses of landslide prevention vs. post-event actions. Natural Hazards and Earth System Sciences, Volume 15(11), pp. 2461-2472. Samela, C. et al., 2020. Safer_RAIN: A DEM-Based Hierarchical Filling-&-Spilling Algorithm for Pluvial Flood Hazard Assessment and Mapping across Large Urban Areas. Water. Sandri, L. et al., 2012. Combining long- and short-term probabilistic volcanic hazard assessment with Benefit-Cost Analysis to support decision making in a volcanic crisis from the Auckland Volcanic Field, New Zealand. Bull Volcanol, Volume 74, p. 705–723. Sands, P., Turabi, A., Saynisch, P. & Dzau, V., 2016. Assessment of economic vulnerability to infectious disease crises. The Lancet, Volume 388, 10058, p. 2443–2448. Schmitt, L., Graham, H. & White, P., 2016. Economic Evaluations of the Health Impacts of Weather-Related Extreme Events: A Scoping Review. Int J Environ Res Public Health, Volume 3(11), p. 1105. Schröter, K., Ostrowski, M., Velasco-Forero, C. & Sempere-Torres, D., 2008. Effectiveness and Efficiency of Early Warning Systems for Flash-Floods (EWASE), London: CRUE Co-ordinator Area 3D. Schwaiger, H. et al., 2015. Reduktion städtischer Wärmeinseln durch Verbesserung der Abstrahleigenschaften von Gebäuden und Quartieren. Stadt der Zukunft, p. 95. Scolobig, A. et al., 2014. Synthesis: Benefits and barriers to multi-hazard mitigation and adaptation, with policy recommendations for decision-support. Deliverable 6.4 of the Matrix project, New methodologies for multi- hazard and multi-risk assessment methods for Europe, s.l.: European Commission 7th Framework Programme. Seismological Society of America, 2021. For Eyewitness Accounts of Earthquake Shaking, Representation Matters. [Online] Available at: https://www.seismosoc.org/news/for-eyewitness-accounts-of-earthquake-shaking- representation-matters/ Self, S., 2006. The effects and consequences of very large explosive volcanic eruptions. s.l.:The Royal Society Publishing. Shoaf, K. & Rotiman, S., 2000. Public health impact of disasters. Australian Journal of Emergency Management, Volume 15(3), p. 58. SHOPP, 2020. SHOPP COVID PPD Cost Analysis, s.l.: SHOPP. Shreve, C. & Kelman, I., 2014. Does Mitigation Save? Reviewing Cost-Benefit Analyses of Disaster Risk Reduction. International Journal of Disaster Risk Reduction, Volume 10(A), p. 213–235. Sigmaplan.be, 2021. Sigma Plan. [Online] Available at: https://www.sigmaplan.be/en/projects/ Sigmund, Z., 2019. Barriers and Incentives for Extensive Implementation of Combined Seismic and Energy Efficiency Retrofits, s.l.: IOP Conf. Ser.: Earth Environ. Sci. Silva, T. P. d. e. a., 2006. Estimativa de Emissões Atmosféricas Originadas por Fogos Rurais em Portugal. Silva Lusitana, Volume 14(2), p. 239 – 263. Sinclair, H., Doyle, E., Johnston, D. & Paton, D., 2012. Assessing emergency management training and exercises. Disaster Prevention and Management, Volume 21(4). Soz, S. A., Kryspin-Watson, J. & Stanton-Geddes, Z., 2016. The Role of Green Infrastructure Solutions in Urban Flood Risk Management, Washington D.C.: World Bank. Spray, C., 2016. Eddleston Water Project Summary Report, s.l.: Tweed Forum. Statistik Austria, 2020. Sterbetafeln. [Online] Available at: https://www.statistik.at/web_de/statistiken/menschen_und_ gesellschaft/bevoelkerung/sterbetafeln/index.html Stein, S. M. et al., 2018. Wildfire, Wildlands, and People: Understanding and Preparing for Wildfire in the Wildland-Urban Interface, s.l.: USDA Forest Service. Stein, U. et al., 2016. uropean Drought and Water Scarcity Policies. In: Governance for Drought Resilience. s.l.:Springer, Cham, pp. 17-43. Bibliography 236 Strauss, J. & Allen, R., 2016. Benefits and costs of earthquake early warning. Seismological Research Letters. Seismological Research Letters, Volume 87(3), pp. 765-772. Strehl, C. & Offermann, M., 2017. Schlussbericht des Forschungsvorhabens KURAS, Berlin: IWW-Tielbericht: Ökonomische Effekte der Regenwasserbewirtschaftung am Beispiel Berlins. Suk, J., Vaughan, E., Cook, R. & Semenza, J., 2020. Natural disasters and infectious disease in Europe: a literature review to identify cascading risk pathways. European journal of public health, Volume 30(5), pp. 928-935. Szewczyk, W. et al., 2020. Economic analysis of selected climate impacts JRC PESETA IV project – Task 14, Luxembourg: Publications Office of the European Union. Tanielian, T. & Jaycox, L. H., 2008. Invisible Wounds of War: Psychological and Cognitive Injuries, Their Consequences, and Services to Assist Recovery. Santa Monica, CA: RAND Corporation. Tanner, T. et al., 2015. The Triple Dividend of Resilience: Realizing Development Goals through the Multiple Benefits of Disaster Risk Management, London and Washington, DC:: Overseas Development Institute and World Bank. Taylor, L., 2016. Cleaning up brownfield sites not only benefits the environment – it also increases nearby property values. USCentre, pp. https://blogs.lse.ac.uk/usappblog/2016/07/13/cleaning-up-brownfield-sites-not-only- benefits-the-environment-it-also-increases-nearby-property-values Téhard, B. et al., 2020. The Value of a QALY for France: A New Approach to Propose Acceptable Reference Values.. Value in Health. Teisberg, T. & Weiher, R., 2009. Benefits and Costs of Early Warning Systems for Major Natural Hazards Background Paper, Washington D.C.: World Bank. The Energy and Water Agency, 2020. Significant Water Management Issues: In the Malta River Basin District.. [Online] Available at: https://era.org.mt/wp-content/uploads/2020/08/Significant-Water-Management-Issues- Document_final-1.pdf The National Herald, 2019. Greece Getting 150m Euro EU Loan for Floods Climate Change. [Online] Available at: https://www.thenationalherald.com/archive_general_news_greece/arthro/greece_getting_150m_ euro_eu_loan_for_floods_climate_change-51058/ Thielen Del Pozo, J., 2015. The benefit of continental flood early warning systems to reduce the impact of flood disasters, s.l.: Publications Office of the European Union. Tillement, S., 2018. How are nuclear risks managed in France?. [Online] Available at: https://theconversation.com/how-are-nuclear-risks-managed-in-france-99524 Tinholt, D. et al., 2013. Study on Analysis of the Needs for Cross-Border Services and Assessment of the Organisational, Legal, Technical and Semantic Barriers, s.l.: European Commission. Transparency International EU, 2017. The rains of Athens: Stopping the floods. [Online] Available at: https://transparency.eu/the-rains-of-athens/ Tweed Forum, 2020. Eddleston Water Hydrologic and Hydraulic Modelling of NFM: Phase 2., s.l.: Tweed Forum. UNDP, 2015. Socio-economic impact of Ebola Virus Disease in West African Countries: a call for national and regional containment, recovery and prevention, UNDP, Regional Bureau for Africa, s.l.: s.n. UNDRR, 2020. Recommendations for a Revised EU strategy on climate change adaptation, s.l.: UNDRR. UNEP, 2004. Impacts of summer 2003 heat wave in Europe, s.l.: Environment Alert Bulletin. University of California, 2020. Economic Contirbution of California‘s Forestry and Forest-Products Sectors, s.l.: UC ANR Publication.. University of Coimbra, 2020. Association for the Development of Industrial Aerodynamics, Coimbra, Portugal: University of Coimbra. UrbanGreenUp, 2020. Need a Hand With Finding the Right Green Solutions for Your City?. [Online] Available at: https://www.urbangreenup.eu/news--events/news/need-a-hand-with-finding-the-right-green- solutions-for-your-city-.kl USDA, 2016. Livestock and Products Report - Latvia, s.l.: USDA Foreign Agriculture Service. Bibliography 237 USGS, 2005. Benefits of Volcano Monitoring Far Outweigh Costs–The Case of Mount Pinatubo. [Online] Available at: https://pubs.usgs.gov/fs/1997/fs115-97/ USGS, 2021. Why are we having so many earthquakes? Has naturally occurring earthquake activity been increasing? Does this mean a big one is going to hit? OR We haven’t had any earthquakes in a long time; does this mean that the pressure is building up for a big one?. [Online] Available at: https://www.usgs.gov/faqs/why-are-we-having-so-many-earthquakes-has-naturally-occurring- earthquake-activity-been?qt-news_science_products=0#qt-news_science_products Velinger, J., 2015. More than 100 died due to fires in the Czech Republic last year. [Online] Available at: https://english.radio.cz/more-100-died-due-fires-czech-republic-last-year-8270251 Viscusi, W. K. & Masterman, C., 2017. Income Elasticities and Global Values of a Statistical Life. J. Benefit Cost Anal, Volume 2, pp. 226-250. VMM, 2011. Flood Report November 2010. Operational Water Management Department, VMM (Flemish Environment Agency), Appendix 2.2. (requested translated document, original language document online), s.l.: s.n. Vöhringer, F. et al., 2017. Assessing the impacts of climate change for Switzerland, s.l.: Bern: The Federal Office for the Environment. Vousdoukas, M. I. et al., 2020. Adapting to rising coastal flood risk in the EU under climate change. In: Climate change impacts and adaptation in Europe - JRC PESETA IV final report. s.l.:European Commission. Vukanovic, S., 2018. Climate and disaster resilient Transport Infrastructure, s.l.: World Bank. Walmsley, T., Rose, A. & Wei, D., 2020. The Impacts of the Coronavirus on the Economy of the United States. Economics of Disasters and Climate Change, Volume 5, pp. 1-52. Weingraber, F., 2020. Government of Oberösterreich, Pers Comm., s.l.: s.n. Weitzman, M. L., 2011. Fat-Tailed Uncertainty in the Economics of Catastrophic Climate Change. Review of Environmental Economics and Policy, Volume 5(2), pp. 275-292. Wheatley, S., Sovacool, B. & Sornette, D., 2016. Reassessing the safety of nuclear power. Energy Research & Social Science, Volume 15, pp. 96-100. White, I. et al., 2018. Flood resilience technology in Europe: identifying barriers and co-producing best practice. ournal of Flood Management, pp. 468-478. WHO, 2016. Ebola Situation Report - 16 March 2016, s.l.: s.n. WHO, 2020. Mental health and COVID-19. [Online] Available at: https://www.euro.who.int/en/health-topics/health-emergencies/coronavirus-covid-19/publications- and-technical-guidance/noncommunicable-diseases/mental-health-and-covid-19 WHO, 2021. Floods. [Online] Available at: https://www.who.int/health-topics/floods#tab=tab_1 Wikipedia, 2020. Economy of Finland. [Online] Available at: https://en.wikipedia.org/wiki/Economy_of_Finland Wilson, D., Das, M. & Gorgens, M., 2020. What Health Emergencies And Disaster Risk Recovery Efforts Have In Common.. [Online] Available at: https://blogs.worldbank.org/health/what-health-emergencies-and-disaster- risk-recovery-efforts-have-common Winter, M. et al., 2016. The Economic Impact of Landslides and