Abstract

Wetlands provide ∼$47.4 trillion/year worth of ecosystem services globally and support immense biodiversity, yet face widespread drainage and pollution, and large-scale wetlands restoration is urgently needed. Payment for ecosystem service (PES) schemes provide a viable avenue for funding large-scale wetland restoration. However, schemes around the globe differ substantially in their goals, structure, challenges, and effectiveness in supporting large-scale wetland restoration. Here, we suggest wetland-based PES schemes use common asset trusts (CATs) to build investment portfolios of wetlands across landscapes that sustain and enhance overall provision of multiple ecosystem services. CATs can meet the needs of multiple investors, permit bundled payments, and provide flexibility to invest in the restoration of numerous services/values, all using a coordinated, highly collaborative, prioritized, and transparent process. CATs would support financial viability, facilitate efficiency to reduce administrative burdens, and enable credibility and social licence building to restore wetland values and services globally. Wetlands provide ∼$47.4 trillion/year worth of ecosystem services globally and support immense biodiversity, yet face widespread drainage and pollution, and large-scale wetlands restoration is urgently needed. Payment for ecosystem service (PES) schemes provide a viable avenue for funding large-scale wetland restoration. However, schemes around the globe differ substantially in their goals, structure, challenges, and effectiveness in supporting large-scale wetland restoration. Here, we suggest wetland-based PES schemes use common asset trusts (CATs) to build investment portfolios of wetlands across landscapes that sustain and enhance overall provision of multiple ecosystem services. CATs can meet the needs of multiple investors, permit bundled payments, and provide flexibility to invest in the restoration of numerous services/values, all using a coordinated, highly collaborative, prioritized, and transparent process. CATs would support financial viability, facilitate efficiency to reduce administrative burdens, and enable credibility and social licence building to restore wetland values and services globally. IntroductionWetland restoration can contribute significantly to meeting many global, national, and local goals and initiatives, including several United Nations (UN) Sustainable Development Goals (SDGs).1Mitsch W.J. Bernal B. Hernandez M.E. Ecosystem services of wetlands.Int. J. Biodivers. Sci. Ecosyst. Serv. Manag. 2015; 11: 1-4Crossref Scopus (148) Google Scholar,2Seifollahi-Aghmiuni S. Nockrach M. Kalantari Z. The potential of wetlands in achieving the sustainable development goals of the 2030 agenda.Water. 2019; 11: 609Crossref Scopus (31) Google Scholar Using the Ramsar definition, wetlands include any inland, coastal, or marine waterbody, still or flowing, fresh or saline, permanent or temporary, to a depth of 6 m at low tide.3Ramsar Convention SecretariatAn Introduction to the Convention on Wetlands (Previously the Ramsar Convention Manual).5th. Ramsar, Gland, Switzerland2016https://www.ramsar.org/sites/default/files/documents/library/handbook1_5ed_introductiontoconvention_e.pdfGoogle Scholar This includes fens, peat bogs, swamps, marshes, oyster reefs, rivers, lakes and artificial water bodies, mangroves, seagrass meadows, mudflats, and some coral reefs. In many cases, wetlands also include adjacent riparian and coastal zones.3Ramsar Convention SecretariatAn Introduction to the Convention on Wetlands (Previously the Ramsar Convention Manual).5th. Ramsar, Gland, Switzerland2016https://www.ramsar.org/sites/default/files/documents/library/handbook1_5ed_introductiontoconvention_e.pdfGoogle Scholar Wetland ecosystems provide a range of ecosystem services (i.e., the benefits to humans from ecosystems), including water purification, carbon sequestration, food provision, flood regulation, storm surge protection, and ecotourism, and support biodiversity, and cultural and spiritual values.1Mitsch W.J. Bernal B. Hernandez M.E. Ecosystem services of wetlands.Int. J. Biodivers. Sci. Ecosyst. Serv. Manag. 2015; 11: 1-4Crossref Scopus (148) Google Scholar The global value of wetland ecosystem services is estimated at ∼$47.4 trillion/year, with estuarine and palustrine wetlands among the most service-rich ecosystems relative to extent.4de Groot R. Brander L. van der Ploeg S. Costanza R. Bernard F. Braat L. et al.Global estimates of the value of ecosystems and their services in monetary units.Ecosystem Services. 2012; 1: 50-61https://doi.org/10.1016/j.ecoser.2012.07.005Crossref Scopus (1399) Google Scholar,5Davidson N.C. van Dam A.A. Finlayson C.M. McInnes R.J. Worth of wetlands: revised global monetary values of coastal and inland wetland ecosystem services.Mar. Freshw. Res. 2019; 70: 1189-1194https://doi.org/10.1071/MF18391Crossref Scopus (60) Google Scholar The total value of ecosystem services to human wellbeing comprises both market (market price or exchange values) and non-market values. Estimates of the total value are required to truly recognize the contribution the wetlands make to human wellbeing, and to enable us to appropriately determine the ecosystem services most in need of protecting from degradation or loss.Despite the well-established provision of ecosystem services, global wetland extent is still declining.6Gardner R. Finlayson C. Global wetland outlook: state of the world’s wetlands and their services to people.in: Secretariat of the Ramsar Convention. 2018: 88Google Scholar Davidson7Davidson N.C. How much wetland has the world lost? Long-term and recent trends in global wetland area.Mar. Freshw. Res. 2014; 65: 934-941Crossref Scopus (884) Google Scholar estimates that 54%–57%, and possibly as much as 87%, of global wetlands have been lost as a result of land use change for agricultural, urban, and industrial expansion. Large-scale wetland restoration would directly support the UN SDGs by providing a critical buffer against global climate change, improving water quality, increasing infrastructure resilience to floods and storm surge, protecting or enhancing biodiversity, and addressing food supply crises.2Seifollahi-Aghmiuni S. Nockrach M. Kalantari Z. The potential of wetlands in achieving the sustainable development goals of the 2030 agenda.Water. 2019; 11: 609Crossref Scopus (31) Google Scholar,8United Nations General Assembly (2015). Transforming Our World: The 2030 Agenda for Sustainable Development. Div. Sustain. Dev. Goals New York, NY, USA.Google ScholarThe protection and restoration of wetlands is being facilitated by many policy instruments, including outreach and education (e.g., awareness campaigns), international conventions (e.g., the Ramsar Convention and Convention on Biological Diversity), governance instruments (e.g., national policies and programs), regulatory approaches (e.g., environmental standards), covenants and easements, environmental taxes, restoration subsidies, and market-based approaches (e.g., environmental markets and eco-labeling).9Zhao Q. Bai J. Huang L. Gu B. Lu Q. Gao Z. A review of methodologies and success indicators for coastal wetland restoration.Ecol. Indic. 2016; 60: 442-452Crossref Scopus (124) Google Scholar, 10Gardner R.C. Rehabilitating nature: a comparative review of legal mechanisms that encourage wetland restoration efforts.Cath. UL Rev. 2002; 52: 573Google Scholar, 11Greenhalgh S. Selman M. Daigneault A. Kaighin C. Sinclair R. Policy Instruments for Ecosystem Services.Landcare Research science series. 42. Manaaki Whenua Press, Lincoln, New Zealand2014http://www.mwpress.co.nz/__data/assets/pdf_file/0019/74521/Policy_Instruments_for_Ecosystem_Services.pdfGoogle Scholar Among these approaches, public/private funding schemes that include payments for ecosystem services (PES), provide a potential way of raising the financial capital needed to deliver large-scale wetland restoration.12Salzman J. Bennett G. Carroll N. Goldstein A. Jenkins M. Payments for ecosystem services: past, present and future.Tex. A&M L. Rev. 2018; 6: 199Crossref Google Scholar, 13Benson C.E. Carberry B. Langen T.A. Public–private partnership wetland restoration programs benefit Species of Greatest Conservation Need and other wetland-associated wildlife.Wetl. Ecol. Manag. 