Floods on the Road Network. Procedia Engineering, Volume 143, p. 1425–1434. Woessner, J., Laurentiu, D., Giardini, D. & al., e., 2015. The 2013 European Seismic Hazard Model: key components and results. Bull Earthquake Eng, Volume 13, p. 3553–3596. Woo, G., 2008. Probabilistic criteria for volcano eruption evacuation decisions. Natural Hazards, Volume 45, p. 87–97. Woo, G., 2015. Cost–Benefit Analysis in Volcanic Risk, s.l.: In Volcanic Hazards, Risks and Disasters, edited by John F. Shroder and Paolo Papale, 289–300. Elsevier.. Woo, G., 2019. Downward counterfactual search for extreme events, Frontiers in Earth Science, December 2019, s.l.: s.n. World Bank, GFDRR, 2014. Understanding Risk in an Evolving World : Emerging Best Practices in Natural Disaster Risk Assessment., Washington, DC: World Bank. Bibliography 238 World Bank, 2007. Odra River Flood Protection. [Online] Available at: https://projects.worldbank.org/en/projects- operations/project-detail/P086768?lang=en World Bank, 2014. The Economic Impact of the 2014 Ebola Epidemic: Short- and Medium-Term Estimates for West Africa, s.l.: s.n. World Bank, 2016. Discounting Costs and Benefits in Economic Analysis of World Bank Projects, Washington D.C.: World Bank. World Bank, 2017a. Europe and Central Asia - Country risk profiles for floods and earthquakes - Technical Report, Washington D.C.: World Bank Group. World Bank, 2017b. Guidance note on shadow price of carbon in economic analysis, Washington D.C.: World Bank. World Bank, 2018a. Strengthening Disaster Risk Management, Washington D.C.: World Bank. World Bank, 2018b. Istanbul Seismic Risk Mitigation and Emergency Preparedness Project: Project Performance Assessment Report, Washington D.C.: World Bank. World Bank, 2019a. Improving Resilience and Emergency Response, Washington D.C.: World Bank. World Bank, 2019b. Strengthening Preparedness and Critical Emergency Infrastructure, Washington D.C.: World Bank. World Bank, 2019d. Turkey - Disaster Risk Management in Schools Project, Washinigton D.C.\: World Bank. World Bank. 2020a. Analysis of Heat Waves and Urban Heat Island Effects in Central European Cities and Implications for Urban Planning. World Bank, Washington, DC. https://openknowledge.worldbank.org/handle/10986/34335 World Bank, 2020b. Europe and Central Asia Economic Update, Fall 2020: COVID-19 and Human Capital, Washington D.C.: World Bank. World Bank, 2020c. Strengthening Resilience in the Transport Sector, s.l.: World Bank Group. World Bank, 2021. Cyprus, Washington D.C.: World Bank. World Health Organization, 2020. Chemical Incidents, s.l.: s.n. World Nuclear Association, 2021. Nuclear Power in France. [Online] Available at: https://www.world-nuclear.org/information-library/country-profiles/countries-a-f/france.aspx WSL Institute for Snow and Avalanche Research SLF, 2020. Long-term Statistics. [Online] Available at: https://www.slf.ch/en/avalanches/destructive-avalanches-and-avalanche-accidents/long-term- statistics.html WUIVIEW, 2019. Wildland-Urban Interface Virtual Essays Workbench Deliverable D4.1: WUI state of the art and regulatory needs in Europe, s.l.: WUIVIEW. Xiong, J. & Alegre, E. X., 2019. Climate Resilient Road Assets in Albania, Washington, DC.: World Bank. Yang, J., Yu, Q. & Gong, P., 2008. Quantifying air pollution removal by green roofs in Chicago. Atmospheric environment, Volume 42(31), pp. .7266-7273. Yi, Z., Burton, H. V., Shokrabadi, M. & Issa, O., 2020. Multi-scale Benefit-Cost Analysis of the Los Angeles Soft-Story Ordinance. Engineering Structures, p. 214. Žuvela-Aloise, M. et al., 2018. Modelling reduction of urban heat load in Vienna by modifying surface properties of roofs. Theoretical and applied climatology, Volume 131(3-4), pp. 1005-1018. Bibliography 239 5. Annexes 5.1. Annex 1: Key terms and definitions related to methodologies to the estimation of costs and benefits of DRM investments Benefit-cost analysis: Process used to identify, investments. The IRR is a discount rate that would measure, and analyse the benefits of a project, make the NPV of all monetary flows equal to zero in a program, or decision versus the costs associated with discounted monetary flow analysis. The external rate it. of return also considers inflation and costs of capital. Benefit-cost ratio: Ratio used in BCA to summarize Net present value: Difference between the present the relationship between overall relative benefits and value of monetary inflows and the present value of costs of a project. A BCR lower than 1 means that the cash outflows over a period. The idea behind the NPV project net benefits could be negative—that is, is to project all future monetary inflows and outflows benefits are lower than costs. associated with a project/program/decision, discount all these flows to the present day, and add them Direct and indirect benefits/costs: Benefits/costs can together. A positive NPV means that, after accounting directly be associated with the impact of the project/ for the time value of monetary flows, the project/ program/decision, for example, asset losses prevented program/decision could yield net benefits. or environmental value enhanced due to a flood prevention measure preventing a substantial impact Sensitivity analysis: Determines and showcases how on the asset as well as direct costs of the flood results change when assumptions, particular prevention measure. They can also be indirectly parameters, or variables of an analysis are changed. associated with the impact, for example, productivity losses prevented given the measure as well as Value of statistical life and value of a life year: The increases of prices in the area leading to displacement value of statistical life (VSL) is the marginal rate of and loss of welfare/well-being of certain populations. substitution between income (wealth) and mortality risk, that is, how much individuals are willing to pay on Discount rate: Rate of return used to discount future average to reduce the risk of death. It does not cash flows back to their present value. Financial therefore indicate the value of an actual live but the discount rates are the interest rates used to calculate value of marginal changes in the likelihood of death. the present value of future cash flows from a project or The value of a life year (VOLY) is derived from the investment. Social discount rates indicate a society’s willingness to pay (WTP) for increasing life expectancy average valuation of future versus present impacts of by one additional year, which is considered more interventions (benefits and costs). A high discount rate appropriate for disasters that are mostly displacing indicates a lower valuation of the future and a mortality (that is, affecting certain age groups) rather preference for the present, which particularly in the than causing mostly premature deaths. Theoretically, context of climate change also concerns measurements of actual changes in life expectancy intergenerational equity aspects. would be the exact measure to consider. Internal rate of return (external rate of return): Metric used in analysis to estimate the benefits of potential Annexes 240 5.2. Annex 2: A step-by-step practitioner report on applying the Triple Dividend BCA This part includes a detailed description of methods often overlapping, and the possibility of confounding and approaches used at each step of the Triple effects of other unrelated interventions made the Dividend BCA as well as lessons learned. It can be assessment particularly difficult. used as a guide as it outlines many of the practical difficulties that may be faced when undertaking Triple Existing data and literature allowed us to directly Dividend BCA with limited resources (time, budgets, identify the first dividend (that is, lives saved) of a data) and with the objective of covering a large number project in most cases, but only in some cases or partly of investments to review. the second and third dividends. Although the third dividend of investments can be multi-faceted, we were 1. DEFINING THE GOALS AND OBJECTIVES OF able to quantify only a handful of those benefits. THE PROJECT Therefore, our calculation of BCRs is necessarily a lower bound estimate rather than overestimation. For this particular analysis, the goals and objectives Despite the limitations, we were able to identify described for each investment were the ones described benefits beyond the first dividend often using the best in project documentation for EU and World Bank available yet coarse data. projects. The case studies that were mostly considered for more in-depth analysis were those that had goals 2. LIST ALTERNATIVE PROJECTS and objectives closely related to DRR investments. Otherwise, additional objectives of the investments Due to the unavailability of data, we mainly focused on were outlined qualitatively and were considered as a retroactive analysis of investments without using a much as possible in the analysis as co-benefits to DiD approach. A theoretical best practice approach ensure that costs considered would be in line with the with a perfect counterfactual was mostly not possible scope of benefits. in this analysis. However, some analysis was undertaken with theoretical investments so that the The overarching goal of each of the projects evaluated counterfactual could reasonably be assumed, which using the triple dividend BCA is disaster risk reduction also served as theoretical synthetic controls. and ultimately building resilience. This can occur either directly (for example, building dams and EWS) Unlike the private sector investment projects, DRM/ or indirectly (for example, school retrofit program). DRR projects generally are managed and funded by Examples of disasters include floods, earthquakes, the public sector and therefore seldom have heatwaves, wildfires, and storms. Investment in each alternatives. Aimed at maximizing societal benefits, of these projects is pre-defined, and the consequent such investment projects often do not have alternatives, objectives and benefits are well perceived. However, meaning that we have to resort to BCA of a given most of the benefits are often qualitative, and often project instead of additionally identifying the cost- range between direct financial and indirect societal effectiveness of alternative projects with same goals benefits. Under the triple dividend approach, we and objectives (that is, with similar benefits) but with capture and quantify as many of these benefits as different benefits. Under this simplified scenario, we possible using a combination of robust methodologies. only considered specific projects undertaken for disaster risk reduction in