2018; 26: 195-211Crossref Scopus (18) Google Scholar, 14Farley J. Costanza R. Payments for ecosystem services: from local to global.Ecol. Econ. 2010; 69: 2060-2068Crossref Scopus (443) Google Scholar PES schemes may be regulated (e.g., government-led programs to achieve legislated environmental limits) or voluntary (e.g., non-government organization-led programs to achieving non-binding goals), and seek to provide payment for the additional or sustained existing ecosystem services that restored ecosystems provide, often to offset impacts elsewhere.PES schemes have primarily arisen from trading carbon for climate change mitigation or trading nutrients for water quality improvement, mitigation banking, or sale of habitat protection/restoration “stamps.”12Salzman J. Bennett G. Carroll N. Goldstein A. Jenkins M. Payments for ecosystem services: past, present and future.Tex. A&M L. Rev. 2018; 6: 199Crossref Google Scholar,15Salzman J. Bennett G. Carroll N. Goldstein A. Jenkins M. The global status and trends of payments for ecosystem services.Nat. Sustain. 2018; 1: 136-144Crossref Scopus (257) Google Scholar New scheme mechanisms (e.g., crowd funding), new support technologies (e.g., block-chain mechanisms and remote sensing), and new opportunities (e.g., blue carbon, property protection,16Ivčević A. Statzu V. Satta A. Bertoldo R. The future protection from the climate change-related hazards and the willingness to pay for home insurance in the coastal wetlands of West Sardinia, Italy.Int. J. Disaster Risk Reduct. 2021; 52: 101956Crossref Scopus (9) Google Scholar and bioenergy) are on the horizon and present options for schemes that endeavor to fund future wetland restoration within the UN “decade of ecosystem restoration (2021–2030).”17Waltham N.J. Elliott M. Lee S.Y. Lovelock C. Duarte C.M. Buelow C. Simenstad C. Nagelkerken I. Claassens L. Wen C.K.-C. et al.UN decade on ecosystem restoration 2021–2030—what chance for success in restoring coastal ecosystems?.Front. Mar. Sci. 2020; 7: 71Crossref Scopus (94) Google ScholarWhile promising, PES schemes do not often deliver the expected benefits from wetland restoration.15Salzman J. Bennett G. Carroll N. Goldstein A. Jenkins M. The global status and trends of payments for ecosystem services.Nat. Sustain. 2018; 1: 136-144Crossref Scopus (257) Google Scholar,18Bullock J.M. Aronson J. Newton A.C. Pywell R.F. Rey-Benayas J.M. Restoration of ecosystem services and biodiversity: conflicts and opportunities.Trends Ecol. Evol. 2011; 26: 541-549Abstract Full Text Full Text PDF PubMed Scopus (622) Google Scholar,19Hrabanski M. The biodiversity offsets as market-based instruments in global governance: origins, success and controversies.Ecosyst. Serv. 2015; 15: 143-151Crossref Scopus (32) Google Scholar These failures can arise where wetland restoration is a secondary objective or a tool supporting a primary objective (e.g., reducing carbon or improving water quality) and where the schemes face their own difficulties.20Pan X. Xu L. Yang Z. Yu B. Payments for ecosystem services in China: policy, practice, and progress.J. Clean. Prod. 2017; 158: 200-208Crossref Scopus (63) Google Scholar For example, a review of the effectiveness of four North American water quality trading schemes (in which, wetlands are one of many options for improving water quality) identified many challenges, including inadequacy in monitoring, low participant motivation,21Stephenson K. Shabman L. Rhetoric and reality of water quality trading and the potential for market-like reform.JAWRA J. Am. Water Resour. Assoc. 2011; 47: 15-28Crossref Scopus (46) Google Scholar difficulties in achieving and enforcing compliance, ill-defined property rights, and high administrative and transaction costs.22Cherry S. Britney E.M. Siegel L.S. Muscari M.J. Strauch R.L. Mcneil M.S. Wetlands and Water Quality Trading: Review of Current Science and Economic Practices with Selected Case Studies. U.S. Environmental Protection Agency, 2007Google Scholar Similar challenges were also identified by a review of PES schemes across China.20Pan X. Xu L. Yang Z. Yu B. Payments for ecosystem services in China: policy, practice, and progress.J. Clean. Prod. 2017; 158: 200-208Crossref Scopus (63) Google Scholar It is likely that PES-based restoration schemes in other locations will face similar and scheme-specific challenges. If wetland restoration is to deliver a substantial contribution toward local ambitions and ultimately global SDGs,1Mitsch W.J. Bernal B. Hernandez M.E. Ecosystem services of wetlands.Int. J. Biodivers. Sci. Ecosyst. Serv. Manag. 2015; 11: 1-4Crossref Scopus (148) Google Scholar,2Seifollahi-Aghmiuni S. Nockrach M. Kalantari Z. The potential of wetlands in achieving the sustainable development goals of the 2030 agenda.Water. 2019; 11: 609Crossref Scopus (31) Google Scholar,23Jaramillo F. Desormeaux A. Hedlund J. Jawitz J. Clerici N. Piemontese L. Rodríguez-Rodriguez J. Anaya J. Blanco-Libreros J. Borja S. et al.Priorities and interactions of sustainable development goals (SDGs) with focus on wetlands.Water. 2019; 11: 619Crossref Scopus (47) Google Scholar it is imperative that financial incentive mechanisms, such as PES, are well designed to maximize success in achieving a chief objective of large-scale wetland restoration. This is in contrast to existing schemes that typically primarily focus on ecosystem service provisioning and have wetland restoration as a secondary objective.Notable types of PES schemes providing incentives for wetland restoration include carbon markets; water quality trading; habitat stamps and wild harvesting; eco-labeling; crowd funding; and water funds. While each scheme has advantages, disadvantages, and room for improvement (Table S1), three cross-cutting challenges exist: (1) demonstrating sustained financial viability; (2) establishing credibility with effective verification and accounting; and (3) balancing trade-offs to achieve general acceptability, and to establish and maintain social license to operate (Table S1).24Bellver-Domingo A. Hernández-Sancho F. Molinos-Senante M. A review of Payment for Ecosystem Services for the economic internalization of environmental externalities: a water perspective.Geoforum. 2016; 70: 115-118Crossref Scopus (38) Google Scholar, 25Schomers S. Matzdorf B. Payments for ecosystem services: a review and comparison of developing and industrialized countries.Ecosyst. Serv. 2013; 6: 16-30Crossref Scopus (324) Google Scholar, 26Bremer L.L. Brauman K.A. Nelson S. Prado K.M. Wilburn E. Fiorini A.C.O. Relational values in evaluations of upstream social outcomes of watershed Payment for Ecosystem Services: a review.Curr. Opin. Environ. Sustain. 2018; 35: 116-123Crossref Scopus (38) Google ScholarHere, we suggest that PES schemes dedicated to, and specifically designed for, wetland restoration will be more effective than single-service-focused schemes and non-financed instruments in not only increasing the rate and extent of wetland restoration, but also increasing the flow of multiple ecosystem services. Taking on board the challenges faced by many PES schemes (Table S1), we propose using a common asset trust (CAT) approach as the platform for a PES scheme designed to enhance wetland restoration efforts. Below we analyze the three main challenges for PES schemes and how these challenges may be overcome. We then outline how a CAT could solve many of these challenges to enhance wetland restoration, and identify the roles and responsibilities of key stakeholders.Common challenges across schemesThe three key challenges across schemes are financial viability, credibility, and maintaining a social license to operate.Financial viabilityFinancial viability is critical to the success of any PES scheme. Funding is often insufficient, intermittent, or highly variable, to confidently cover the costs of wetland restoration (including the opportunity cost of land use change), associated assessments, monitoring and administration, and on-going maintenance after construction.27Stephenson K. Shabman L. Nutrient assimilation services for water quality credit trading programs: a comparative analysis with nonpoint source credits.Coast. Manag. 2017; 45: 24-43Crossref Scopus (17) Google Scholar, 28Wylie L. Sutton-Grier A.E. Moore A. Keys to successful blue carbon projects: lessons learned from global case studies.Mar. Policy. 2016; 65: 76-84Crossref Scopus (149) Google Scholar, 29Raffini, E., and Robertson, M. (2005). Water quality trading: what can we learn from 10 years of wetland mitigation banking? U.S. Environmental Protection Agency Papers. 