the EU and neighbouring We identified DiDs as being theoretically the best countries. methodology to calculate the benefits of DRM/DRR investments. However, identifying a suitable 3. LIST STAKEHOLDERS (THAT IS, BENEFICIARIES) counterfactual in addition to the limitation of panel data were challenges that limited our analysis to more Difficulties were faced in defining the beneficiaries fact-finding than sophisticated econometric or that could be reasonably assumed for certain types of statistical estimation. Second and third dividends are investments with broader potential reach or high Annexes 241 positive spillover effects. While all the economic • Modelling future risks. This is the direct subsectors are interconnected, separating out the approach – projecting the future risks will impacts of an investment on all economic subsectors allow us to identify how much damages and across different regions requires detailed input-output losses would have been avoided from DRM data. In the absence of such an ideal set of data and investments. information, we rather took a conservative approach and assumed beneficiaries would be those outlined as • Existing case studies. Indirect approach. direct beneficiaries of intervention. However, some Especially case studies conducted by the WB notable exceptions were made, for instance for EWS. can be useful in this regard. Assuming all necessary data and information are available, 4. SELECT AND MEASURE ALL COST AND we can then extract them to calculate TD and BENEFIT ELEMENTS conduct the BCA. Selection of case studies will be a tricky matter – we need a comparable Overall, we only included what could be a certain DRM project for this purpose. benefit and with sufficient evidence available in order to avoid overestimation. The selection of possible costs • Past disasters and DRM investments. This is and benefits was based on a review of literature, another indirect approach to calculate the first discussion with senior experts, consultations and dividend. If we have data on past investments, brainstorming within the team. The major component and also have a DiD set up (that is,, pre- and of cost comes directly from project documents where post-DRM data from treatment and control direct investments are listed. In addition, we also regions), then we can calculate the first identified other operational costs associated with the dividend using DiD econometric method. implementation of the said project. Wherever possible, we matched costs with each dividend. However, some Risk analytics supported the estimation of avoided costs such as direct investments are overlapping losses and lives saved through comparing impacts across dividends and we do not categorize them by with and without interventions. The principle was to dividends. assess the lives lost and losses incurred in a case study location,  with and without the intervention being In particular, first and third dividends are reasonably studied, using a combination of recorded impacts and outlined and quantified. For the first dividend, simulated impacts. For instance, in areas where an economic benefits stem from quantifying the value of engineered structure is expected to have an impact on lives saved due to interventions. On the other hand, replicable physical processes (for example, flood the third dividend, whenever identified, comes from protection impact on flood extent), we would propose quantifying the co-benefits of such interventions. to model the effect of that protection adjusting the frequency of flooding using a suitable model (for However, the literature around the broader economic example, a disaster risk model). In the case of non- benefits of DRR investments (second dividend) is less engineered interventions, other exposures or impact established. In addition to the common challenges of analysis on a scenario basis were considered, with attribution and data for management, there were also attention to how multiple factors might affect the difficulties in determining the benefits that could be impact beyond the limits of the intervention itself. reasonably considered for disaster risk investments under the second dividend. 5. PREDICT OUTCOME OF COSTS AND BENEFITS OVER THE RELEVANT TIME PERIOD The basis for the prediction of benefits and costs in DRR investments (specifically Dividend 1) is based on For the prediction of costs and benefits over a relevant risk assessments. There are alternative approaches to time period, two parameters are particularly important calculating the direct benefits of DRM when disasters to consider including i) lifespan of infrastructure/ strike outlined below. The report has aimed to model measure considered and ii) valuation of lives saved. future risk as much as possible as the other options were not considered given lack of data, information In this report, the selection of lifespan varied for various and scope of the study. types of investments given different lifetimes of infrastructure, also dependent on the type of Annexes 242 intervention (retrofitting, building, and so on). The time • PESETA III report value with a VSL of €1.3 million period used in the economic analysis of projects per person should reflect reasonable estimates of the full duration of costs and benefits associated with the project, • OECD VSL US$1.8–5.4 million (median of US$3.6 rather than be capped at 20 years or some arbitrary million) cut-off date. • VSL of €400,000 per fatality and €65,000 per injury World Bank’s investments in DRM consider that as per 2014 European Commission BCA guidelines prevention saves lives, so that BCAs associate some numerical estimate to the value of life, the so-called • Adjusting the US VSL US$9.7 million with income VSL. The literature (Braathen, et al., 2009; David, elasticities (Viscusi and Masterson (2017) values) 2000) outlines problems with using VSL for valuation of lives saved. In fact, high VSLs tend to bias impacts • DALYs that can be used for health impact and risks upwards, leading to leading to overestimation assessments globally but are generally not used as of benefits relative to costs. Moreover, country VSLs an economic measure. are relative to GDP, so that any analyses focusing at different than country levels would need to consider 6. CONVERT ALL COSTS AND BENEFITS INTO A how to resolve this/what value to apply (such as COMMON CURRENCY average/median EU GDP and so on). For comparison purposes, it is important to convert all After multiple considerations, this report has costs and benefits into a common currency. Given the undertaken a consistent approach to the calculation regional focus of this analysis, we express all monetary of the VSL. The choice of valuation of lives saved to values in the Euro currency. For this purpose, we use estimate the first dividend required an in-depth review the official annual average exchange rates as reported of the literature and approaches of different institutions in the World Bank’s World Development Indicators. (for example, EC, OECD, and the World Bank) as well as discussions with the client and advisors to ensure Since the BCR is unitless but sensitive to currency an approach that would apply methodological best year, we made sure to express both the costs and practices, ensure the relevance of estimations to the benefits in the same fiscal year. When necessary, we EU context and ensure least possible controversy over use consumer price index (2010 base year, that is, estimated values. 2010 = 100) for converting monetary values from one year to another. We employ the same strategy for all This report has used country-specific BCAs based on historical monetary data. an average value for upper income countries (considered suitable for EU countries). For non-EU 7. APPLY THE DISCOUNT RATE countries under consideration, we have adjusted the VSL for relative income (that is, the ratio of per capita Standard economic analysis links social discount rates GDP of the country of interest to the average per capita to the long-term growth prospects of the country where GDP in the EU) and income elasticity of VSL (set at 1 the project takes place. Higher (lower) growth which is consistent with the suggestion that the income prospects would normally imply a higher (lower) elasticity of VSL is slightly above 1 for non-US discount rate for a particular country. Given reasonable countries). These values are all based on research by parameters for the other variables in the standard Viscusi and Masterman (2017) for VSL or Chiabai, Ramsey formula linking discount rates to growth rates, Spadaro, and Neumann (2018) for VOLY (Value Of Life a 3 percent per capita growth rate translates into a 6 Years) approach would be used wherever applicable percent discount rate, and per capita growth rates of and possible with data available for assessing certain 1–5 percent yield discount rates of 2–10 percent investments such as heatwaves. We will also be using (World Bank, 2016). QALYs, which is more common and used in BCAs as a proxy for time spent in hospitals due to heat. The literature (Gollier, et al., 2014) outlines challenges associated with the choice of discount rates. This Alternative approaches or values considered for applies particularly for investments that are mainly estimating the value of lives saved were as follows: addressing future challenges with high uncertainty but Annexes 243 substantial negative impacts (Weitzman, 2011). It was (NPV) of an investment according to even argued by some to apply a very low discount rate, or close to zero. Considering the debate whether the discount rate should be zero for environmental investments, we resort a low value of social discount rate. NPV is the difference between the present values of World Bank financed projects consider that economic benefits (B_t) and costs (C_t) from all the future years. analysis should link social discount rates to long-term When all the economic benefits are accounted for, a growth prospects of the country where the project project is economically/socially beneficial if NPV>0. takes place. Given reasonable parameters for the other variables, the standard Ramsey discount rate formula Finally, we calculate the ERR which provides the is generally used. The discount rate is relative to GDP, estimated rate of return equating the present values of so that any analyses focusing at different than country benefits and costs. That is, the rate of return at which levels would need to consider what value to apply the DRM project will be equally beneficial to a market- (such as average/median EU GDP and so on). It is based investment project. This is calculated as noted that the JRC also applies specific discount rates, and it is important to understand differences between sectors as DRM investments are cross-sectoral. This report applies varied discount rates aligned with appropriate values for social DRR investments but also market values. Given the controversy over discount 9. PERFORM SENSITIVITY ANALYSIS rates but also the tendency for economists to apply discount rates aligned with market values, the report Regardless of the choice of different parameters, it is includes country-specific discount rates ranging from good practice to provide a sensitivity analysis. This 1.5 percent (which is suggested by the UK treasury for analysis is undertaken with respect to model health-related assessments) to 5 percent (which is parameters that are based on judgement and expert consistent with the Imperial College’s suggested 4 opinions instead of established practices. In this percent discount rate). Specialized discount rates are analysis, since the choice of discount rate is somewhat used for example for environmental investments. arbitrary, it is important to investigate how sensitive the results of this analysis are to different discount 8. CALCULATE THE NPV OF THE PROJECT UNDER rates. In particular, we perform sensitivity analysis for CONSIDERATION the range of discount rates from 1.5 percent to 5 percent. All the projects under consideration have streams of future benefits. These needs, for the sake of Generally, net benefits calculated tend to be quite comparison, to be valued at current prices. That is, we sensitive to the choice of valuation of lives in particular converted all future monetary values to present and lifespan (as related to different disaster scenarios). monetary value using the appropriate discount rate. This is also linked to the choice of disaster risk For this purpose, we use the standard formula: scenarios and therefore these parameters should generally always be included in a sensitivity analysis. 10. OUTLINE POTENTIAL EQUITY ISSUES It is widely recognized that most DRM projects have positive net benefits, but the concrete distributional where P and F denote present and future values, t effects of such projects are mostly unknown. A known denotes time and τ denotes time difference between fact is that the impacts of disasters disproportionately present and future. Finally, r denotes the discount rate. affect poorer households (World Bank 2020a) and it would therefore be of crucial importance to assess the In addition, we calculate the net present benefits differential impacts of DRR investments as the value of Annexes 244 avoided losses in terms of developmental impacts and missing, these equity, environmental and reduced recovery times may differ depending on the intergenerational factors could be considered and characteristics of individuals or households benefitting addressed through scoring/rating based on qualitative from it. However, an investigation into the distributional analysis. effects of DRM investments will require quantile regression analysis based on detailed household level 11. SUMMARY AND RECOMMENDATIONS survey data, which is not available for our analysis. The triple dividend approach to identifying additional Equitable distribution of benefits intrinsically depends societal benefits is becoming increasingly popular, on the capacity of local communities to capitalize on especially for environmental project appraisals in the employment opportunities created in the process recent years. While the multi-faceted benefits were of project implementation. For example, construction qualitatively justified, this analysis quantifies as many of large DRM infrastructures requires labour, who can of them as possible using the best possible approach. be locally recruited. One potential way of ensuring this In addition to the educational value of this analysis, we could be to include local communities in the also identified important caveats in conducting a full- implementation of the project, either through allocating scale triple dividend BCA for DRM projects. property rights or through legally binding contracts with local authorities. However, such policies might Available information enabled us to identify the first have their own costs and benefits, and require more dividend in all the cases, and the third dividend in most focused analysis. of the cases. However, the complicacy remains around identifying and quantifying the second dividend. Most Moreover, employment opportunities furthered by of the benefit items under the second dividend may large DRR investments may not be permanent. Local arise from alternative sources, implying that a workers with the experience of working in those dedicated investigation with the scope of primary projects will have to seek future employment elsewhere survey is necessary for identifying those benefits, instead of locally. It is possible that experienced which is beyond the scope of this analysis. workers may not be available locally, which will complicate the project appraisal even further. While the report has aimed to further as much as possible comprehensive analysis, many caveats still Environmental factors should be covered by Triple remain. In addition to difficulties of estimating more Dividend 3 considerations. However, those have not intangible benefits included in the third dividend such been estimated it is worth at least qualitatively as environmental benefits or externalities, distributional describing the potential impacts the investment could impacts in terms of poverty and employment growth have, positive and negative, in terms of environmental could also not be estimated. This will remain as a externalities or climate change. Whenever data is limitation, and a potential future scope of investigation. 5.3. Annex 3: Additional Information on the Methodological Approach ALTERNATIVES TO TYPICAL BCA PROCEDURES historical data for probabilistic estimations of losses), (b) consideration of potential impacts of climatic Several studies have identified the limitations and changes and high uncertainty or irreversibility, (c) criticized the use of BCA to evaluate DRM investments. evaluation of reasonable durations of benefits, and (d) These studies (Mechler, 2016; Kull, et al., 2013; broader considerations of processes of vulnerability Shreve & Kelman, 2014) have argued for a shift in the and technical limitations for the estimation of non- emphasis on BCAs and proposed alternative economic market goods. The studies have also highlighted analysis tools. They have mainly criticized the lack of potential negative externalities from DRR measures (a) risk-based analysis and sensitivity analysis such as environmental or health impacts and undertaken as part of BCAs (due also to lack of distributional considerations (given the emphasis on Annexes 245 maximizing social welfare instead of optimizing the the most significant challenges when incorporating distribution). Discretionary discounting and ethical climate change in BCA is the calculation of total concerns over associating a monetary value to life benefits when longer time horizons are considered have been mentioned as additional challenges to use and where there may be considerable uncertainty. BCA. They also propose to shift from purely In particular, broad-scale climate changes infrastructure-based/’hard’ solutions to more systemic represented in coarse-resolution regional climate interventions emphasizing preparedness/’soft’ models cannot be used with confidence to solutions. determine local trends in precipitation at the scale of a single case study without significant un- There are several alternatives to BCA proposed in certainty, added to which is the likely contribution literature. These approaches can be valuable to of other environmental and socio-economic factors determine under which conditions a particular (for example, catchment management and investment might be considered economically viable development of floodplains) affecting changes in and to collect useful information (expert and flood hazard in the same time frame. This will imply stakeholder judgment) on the possible consequences that instead of taking an optimal decision, implying of a project and opinions about parameters (river flows reliable descriptions of the future, we may engage or bridge span for floods for example). The approaches in a process of robust decision-making that would are particularly critical for consideration when enable the best outcomes under a range of futures investing in infrastructure that has a long life span. and worldviews. Like the criticality model, this approach enables us to look beyond the • Cost-effectiveness analysis (CEA) is used to identify infrastructure and consider the broader user and least-cost options to meet a specific, predefined welfare perspective to investments with potential target or policy objective. Because project costs are large impacts. Hallegatte et al. (2012) even the variable of consideration, CEA does not require conclude that there should always be a discussion the quantification of benefits and can therefore also of a menu of possible investments in various be applied with intangible or more qualitative contexts and a variety of methodologies applied. benefits. Robust decision-making approaches involve a process • The MCA methodology emphasizes low cost and is of dialogue given acceptance of uncertainty and are by organized around objectives, criteria, and indicators nature iterative and adaptive. However, different that can be compared to the performance of approaches can be used, including ‘no-regret’ different (policy) options over time in achieving strategies (for example, controlling leakages in water one’s stated objectives (economic, social, pipes) or minimizing regrets (building larger reservoirs environmental, and fiscal criteria). A form of MCA is when applicable), reversible and flexible strategies multi-criteria evaluation (MCE), also called criticality (adjustable insurance and EWS), safety margin analysis. strategies (calibrating drainage infrastructure with higher runoff figures), and strategies that reduce Criticality analysis (Rozenberg, et al., 2019) has been decision-making time horizons (stepwise investments used in several contexts for the prioritization of in infrastructure starting with lower cost options). infrastructure projects and maintenance and to combine social and economic assessments of critical POTENTIAL ECONOMIC BENEFITS OF interventions. ECOSYSTEM SERVICES • Differentmethodologies have been proposed for Ecosystem services should be valued in a similar