276. http://digitalcommons.unl.edu/usepapapers/276Google Scholar Financial viability rests on sufficient, stable, and sustained payments for projects and acceptable rates of return for project investors (including public financers seeking societal benefits). Highly variable provision of services may lower investor confidence in returns, deter investors, and erode financial viability. In addition, sometimes measuring/estimating service flows requires complex and expensive assessments to boost confidence.14Farley J. Costanza R. Payments for ecosystem services: from local to global.Ecol. Econ. 2010; 69: 2060-2068Crossref Scopus (443) Google Scholar,30Hou Y. Burkhard B. Müller F. Uncertainties in landscape analysis and ecosystem service assessment.J. Environ. Manage. 2013; 127: S117-S131Crossref PubMed Scopus (196) Google Scholar,31Friess D.A. Phelps J. Garmendia E. Gómez-Baggethun E. Payments for Ecosystem Services (PES) in the face of external biophysical stressors.Glob. Environ. Chang. 2015; 30: 31-42Crossref Scopus (37) Google Scholar Often, schemes trade a single-service commodity (e.g., credits for carbon sequestration or nitrogen removal), rather than rewarding the provision of multiple services, where restored wetlands are designed and positioned to optimize cost-effective delivery of that service (Tables S1 and S2).18Bullock J.M. Aronson J. Newton A.C. Pywell R.F. Rey-Benayas J.M. Restoration of ecosystem services and biodiversity: conflicts and opportunities.Trends Ecol. Evol. 2011; 26: 541-549Abstract Full Text Full Text PDF PubMed Scopus (622) Google Scholar,32Matzek V. Wilson K.A. Kragt M. Mainstreaming of ecosystem services as a rationale for ecological restoration in Australia.Ecosyst. Serv. 2019; 35: 79-86Crossref Scopus (7) Google ScholarAs wetlands can deliver multiple ecosystem services,1Mitsch W.J. Bernal B. Hernandez M.E. Ecosystem services of wetlands.Int. J. Biodivers. Sci. Ecosyst. Serv. Manag. 2015; 11: 1-4Crossref Scopus (148) Google Scholar schemes that focus on a single service (i.e., the primary benefit) do not value and reward the provision of co-benefits (i.e., the secondary benefits).33Heberling M.T. García J.H. Thurston H.W. Does encouraging the use of wetlands in water quality trading programs make economic sense?.Ecol. Econ. 2010; 69: 1988-1994Crossref Scopus (19) Google Scholar Carbon markets, for example, offer low and highly variable trading prices, with compliance markets having greater demand (driven by legislated limits) and offer better prices than voluntary markets (Figures S1–S3).34Bayraktarov E. Saunders M.I. Abdullah S. Mills M. Beher J. Possingham H.P. Mumby P.J. Lovelock C.E. The cost and feasibility of marine coastal restoration.Ecol. Appl. 2016; 26: 1055-1074Crossref PubMed Google Scholar, 35Ullman R. Bilbao-Bastida V. Grimsditch G. Including Blue Carbon in climate market mechanisms.Ocean Coast. Manag. 2013; 83: 15-18Crossref Scopus (76) Google Scholar, 36Vanderklift M.A. Marcos-Martinez R. Butler J.R.A. Coleman M. Lawrence A. Prislan H. Steven A.D.L. Thomas S. Constraints and opportunities for market-based finance for the restoration and protection of blue carbon ecosystems.Mar. Policy. 2019; 107: 103429Crossref Scopus (54) Google Scholar Wetland-based carbon sequestration projects are often only viable and competitive against other offset options in low-cost developing countries, e.g., the Sundarbans Mangrove Restoration in India (Note S1).28Wylie L. Sutton-Grier A.E. Moore A. Keys to successful blue carbon projects: lessons learned from global case studies.Mar. Policy. 2016; 65: 76-84Crossref Scopus (149) Google Scholar,36Vanderklift M.A. Marcos-Martinez R. Butler J.R.A. Coleman M. Lawrence A. Prislan H. Steven A.D.L. Thomas S. Constraints and opportunities for market-based finance for the restoration and protection of blue carbon ecosystems.Mar. Policy. 2019; 107: 103429Crossref Scopus (54) Google Scholar,37Stewart-Sinclair P.J. Purandare J. Bayraktarov E. Waltham N.J. Reeves S. Statton J. Sinclair E.A. Brown B.M. Shribman Z.I. Lovelock C.E. Blue restoration—building confidence and overcoming barriers.Front. Mar. Sci. 2020; Crossref Scopus (23) Google Scholar Even then, Vietnam's Markets and Mangroves project (Note S2) within the Mekong Delta initially sought funding by selling carbon credits, but were deterred by the administrative cost burden, and instead were funded by an organic eco-label.38McEwin A. McNally R. Organic Shrimp Certification and Carbon Financing: An Assessment for the Mangroves and Markets Project in Ca Mau Province, Vietnam. REAP Proj. GiZ, SNV, 2014: 81Google Scholar Trading prices are often insufficient to deliver positive returns from wetland restoration in countries with developed economies.36Vanderklift M.A. Marcos-Martinez R. Butler J.R.A. Coleman M. Lawrence A. Prislan H. Steven A.D.L. Thomas S. Constraints and opportunities for market-based finance for the restoration and protection of blue carbon ecosystems.Mar. Policy. 2019; 107: 103429Crossref Scopus (54) Google Scholar,37Stewart-Sinclair P.J. Purandare J. Bayraktarov E. Waltham N.J. Reeves S. Statton J. Sinclair E.A. Brown B.M. Shribman Z.I. Lovelock C.E. Blue restoration—building confidence and overcoming barriers.Front. Mar. Sci. 2020; Crossref Scopus (23) Google ScholarQuantification of ecosystem service provision in market-based schemes can often constitute a substantial cost that affects financial viability.31Friess D.A. Phelps J. Garmendia E. Gómez-Baggethun E. Payments for Ecosystem Services (PES) in the face of external biophysical stressors.Glob. Environ. Chang. 2015; 30: 31-42Crossref Scopus (37) Google Scholar,36Vanderklift M.A. Marcos-Martinez R. Butler J.R.A. Coleman M. Lawrence A. Prislan H. Steven A.D.L. Thomas S. Constraints and opportunities for market-based finance for the restoration and protection of blue carbon ecosystems.Mar. Policy. 2019; 107: 103429Crossref Scopus (54) Google Scholar,39Banerjee S. Secchi S. Fargione J. Polasky S. Kraft S. How to sell ecosystem services: a guide for designing new markets.Front. Ecol. Environ. 2013; 11: 297-304Crossref Scopus (48) Google Scholar For example, Günther et al.40Günther A. Böther S. Couwenberg J. Hüttel S. Jurasinski G. Profitability of direct greenhouse gas measurements in carbon credit schemes of peatland rewetting.Ecol. Econ. 2018; 146: 766-771Crossref Scopus (12) Google Scholar estimated in 2018 that assessing carbon for a 52 ha re-wetted fen in north-eastern Germany cost between €150,000 and €300,000 over 2–3 years. Several mechanisms, including standard setting, applying trading ratios and using direct fund investment, have been trialed to reduce the compliance costs of participating in wetland restoration projects. Germany's MoorFutures regional carbon trading scheme has increased the financial viability of peat-wetland restoration by reducing compliance costs through the setting of local assessment methods and standards (Note S3).41Joosten H. Brust K. Couwenberg J. Gerner A. Holsten B. Permien T. et al.MoorFutures®. Integr. von weiteren Ökosystemdienstleistungen einschließlich Biodiversität Kohlenstoffzertifikate–Standard, Methodol. und Übertragbarkeit in andere Regionen. Bundesamt für Naturschutz (BfN), Bonn, Germany2013https://www.bfn.de/fileadmin/BfN/service/Dokumente/skripten/Skript350.pdfGoogle Scholar,42Bonn A. Reed M.S. Evans C.D. Joosten H. Bain C. Farmer J. Emmer I. Couwenberg J. Moxey A. Artz R. et al.Investing in nature: developing ecosystem service markets for peatland restoration.Ecosyst. Serv. 2014; 9: 54-65Crossref Scopus (87) Google ScholarNorth American point-nonpoint source water quality trading markets (e.g., Colorado's Cherry Creek and Ontario's South Nation River schemes; Notes S4 and S5, respectively),22Cherry S. Britney E.M. Siegel L.S. Muscari M.J. Strauch R.L. Mcneil M.S. Wetlands and Water Quality Trading: Review of Current Science and Economic Practices with Selected Case Studies. U.S. Environmental Protection Agency, 2007Google Scholar,43Tabaichount B. Wood S. Kermagoret C. Kolinjivadi V. Bissonnette J.-F. Mendez A. Dupras J. Water quality trading schemes as a form of state intervention: two case studies of state-market hybridization from Canada and New Zealand.Ecosyst. Serv. 2019; 36https://doi.org/10.1016/j.ecoser.2019.01.002Crossref Scopus (13) Google Scholar and wetland biodiversity mitigation markets (e.g., Chicago's wetland mitigation market; Note S6),44Robertson M. Emerging ecosystem service markets: trends in a decade of entrepreneurial wetland banking.Front. Ecol. Environ. 