decision-making under deep uncertainty (Marchau, manner to any other economic asset: their social value 2019). These are BCA under uncertainty, BCA with (that is, aggregate WTP) must equal the discounted a real options approach, robust decision-making, NPV of these flows. However, the values attributed to and climate-informed decision analysis and all have these services can only be measured indirectly, since different strengths for different applications. One of they are derived from supporting and protecting Annexes 246 activities (that is, strategically implemented DRM The production function approach involves a two-step projects) that have directly measurable values.41 procedure. The procedure includes assessing (i) the Following Barbier (2007), a production function physical effects of changes in a biological resource or approach42 can be used, which requires the ecological service on an economic activity are information on the change in an ecosystem – in terms determined; (ii) the impact of these environmental of service that people care about – to place a value on changes is valued in terms of the corresponding those services.43 This is particularly relevant for change in the marketed output of the relevant activity. regulatory and habitat functions that support or protect Key features of this production function approach economic activities. If the benefits of these services include: (i) an ecological function is effectively a direct enhance the productivity of economic activities, or input into production, and the value marginal product protect them from possible damages, the aggregate of changes in this function can be derived to determine WTP for such services can be estimated as if they were its value; (ii) adopts either profit-maximizing or social a factor input in these productive activities. welfare maximizing framework; (iii) can be applied in a static or a dynamic framework. ECOSYSTEM ECOSYSTEM PROCESSES AND COMPONENTS ECONOMIC SERVICES (BENEFITS) FUNCTIONS Regulatory Role of ecosystems in biogeochemical Ultraviolet-B protection Functions processes Maintenance of air quality Gas regulation Influence of land cover and biologically mediated processes Influence of climate Climate regulation Influence of system structure on dampening Maintenance of temperature, precipitation Disturbance environmental disturbance prevention Storm protection Role of land cover in regulating run-off and Flood risk reduction Water regulation river discharge Soil retention Drainage and natural irrigation Role of vegetation root matrix and soil biota Soil formation in soil structure Maintenance of arable land Nutrient regulation Weathering of rock, organic matter Prevention of damage from erosion and accumulation siltation Waste treatment Role of biota in storage and recycling of Maintenance of productivity on arable land nutrients Maintenance of productive ecosystems Removal or breakdown of nutrients and compounds Pollution control and detoxification Habitat Functions Suitable living space for wild plants and Maintenance of biodiversity animals Niche and refuge Maintenance of beneficial species Suitable reproductive habitat and nursery Nursery and grounds Maintenance of biodiversity breeding Maintenance of beneficial species Source: Barbier (2007, 2009) 41 For example, coastal and estuarine wetlands, such as tropical mangroves and temperate marshlands, act as “natural barriers” by preventing disturbance of storm events, thus providing valuable storm prevention and flood mitigation services. 42 Such PF approaches are being increasingly employed for a diverse range of environmental quality impacts and ecosystem services, including the effects of flood control, habitat-fishery linkages, storm protection functions, pollution mitigation and water purification. 43 On the other hand, stated preference studies (contingent valuation, conjoint analysis and choice experiments) additionally require that the change in the ecosystem must be explained in the survey instrument in a manner that people will understand and not reject the valuation scenario. Annexes 247 5.4. Annex 4: Background Information on case studies EARTHQUAKE behavioural economics found that individuals rarely undertake measures that reduce risk partially, but they Summary of WTP methodologies are willing to considerably invest in adaptation measures that reduce risk to zero. This was shown for A contingent valuation is a method of estimating the example in a study by Botzen, Aerts, and van den value that a person associates with a good or service. Bergh (Botzen, et al., 2009) to determine households’ This can be measured in two ways: WTP and willingness willingness to invest in flood insurance versus elevating to accept (WTA). The first one seeks to comprehend an newly built structures in order to adapt to the flood risk individual’s willingness to obtain a good/service, while that climate change imposes on the Netherlands. The the latter focuses more on how much it would take for results indicated that 52 percent of homeowners someone to give up a good/service. WTP and WTA are are willing to make a substantial investment of €10,000 most commonly used to place value on commodities to elevate a new house to a level that is safe from that are not exchanged in a hypothetical marketplace. flooding. A household’s decision to invest in an As a result, this methodology is most commonly elevated home strongly stems from their expectations applied to public goods and private non-market goods, on the negative effects of climate change, perceptions and in the context of the environment, this pertains to of flood risks, individual risk attitudes, and how close issues including, but not limited to, improvements to they live to a main river. water or air quality, national parks, and reducing the risk of death. As noted from the thought process Dutch citizens go through when deciding to invest in elevating their Researchers measure a person’s environmental WTP house to avoid flood risk, expectations and perceptions or WTA by conducting environmental valuation surveys are critical to determining an individual’s WTP or WTA. that measure both their stated preferences as well as In fact, for people in developing countries, the WTP for their revealed preferences. In “Aesthetic Value of an environmental protection premium is determined Lakes and Rivers” by Corrigan, Egan, and Downing by a combination of beliefs and perceptions about (2009), the co-authors found that people would be one’s own knowledge rather than facts about climate willing to visit Clear Lake (Iowa, USA) more often if the change. This supports insights from other research lake’s water quality was improved. that it is generally more effective to appeal to people’s existing values and beliefs in order to communicate There is some concern about how accurately the importance of investing in climate change or taking hypothetical WTP overestimates a person’s real WTP. actions to mitigate the effects of climate change. To understand this, Blumenschein et al. (2008) compared two methods of removing hypothetical bias: In Song, Wang, and Li (2016) paper, “Residents’ cheap talk approach and certainty approach. A cheap attitudes and WTP for solid waste management in talk approach takes a survey respondent’s answer as Macau,” researchers structured their survey in four is, meanwhile the certainty approach further asks parts: (1) general questions regarding the basic participants how confident they are in their answer. environmental issues, (2) questions measuring They found that unprocessed contingent valuations respondents’ knowledge and attitudes on solid waste have a hypothetical bias, and that this could be easily recycling, (3) a description of the WTP, and (4) removed by implementing a follow-up question about questions collecting socio-economic data on the the certainty of their responses. respondents. By measuring residents’ insight on the environment, the type of adaptation measure in Another factor that impacts someone’s WTP is the question, and their demographics, Song and his co- framing of a hypothetical situation during a contingent authors are able to paint a better picture of the types of evaluation exercise. In order to limit the projected people in the neighbourhood who more willing or less increase in natural disaster risks caused by climate willing to pay for solid waste management. They are change, adaptation measures are recommended to also able to test if there is a correlation between an partially or fully eliminate this risk. Literature in individual’s views and demographic factors or the Annexes 248 degree to which they understand waste management (both the human and material resources needed). and/or broader environmental issues. Example modules defined under the 2014 or 2018 Implementing Decisions include, for example, Civil Protection Capacity Building Advanced Medical Posts, BCRN capabilities, Emergency Medical Teams, Emergency Temporary The following descriptions of the UCPM Knowledge Camp, Flood Containment, Forest Firefighting, Field Network and the Albania Earthquake are useful as Hospital, Flood Rescue, High Capacity Pumping, background information for the work showcased in Urban Search & Rescue, Medical Evacuation, section 3.2.4. Technical Assistance and Support, Water Purification (most with several sub-categories within these 1. UCPM and Knowledge Network classes). In 2019, civil protection experts took part in nearly 50 UCPM training courses. 14 MODEX exercises UPCM/Union Civil Protection Knowledge Network - and 2 full-scale exercises took place, and plug-in and The 2019 revision to the UCPM created a Union Civil host nation support exercises were introduced. 48 Protection Knowledge Network to bring together a countries in and around Europe participate in the number of existing civil protection and disaster exchange of experts programme, with experts being management programs under one umbrella to support hosted by 36 countries. experts, practitioners, policy-makers, researchers, trainers and volunteers to increase DRM knowledge 2. Albania UCPM and EU/World Bank/UN response to and its dissemination within the UCPM. major 2019 earthquakes The various programs under the Knowledge Network In 2019, Albania was struck by two major earthquakes: include: a magnitude 5.6 struck on 21st September, and a magnitude 6.4 on 26th November. The 21st September UCPM Training - Offering both DRM coordination and mainshock had an epicentre 5km Northwest of Durres technical experts training from a programme of 11 (35km West of capital, Tirana) and, according to the courses. These range from basic training to high-level assessment of Albania’s General Directorate for Civil sessions for future mission leaders, including Emergencies (GDCE), 3329 residential buildings were specialised courses such as security training and damaged. The 26th November mainshock was 22 km assessments. Northeast of Durres (30km from Tirana) and, according to the joint EU-World Bank-UN PDNA, damaged Exchange of Experts in Civil Protection – Allows for 11,490 housing units, injured more than 913 people, secondment of civil protection experts between UCPM caused €843m in direct damages and tragically MS, PS and eligible third countries. Through exchanges caused 51 fatalities. 