2006; 4: 297-302Crossref Scopus (54) Google Scholar,45Robertson M. Hayden N. Evaluation of a market in wetland credits: entrepreneurial wetland banking in Chicago.Conserv. Biol. 2008; 22: 636-646Crossref PubMed Scopus (55) Google Scholar often apply trading ratios, which tend to be conservative, to account for uncertainties in service delivery. Trading ratios are a policy mechanism that require polluters or property developers to offset more than the estimated discharge or loss. For example, Ontario's South Nation River phosphorus trading scheme requires polluters to offset four times the amount of phosphorus discharged (Note S5). Trading ratios could allow for less onerous assessment methods, improving the cost effectiveness of restoring larger wetlands.22Cherry S. Britney E.M. Siegel L.S. Muscari M.J. Strauch R.L. Mcneil M.S. Wetlands and Water Quality Trading: Review of Current Science and Economic Practices with Selected Case Studies. U.S. Environmental Protection Agency, 2007Google Scholar,43Tabaichount B. Wood S. Kermagoret C. Kolinjivadi V. Bissonnette J.-F. Mendez A. Dupras J. Water quality trading schemes as a form of state intervention: two case studies of state-market hybridization from Canada and New Zealand.Ecosyst. Serv. 2019; 36https://doi.org/10.1016/j.ecoser.2019.01.002Crossref Scopus (13) Google Scholar However, very high ratios may render wetland projects uncompetitive against other offset options. Using trading ratios with complementary assessment models or simple estimates of efficacy, can increase certainty, ease monitoring costs, and thereby increase competitiveness compared with other offsets.46McKenney B.A. Kiesecker J.M. Policy development for biodiversity offsets: a review of offset frameworks.Environ. Manage. 2010; 45: 165-176Crossref PubMed Scopus (309) Google Scholar, 47King D.M. Price E.W. Developing Defensible Wetland Mitigation Ratios: A Companion to “The Five-Step Wetland Mitigation Ratio Calculator”. University of Maryland, 2004https://nctc.fws.gov/courses/csp/csp3112/resources/Mitigation/WetlandMitigationRatios.pdfGoogle Scholar, 48Needham K. de Vries F.P. Armsworth P.R. Hanley N. Designing markets for biodiversity offsets: lessons from tradable pollution permits.J. Appl. 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Highlights

  • Wetland restoration can contribute significantly to meeting many global, national, and local goals and initiatives, including several United Nations (UN) Sustainable Development Goals (SDGs).[1,2] Using the Ramsar definition, wetlands include any inland, coastal, or marine waterbody, still or flowing, fresh or saline, permanent or temporary, to a depth of 6 m at low tide.[3]

  • Wetland ecosystems provide a range of ecosystem services, including water purification, carbon sequestration, food provision, flood regulation, storm surge protection, and ecotourism, and support biodiversity, and cultural and spiritual values.[1]

  • We suggest that Payment for ecosystem service (PES) schemes dedicated to, and designed for, wetland restoration will be more effective than single-service-focused schemes and non-financed instruments in increasing the rate and extent of wetland restoration, and increasing the flow of multiple ecosystem services

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Summary

SUMMARY

Wetlands provide $47.4 trillion/year worth of ecosystem services globally and support immense biodiversity, yet face widespread drainage and pollution, and large-scale wetlands restoration is urgently needed. We suggest wetland-based PES schemes use common asset trusts (CATs) to build investment portfolios of wetlands across landscapes that sustain and enhance overall provision of multiple ecosystem services. CATs can meet the needs of multiple investors, permit bundled payments, and provide flexibility to invest in the restoration of numerous services/values, all using a coordinated, highly collaborative, prioritized, and transparent process. CATs would support financial viability, facilitate efficiency to reduce administrative burdens, and enable credibility and social licence building to restore wetland values and services globally

INTRODUCTION
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