48 people were rescued from on topics like firefighting, communication, search and collapsed buildings by first responders. rescue, or new and emerging threats, participants gain practical experiences and knowledge of the different The UCPM was activated for both events, and a joint approaches of national systems. EU-WorldBank-UN PDNA was conducted after the November event. Civil Protection Exercises - Alongside full-scale exercises, which are organised by civil protection The September activation saw DG ECHO’s ERCC authorities of countries and co-financed by the EU, deploy an EUCPT of experts from 6 EU MS (NL, IT, UK, modules field and table-top exercises (EU MODEX) are FI, DE, EL) and Norway, an EU liaison officer, and a organised under the supervision of the UCPM. regional information officer of DG ECHO. The EUCPT facilitated the coordination of incoming in-kind EU MODEX exercises - test the self-sufficiency, assistance from 13 countries, including 11 EU MS interoperability, coordination and procedures of (HU, HR, AT, EL, FI, SL, SK, IT, FR, BU, LV) and participating experts, 'modules' and other Response Montenegro and Norway. The EUCPT included a Capacities. A 'module' is defined under Decision No Structural Engineer who, in close exchanges with 1313/2013/EU as a self-sufficient and autonomous national and local authorities and engineers, identified predefined capability or a mobile operational team areas for improvement in the damage assessment Annexes 249 process and methodology. Working with the relevant presents quantitative findings and recommendations authorities and institutions, a unified damage on the education, health, housing, infrastructure, assessment method was proposed based on best productive and DRR sectors, as well as findings on Albanian practices supplemented by international social protection. standards. EXTREME HEAT In response to the 26th November activation, ERCC deployed 2 EUCPTs (alpha and bravo), with Alpha Detailed methodology for UHI analysis deploying on 27th November, and handing over to team Bravo on 4th December. A two-person UNDAC Methodological aspects of the triple dividend approach team was also embedded into the EU-led team. The for green and white solutions in UHI mitigation. teams facilitated the coordination of in-coming modules and in-kind assistance. USAR coordination Epidemiological models provide for the estimation of was led by the Italian team, and other USAR teams the level of risk associated with extreme temperatures. included those from Greece, Romania, France, Israel, These models are distributed lag nonlinear models Turkey and others. Given the relatively small number of which allows for the estimation of the relative risk of active rescue sites, much of the USAR capacity was extreme temperatures by accounting for lagged effects not being engaged fully, and so EUCPT-alpha used the on mortality and the nonlinear nature (Gasparrini, et available USAR engineers to assist the Albanian al., 2010). To estimate the heat-related excess authorities with damage assessment. mortality in Vienna, Austria, this modelling procedure was carried out along with an estimation of the EUCPT-alpha established the DACC to assist the attributable number of deaths according to the Albanian authorities with damage assessment, utilizing methodology of Gasparrini and Leone (2014). By the available USAR Engineering capacity and building pursuing such an approach, we also capture the main on the recommendations of the September UCPM effects of heatwaves (Gasparrini & Armstrong, 2011). activation. The DACC was operated jointly by EUCPT, UNDAC and USAID, and as the DACC proved effective, Daily all-cause death counts for Vienna and daily the Albanian government made further request for maximum temperature for 2003-2009 were used for international engineers, both bilaterally and through modelling the temperature-mortality relationship the UCPM, culminating in 185 international engineers while controlling for the effects of daily air pollution from 18 countries registering with the DACC and levels (O3, NO2, PM10). To capture the exposure- coordinated by them to assist ongoing damage response and lag-response relationships, a cross-basis assessment. function [CB(Tempt)] is defined with a quadratic B-spline (two internal knots of temperature with 4 The PDNA occurred during 18th December – 24th degrees of freedom) for the exposure-response January, encompassing partners from the EU, World function and a natural cubic B-spline (three equally- Bank and UN who provided financial and Technical spaced knots on the log scale) for the lag-response for support to conduct the assessment in addition to the use in the quasi-Poisson regression model: resources the government made available. The PDNA where we controlled for seasonality and long-term and mortality and the empirical estimates of the trends with a natural spline of time [NS(Timet, 8 df/ confidence intervals obtained through Monte Carlo year)], days of the week [DOWt], and air pollution [O3t, simulations can be seen below (see Figure 49). NO2t, PM10t]. The association between temperature Annexes 250 Figure 49: Overall cumulative association between temperature and mortality Source: Gasparrini and Leone (2014) Note: the graph represents the association between mortality (in the scale of relative risk) and temperature distribution. The association is represented in the scale of relative risks. The dotted and dashed vertical lines represent the centre point and values for defining extreme heat and cold, respectively. With this approach, we calculated an annual number of hot days in a cell (c), HDred,c is the reduced average of heat attributable deaths above a daily maximum annual number of hot days given the scenario and temperature of 30ºC to be 106 deaths (ranging 39- Popc is the population in the cell. In this spatially 165 of 95 percent confidence intervals). Given the explicit approach, we sum over the cells to estimate spatial dimension of UHI effects, we include address the total reduced heat-related mortality counts given exposure the heat hazard by employing the urban the scenario of measures and propagate this amount climate models already produced for Vienna (Žuvela- for the following 50 years. Aloise, et al., 2018), population distribution on a raster of Vienna and the results of the temperature-mortality regression. The results of the urban climate model Extreme heat can have significant impacts on both show the current annual average number of hot days indoor and outdoor labour productivity in Europe, in a year for each cell in the raster and the average leading to large losses economic losses (Gosling, reduced number of hot days given the set of green Zaherpour, and Ibarreta 2018). Given time and data measures or a combination of green and white constraints, we employ the approach of Hübler, measures. Given the attributable fraction of deaths Klepper, and Peterson (Hübler, et al., 2018) to estimate due to heat (AF), the total deaths (TD) and years (Y) the reductions in labour productivity loss with the over the time period, and the total population (Poptot), scenarios of implementation that would otherwise we estimate the reduced heat-related mortality counts occur on hot days. Bux (2006) found that productivity (Dred,c) in Vienna for a scenario of measures: losses can range between 3-12 percent for temperatures of 26-36ºC. For hot days, we assumed an averaged reduced worker productivity loss of 7 percent (Vöhringer, et al., 2017). To estimate the reduced loss in productivity for the city of Vienna, we scale down to the city according to the population where HDavg,c is the current average annual number (Pop). Annexes 251 Tourismus, 2018). Since Vienna does not currently have a high uptake of air conditioning, we assume the cooling savings are an estimate the value of lower indoor temperatures to society. We calculate the loss in GRP according to the average number of reduced hot days per year (HD), the current Green roofs also improve stormwater management in GRP per capita, the average productivity loss on a hot urban areas by reducing the amount of stormwater day (p; 7 percent) and the wage share (w; 69 percent). run-off being conveyed in municipal sewer systems. We assume a 50 percent decrease in the run-off from Several economic and environmental benefits are greened roof surfaces. Although Vienna does not have assessed for green infrastructure under the third a specific stormwater charge per area of sealed dividend. Energy efficiency improvements are valued surfaces, many Austrian cities, such as Klagenfurt and given the additional insulating layer of green roofs Salzburg, charge annual rates of 2.2 €/m2 for sealed (Berardi, GhaffarianHoseini, and GhaffarianHoseini area. We estimate these benefits by multiplying the 2014). We compare the differences in the thermal total greened area with a 50 percent reduction of the properties of green and conventional roofs according charge. Furthermore, green roofs provide habitats in to Clark, Adriaens, and Talbot (2008) to estimate urban areas for organisms, which was otherwise non- heating and cooling savings as in the following. existent (Currie & Bass, 2010). Since the quality of the green roof is only a fraction of a completely natural space, we value the improvement to urban habitats with 15 percent of the cost (Bianchini & Hewage, 2012) for restoring land (MacMullan, et al., 2009). Lastly, green roofs support urban areas in pollution mitigation and carbon dioxide sequestration. We take removal rates of pollutants, including nitrous oxide, ozone, sulphur dioxide and particulate matter (Yang, The heating (Hsav) and cooling (Csav) savings are et al., 2008) and carbon sequestration rates of green calculated given the thermal conductivities of roofs (Getter, et al., 2009) to estimate the reduction conventional (Rconv) and green roofs (RGR) and the these negative externalities to society. The valuations average heating (HDD15°C) and cooling (CDD18°C) incorporate the average of the high and low shadow degree days for the past five years of Vienna (BIZEE, prices of carbon (World Bank, 2017b), which are 2020). To estimate the monetary amounts of savings, increasing into the future, as well as the shadow prices we use the average price of electricity of 0.196 €/kWh of the air pollutants according to EU-wide damage and the average price of natural gas heating at 0.068 costs (World Bank, 2017b). €/kWh (Bundesministerium für Nachhaltigkeit und Annexes 252 MASS MOVEMENT / LANDSLIDE Flow chart for criticality analysis process of roads in Albania Figure 50: Flow chart showing Albania’s climate-resilient roads’ project approach for parts 1 and 2 Source: Xiong & Alegre, 2019 Annexes 253 5.5. Annex 5: Netherlands results from national assessments and BCAs over a century Table 89: Highlights of one century of BCAs for Dutch flood risk management: conclusions and applications Source: Bos and Zwaneveld 2017 Annexes 254 Table 90: Highlights of one century of BCA’s for Dutch flood risk management: benefits and uncertainty estimations Source: Bos and Zwaneveld 2017 Table 91: The history of Dutch BCA Source: Bos and Zwaneveld 2017 Annexes 255 5.6. Annex 6: Consultations table for case studies INSTITUTIONS CONTACTED (WITH TITLE NUMBER OF TELEPHONE EMAIL WITH FOLLOW-UP EMAIL NUMBER NAME OF CASE STUDY OF THE CONTACT PERSON, PEOPLE CONVERSATION & QUESTIONNAIRE EXCHANGE IF AVAILABLE) CONTACTED DISCUSSION 1 Strengthening of Department of Civil Protection, Ministry 2 Yes Yes Yes residential buildings in Italy 2 Building safer schools World Bank 3 Yes Yes Yes 3 Resilient transport World Bank 1 Yes Yes No modelling 4 Resilient roads and escape POR FESR Campania 2 Yes No No routes 5 Climate resilient rail World Bank 2 Yes Yes Yes transport 6 Rate of Return on Health National Institute for Health Research 3 Yes Yes No Investments 7 Response capacity of fire Mol-DG Fire Rescue Service of the 2 Yes Yes Yes and rescue services Czech Republic 8 New vehicles for voluntary Marshall Office of Lublin, Voivodeship 1 Yes No No fire service units executive board 9 Strengthen firefighters to Joint Secretariat Czech Republic - 1 Yes No No improve preparedness Republic of Poland 10 Civil protection and Interreg V-A - Spain-Portugal European 1 Yes Yes Yes emergency response Commission Programme (Manager) around the border 11 Preparedness for Hydromet agency in France (Météo 1 Yes Yes Yes heatwaves France France) 12 Flood protection and World Bank 1 Yes Yes Yes liveability Annexes 256 13 Flood defence RIOCOM 4 Yes Yes Yes infrastructure Austria (Machland dam) 14 Flood risk management on International Sava River Basin 6 Yes Yes No the Sava river Commission, Interreg Europe 15 Flood protection and job Deputy Minister of Development and 2 Yes Yes No creation Investment 16 Flash floods resilience European Commission (Director 1 Yes No No General) 17 Flood protection in cross- Department of European Union 1 Yes Yes No border areas Projects, Regional Development Fund of Central Macedonia (MSc Civil Engineer) 18 Green infrastructure to European Commission 1 Yes Yes Yes reduce surface water flooding 19 Storm surge barriers RWS (Economist) 1 Yes Yes Yes 20 Irrigation and resilience to Spain Ministry of Environment and 1 Yes No No droughts Agriculture 21 Water security APA - Agência Portuguesa do Ambiente 1 Yes Yes No 22 Green roofs in Vienna FFG/BMVIT, City of Vienna Austria 1 Yes Yes Yes 23 Retrofitting buildings for World Bank 3 Yes Yes Yes safety 24 Earthquake early warning World Bank 3 Yes Yes Yes in Bucharest 25 Portugal managing University of Coimbra in Coimbra, 3 Yes Yes Yes wildlife-urban interface: Portugal; Agency for the Integrated Industries Management of Wildfires 26 Portugal managing University of Coimbra in Coimbra, 3 Yes Yes Yes wildlife-urban interface: Portugal; Agency for the Integrated Homes Management of Wildfires Annexes 257 27 Multifunctional ship to Ministry of the Environment of Estonia 3 Yes Yes No tackle marine pollution (Head of Marine Environment Department), Police and Border Guard Board (Police Captain) 28 Dealing safely with European Commission 2 Yes Yes Yes hazardous waste 29 Cleaning up uranium site Ministry of Environment of Czech 2 Yes Yes No Republic, State Environmental Fund 30 Security of nuclear plants ISRN, Institut de Radioprotection et de 2 Yes No No Surete Nucleaire 31 Flood early warning system Belgium Environmental Agency 1 Yes Yes Yes Flanders 32 INTERREG project Tweed forum 1 Yes Yes Yes Eddleston Water 33 Sigma plan – coastal vlaamsewaterweg 1 Yes Yes Yes protection of the Scheldt Estuary 34 Union Civil Protection Disaster Preparedness and Prevention 3 Yes Yes Yes Knowledge Network in Initiative for South-EasternEurope Albania Earthquake (Head of the Secretariat); Knowledge Network 35 Union Civil Protection Disaster Preparedness and Prevention 3 Yes Yes Yes Knowledge Network in Initiative for South-EasternEurope Croatia Earthquake (Head of the Secretariat); Knowledge Network 36 Fuel management in University of Coimbra, Portugal, 2 Yes Yes Yes Europe Department of Mechanical Engineering; EFI group 37 Alerting and Preparedness Portugal Health Regulatory Authority 1 Yes Yes Yes in Portugal 38 Alerting and Preparedness Wildfire Management Consulting & 1 Yes Yes Yes in Greece Training (Founder) Annexes 258 39 Forest management for Austria Federal Ministry for 1 Yes Yes Yes wildfire prevention Sustainability and Tourism 40 River Climate Park for Rivierklimaatpark project Team 1 Yes Yes No flood protection 41 Value of meteorological World Meteorological Organization 1 Yes Yes Yes services Finland 42 Value of the Meteorological Wea. Climate Soc (Economist) 1 Yes Yes Yes services for the transport sector 43 Wetlands restoration Danish implementing agency, 1 Yes Yes Yes 44 Protection against erosion Consultancy for Environmental 1 Yes Yes No and coastal flooding Economics (CEEP) & Policy 45 Restoration of coastal LIFE/EU 1 Yes Yes No habitats 46 Earthquake proof hospital Assessorato Regionale della Salute 1 Yes Yes No 47 Value of the Meteorological London Economics 1 Yes Yes Yes services 48 Network of cities for LIFE Veneto ADAPT 1 Yes Yes No climate change adaptation 49 Multiple resilience European Commission 1 Yes No No measures and economic opportunities 50 Ecological water security La Région Provence Alpes Côte d'Azur 1 Yes Yes No 51 Flood Resilience World Bank 3 Yes Yes Yes 52 Mutual assistance and Interreg V-A - Spain-Portugal European 1 Yes No No managing cross-border Commission Programme (Manager) risks 53 Drought planning in water Spanish National Research Council 1 Yes No No resource systems Annexes 259 54 Protection of sea from Parliamentary Secretary for EU Funds 1 Yes No No wastewater contamination - Planning and Priorities Coordination Division 55 Flood protection and Hungary Ministry for Innovation and 1 Yes Yes No agriculture Technology 56 Blue-green infrastructure City of Dordrecht 2 Yes Yes Yes for flood protection 57 Investments in National World Bank 2 Yes Yes No Meteorological and Hydrological Services 58 COVID19 Lessons Learned World Bank (Former STC) 1 Yes Yes Yes 59 Drina Flood Protection DPPI SEE Secretariat 1 Yes Yes Yes 60 Resilient rebuilding of Regione Umbria- Servizio 3 Yes No No cultural buildings following Programmazione Comunitaria an earthquake 61 Effective monitoring and University College London, Earthquake 1 Yes Yes No early warning investments Engineering of earthquake and nuclear risks 62 Investments in National World Bank 2 Yes No No Meteorological and Hydrological Services 63 Nature-based Solution European Commission: 1 Yes Yes Yes Investments in Flood Risk DG ECHO Reduction 64 Overall Report European Commission: 8 Yes Yes Yes DG ECHO, DG ECFIN, DG CLIMA, DG ENV, DG REGIO; JRC Annexes 260 5.7. Annex 7: Full overview of final case studies by hazards, sectors, countries and funding Note: This list is not including all case studies that were considered for this report, be considered that some case studies were dropped, and others added since the which were more than 100 (as included in the inception report), although it has to inception report delivered in June 2020. NAME OF CASE TYPE OF FUNDING TOTAL FUNDING CLOSING NBR COUNTRIES SECTOR HAZARD TYPE OF ANALYSIS STUDY  INVESTMENT INSTITUTIONS (EURO) DATE 1 Strengthening of Italy Seismic Housing and Earthquake Quantitative, National 1,000,000,000 On-going residential buildings Strenghtening public buildings Own Analysis in Italy 2 Cultural heritage Italy Seismic Housing and Earthquake Qualitative EU 10,000,000 On-going protection Strenghtening public buildings; cultural heritage 3 Climate-proofing United Urban Heat Island Housing and Heatwaves Qualitative EU and 1,615,636 2016 social housing Kingdom Effects public buildings national 4 Building safer Turkey Seismic Education Earthquake (Partial) World Bank 270,000,000 2024 schools Strenghtening Quantitative, based on the literature 5 Schools in seismic Across Seismic Education Earthquake Quantitative, National 57,866,800,000 hypothetical countries across Europe Strenghtening Own Analysis scenario Europe 6 Resilient transport Serbia Structural Transport Flood Qualitative World Bank 830,000 2018 modelling protection 7 Resilient roads and Italy Preventive Transport Volcano Qualitative EU and 53,415,000 2013 escape routes Investment national 8 Climate resilient rail Romania Structural Transport Flood Qualitative EU 2,000,000,000 2020 transport protection Annexes 261 NAME OF CASE TYPE OF FUNDING TOTAL FUNDING CLOSING NBR COUNTRIES SECTOR HAZARD TYPE OF ANALYSIS STUDY  INVESTMENT INSTITUTIONS (EURO) DATE 9 The Case of EU Equipment for Health Epidemic (Partial) EU 4,500,000,000 2021 (tbc) Pandemic health-related Quantitative, Preparedness disasters based on the literature 10 Rate of Return on EU (Italy, UK, Return on Health Epidemic (Partial) National varies 2020 Health Investments Sweden, Investment of Quantitative, Netherlands) National Public based on the Health Program literature 11 Response capacity Czech Cross-border Emergency Wildfires Qualitative EU and 58,377,714 2013 of fire and rescue Republic support, response national services coordination mechanisms and capacity building 12 New vehicles for Poland Rescue and Emergency All hazards Qualitative EU and 7,510,000 2018 voluntary fire service emergency response national units response equipment 13 Strengthen Czech Cross-border Emergency Wildfires Qualitative EU and 7,936,284 2019 firefighters to Republic/ support, response national improve Poland coordination preparedness mechanisms and capacity building 14 Civil protection and Portugal/ Cross-border Emergency Wildfires Quantitative, EU and 3,856,250 2020 emergency response Spain support, response Own Analysis national around the border coordination mechanisms and capacity building 15 Early Warning and Danube early warning and Early warning Droughts Qualitative national 1,974,750 2019 preparedness for region capacity building Droughts for droughts preparedness Annexes 262 NAME OF CASE TYPE OF FUNDING TOTAL FUNDING CLOSING NBR COUNTRIES SECTOR HAZARD TYPE OF ANALYSIS STUDY  INVESTMENT INSTITUTIONS (EURO) DATE 16 Preparedness for France Early warning Early warning Heatwaves Quantitative, National 286,933 2020 heatwaves France Own Analysis 17 IT and Poland Early warning Early warning All hazards Qualitative EU and 75,538,065 2013 communication for national early warning 18 Integrated flood Greece/ Early warning Early warning Flood Qualitative EU and 1,159,248 2020 services and climate Cyprus national change awareness 19 Intelligent system Greece Early warning Early warning All hazards Qualitative EU and 922,631 2020 for better disaster national response 20 Early warning for Spain Decision making Early warning Volcano Qualitative EU and 1,590,032 2019 volcanic activity for evacuation national 21 Information and Malta Early Warning Communication/ All hazards Qualitative EU and 7,000,000 2019 early warning for ICT national preparedness 22 Flood protection Poland Structural Industry Flood (Partial) World Bank 505,000,000 2020; 2023 and livability protection Quantitative, and national based on the literature 23 Delta Works Netherlands Structural Housing and Flood Qualitative national 5,000,000,000 1997 protection Public Buildings 24 Flood defense Austria Structural Water; Housing Flood Quantitative, National 182,600,000 2020 (tbc) infrastructure protection and Public Own Analysis Austria (Machland Buildings damm) 25 Flood risk Croatia/ Nature-based Response & Flood Qualitative EU and 1,626,842 2020 management on the Serbia Solutions Equipment national Sava river 26 Flood protection and Greece Structural Housing and Flood Qualitative EU and 84,000,000 2013 job creation protection Public Buildings national Annexes 263 NAME OF CASE TYPE OF FUNDING TOTAL FUNDING CLOSING NBR COUNTRIES SECTOR HAZARD TYPE OF ANALYSIS STUDY  INVESTMENT INSTITUTIONS (EURO) DATE 27 Flash Flood Malta Structural Housing and Flood Qualitative EU and 62,505,662 2013 resilience protection Public Buildings national 28 Flood protection in Bulgaria/ Structural Housing and Flood Qualitative EU and 9,902,960 2020 cross-border areas Greece protection Public Buildings national 29 Floodplain United Nature-based Agriculture Flood (Partial) National 3,079,000 2017 Restoration Kingdom Solutions Quantitative, based on the literature 30 Green infrastructure Spain Nature-based Housing and Flood Qualitative EU and 1,817,972 2019 to reduce surface Solutions Public Buildings national water Flood 31 Storm surge barriers Netherlands Nature-based Housing and Flood Qualitative National 450,000,000 2007 Solutions Public Buildings 32 Irrigation and Spain Irrigation and Agriculture; water Droughts (Partial) EU and 31,300,000 2013 resilience to water provision Quantitative, national droughts system based on the literature 33 Water security Portugal Irrigation and Agriculture; water Droughts Qualitative EU and 65,000,000 2013 water provision national system 34 Green roofs in Austria Urban Heat Island Buildings Heatwaves Quantitative, National varies On-going Vienna Effects Own Analysis 35 Retrofitting Romania Seismic Emergency Earthquake (Partial) World Bank 54,432,000 2024 buildings for safety Strenghtening response; Public Quantitative, buildings based on the literature 36 Earthquake early Romania Early Warning Emergency Earthquake Quantitative, EU and 3,064,328 2013 warning in response; Public Own Analysis national Bucharest buildings; Early Warning Annexes 264 NAME OF CASE TYPE OF FUNDING TOTAL FUNDING CLOSING NBR COUNTRIES SECTOR HAZARD TYPE OF ANALYSIS STUDY  INVESTMENT INSTITUTIONS (EURO) DATE 37 Portugal managing Portugal Wildland-urban Industries Wildfires Quantitative, EU and 44,482,550 hypothetical wildlife-urban interfaces Own Analysis national scenario interface: Industries (40-year time horizon) 38 Portugal managing Portugal Wildland-urban Housing and Wildfires Quantitative, EU 2,000,000 hypothetical wildlife-urban interfaces Public buildings Own Analysis scenario interface: Homes (30-year time horizon) 39 Avalanche Switzerland Landslide Recreation Landslides/ Qualitative National varies 2007 mitigation strategies prevention and avalanches response investments 40 Mapping landslide Croatia/ Information Response & Landslides Qualitative EU 974,695 2019 hazards Bosnia and System and Equipment Herzegovina/ cooperation Montenegro mechanism 41 Multifunctional ship Estonia Preventive Fishing Oil spills (Partial) EU and 33,100,000 2013 to tackle marine investments in Quantitative, national pollution vessels and based on the equipment in literature coastal areas 42 Dealing safely with Latvia Cleaning up Water Chemical Quantitative, EU and 29,000,000 2013 hazardous waste hazardous waste Own Analysis national 43 Cleaning up uranium Czech Cleaning up Water Radiological Qualitative EU 23,895,700 2013 site Republic Uranium 44 Security of nuclear France Security of Energy Nuclear Qualitative National 24,000,000,000 On-going plants nuclear power plant 45 Flood early warning Belgium Early Warning Early Warning Flood Quantitative, National 22,763,074 On-going system Flanders Own Analysis Annexes 265 NAME OF CASE TYPE OF FUNDING TOTAL FUNDING CLOSING NBR COUNTRIES SECTOR HAZARD TYPE OF ANALYSIS STUDY  INVESTMENT INSTITUTIONS (EURO) DATE 46 INTERREG project Scotland Nature-based Agriculture & Flood (Partial) EU and 2,387,000 2020 Eddleston Water Solutions forestry Quantitative, National based on the literature 47 Early Warning Germany Early Warning Early Warning Flood Qualitative National 148,000 2010 System in Grimma 48 Sigma plan – Belgium Nature-based Agriculture & Flood (Partial) National 397,000,000 On-going coastal protection of Solutions forestry Quantitative, the Scheldt Estuary based on the literature 49 European Flood Across Early Warning Early Warning Flood Qualitative EU 21,800,000 2003 Awareness System Europe 50 Property Level Italy Property Level Housing and Flood Quantitative, National 22,763,074 2016 Protection Protection Public Buildings Own Analysis 51 Union Civil Albania & Responder Emergency Earthquake Quantitative, EU 6,000,000 & 2019 & Protection Croatia Capacity – response & Own Analysis 3,700,000 2020 Knowledge Network Building equipment in Earthquake 52 Safety from natural France/Spain Information Early Warning Landslides Qualitative EU 4,220,000 2020 risks on the Bielsa- System and Aragnouet and cooperation Espacio Portalet mechanism road links 53 PyrMove Landslide France Information Early Warning Landslides Qualitative EU 1,042,144.82 On-going Prevention System and cooperation mechanism 54 Climate Resilient Albania Preventive Transportation Landslides (Partial) World Bank 13,800,000 2019 Road Assets investments in the Quantitative, resilience of roads based on the literature Annexes 266 NAME OF CASE TYPE OF FUNDING TOTAL FUNDING CLOSING NBR COUNTRIES SECTOR HAZARD TYPE OF ANALYSIS STUDY  INVESTMENT INSTITUTIONS (EURO) DATE 55 SUSEN sustainable Czech Security of Emergency Nuclear Qualitative National 100,219,918 On-going energy project Republic nuclear power response & plant equipment 56 Atlas of Rains Poland Early Warning Early Warning Flood Qualitative National 1,154,517 2020 Intensities (PANDA) 57 fuel management in Portugal Fuel Management Forestry Wildfire Quantitative, EU 2,212,203 On-going Europe for Wildfire Risk Own Analysis Reduction in forests 58 Alerting and Portugal Decision Support Early Warning Wildfire Quantitative, National 19,264,600 On-going Preparedness in Tools for Climate Own Analysis Portugal Change Adaptation and Alerting 59 Alerting and Greece Decision Support Early Warning Wildfire Quantitative, National 8,000,000 On-going Preparedness in Tools for Climate Own Analysis Greece Change Adaptation and Alerting 60 Interreg España- Spain/ Cross-border Emergency Wildfire Qualitative EU and 704,138 2014 Portugal Portugal support, response & National coordination equipment mechanisms and capacity building 61 Landslide Italy Land use planning Housing and Landslide Qualitative National 57,000 2010 management investments Public Buildings 62 ARIEM+ Spain/ Early Warning Early Warning All hazards Qualitative EU 4,193,521 2020 Portugal 63 BASE Project for Portugal Participatory Housing and All hazards (Partial) National 7,555,674.25 2016 Climate Change Methodologies for Public Buildings Quantitative, Adaptation Climate Change based on the Adaptation literature Annexes 267 NAME OF CASE TYPE OF FUNDING TOTAL FUNDING CLOSING NBR COUNTRIES SECTOR HAZARD TYPE OF ANALYSIS STUDY  INVESTMENT INSTITUTIONS (EURO) DATE 64 Forest management Austria Early Warning Early Warning Wildfire Quantitative, Regional 188,168 hypothetical for wildfire Own Analysis scenario prevention (30-year time horizon) 65 Mill Brook Scheme United Nature-based Recreational; Flood Qualitative National 15,181 2016 Kingdom Solutions water 66 Padgate River United Nature-based Recreational; Flood Qualitative National 281,125 2015 Restoration Kingdom Solutions water; Agriculture & forestry 67 Mayes Brook River United Nature-based Recreational; Flood Qualitative National 4,273,100 2012 Restoration Project Kingdom Solutions Agriculture & forestry 68 Slowing the Flow at United Structural Agriculture & Flood Qualitative National 4,500 ,000 2015 Pickering Kingdom Protection forestry; water 69 Green and Grey Germany Nature-based Agriculture & Flood (Partial) National 10,250 (per ha) 2012 solution in Elbe Solutions forestry; water Quantitative, River flood based on the protection literature 70 Sandwich Tidal United Nature-based Agriculture & Flood Qualitative National 24,400,000 2015 Defence Scheme Kingdom Solutions forestry; water 71 Alkborough Flats United Nature-based Agriculture & Flood Qualitative National 12,480,000 2015 Managed Kingdom Solutions forestry; water Realignment 72 FP7 OPERAs in Spain Nature-based Recreation Flood Qualitative EU and local 11,459,749 2017 Barcelona Solutions 73 URBAN GreenUP Across Local multi- Housing and All Hazards Qualitative EU 15,000,000 On-going Europe purpose green Public Buildings; investments recreation 74 Budapest City Park Hungary Local multi- Recreation All Hazards Qualitative national 617,100,00 2017 purpose green investments Annexes 268 © 2021 International Bank for Reconstruction and Development / The World Bank 1818 H Street NW, Washington DC 20433