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Restoring freshwater ecosystems is vital to limiting global warming, adapting to climate change and reversing biodiversity loss. Healthy rivers, lakes and wetlands — including salt marshes, mangroves and peatlands — are fundamental to planetary health and human well-being.

Restoration is critical for freshwater systems

Restoration offers a powerful pathway to conserve freshwater ecosystems, secure water resources and sustain ecosystem services for current and future generations, while addressing the interconnected crises of climate change and biodiversity loss.

Although restored freshwater ecosystems often fail to reach the same level of ecosystem functioning and structure as undisturbed systems — making conservation the top priority — restoration remains essential for reversing environmental degradation, revitalizing nature and giving humanity a chance to build resilience against growing climate impacts.

Well-designed and appropriately implemented freshwater restoration can support climate mitigation and biodiversity conservation by restoring habitat and ecological connectivity for freshwater species. It can also provide life-sustaining ecosystem services to communities near and far, including protecting against intensifying climate impacts through flood protection and erosion control, and mitigating severe droughts by providing water sources during dry periods. Beyond environmental gains, well-designed and implemented habitat restoration efforts can also help reduce poverty, provide food security and support local economies through job creation and broader socioeconomic gains, including improved education, skills development and capacity-building.

The 2020-2030 U.N. Decade on Ecosystem Restoration is a collective effort to prevent, halt and reverse the degradation of ecosystems on every continent and throughout the world’s ocean. Freshwater ecosystems are among the most severely impacted, with one-third of natural freshwater systems having disappeared since the 1970s. As such, they must be a central focus of this global restoration effort.
 

Scaling restoration across freshwater ecosystems

Restoration will look different depending on the context — whether it is rewetting drained wetlands by reconnecting them with their original waterways, reducing impervious surfaces to enhance groundwater recharge, or removing dams to restore free-flowing rivers. Successful restoration will require an integrated approach that identifies and addresses the land-based drivers of degradation, including pollution from industrial activities, agricultural runoff, urban land-use and land cover changes.

Global data is still far too limited to regularly assess restoration progress for several key freshwater ecosystems — including wetlands (with the exception of mangroves and salt marshes), peatlands, rivers and lakes — underscoring the urgent need for improved global monitoring. For some of the ecosystem types where we do have data, we are far off track from meeting global climate and biodiversity targets. For example, mangrove restoration must accelerate more than tenfold, while an additional 15 million hectares (Mha) of peatlands must be restored by 2030. Although some gains have been observed in salt marsh restoration, there is insufficient data to determine whether these are enough to meet climate and biodiversity goals.

These are measures of gross gains in ecosystem extent. However, measures of ecosystem integrity are also essential for understanding the extent to which freshwater restoration efforts result in healthy, resilient and self-sustaining ecosystems. While global efforts to monitor ecosystem integrity are beginning to emerge, there is still no dedicated dataset that tracks this vital measure specifically for freshwater ecosystems.

To successfully scale and strengthen global restoration efforts, we must ensure that our underlying economic and political systems actively support and sustain meaningful, long-term impact. Given that many freshwater ecosystems and river basins span national borders — with approximately 60% of the world’s freshwater flows associated with transboundary rivers, lakes and aquifers — cooperation among countries is crucial for success.

Restoration must also be locally led and carried forward in partnership with Indigenous Peoples and Afro-descendant Peoples, who have long stewarded these ecosystems. Engaging their knowledge systems in respectful, ethical and reciprocal ways is essential to ensure that scientific and community expertise inform restoration together.

Tracking progress on global outcomes

7561: Wetland restoration, as measured by total gross gains in wetland extent

Status: Insufficient Data
Target Methodology:

1.5°C-compatible targets for restoring wetlands are not available. Similarly, there is no scientific consensus on what constitutes a sufficiently ambitious target for freshwater biodiversity conservation, and the literature generally lacks quantitative and time-bound targets for this indicator. Accordingly, we can only indicate the direction of change required — that wetland restoration must increase — as informed by Roe et al. 2021 and Goyette et al. 2021.

Wetlands occupy only 4-6% of the Earth’s land area but store an estimated 20-25% of the world’s soil carbon. These ecosystems support rich and unique biodiversity and provide essential ecosystem services to people, including water purification and flood water storage. Despite their critical importance, the world has lost around 21% of wetlands over the past three centuries.

Fortunately, restoration of drained or degraded wetlands has emerged as a priority for key global environmental initiatives. Restoration can take several forms. Rewetting involves plugging drainage ditches or reestablishing the hydrological connectivity of wetlands. This approach is most effective when combined with planting native wetland species while removing nonnative species. Fencing is yet another approach whereby livestock is excluded to allow for the regeneration of native vegetation — vital for maintaining wetlands’ carbon sequestration and storage capacity.

Rather than focusing solely on the most degraded part of a waterbody, successful restoration efforts should be designed at the watershed scale. They should consider terrestrial-freshwater linkages and clearly identify and address the sources of freshwater degradation and loss, such as unsustainable land-use practices, agricultural runoff, pollution or extensive impervious surfaces within the watershed. Planning should also focus on geographically isolated wetlands, which are often absent from management decisions.

While wetland restoration efforts can benefit biodiversity and ecosystem services, outcomes are highly variable. A study of over 600 wetland sites worldwide found that even after 100 years, biological function remained, on average, 26% lower than in undisturbed wetlands. To enhance the success of wetland restoration projects, the Ramsar Convention sets key principles, emphasizing catchment-level planning, strengthening upland-wetland linkages, engaging local and Indigenous communities and ensuring long-term stewardship through ongoing management and monitoring.

The urgent need to restore degraded wetlands is widely recognized, with several international initiatives working to accelerate action. While explicit science-based targets aligned with key climate and biodiversity goals are not available, the Ramsar Convention notes that at least 123 million hectares (Mha) of wetlands must be restored to achieve the Kunming-Montreal Global Biodiversity Framework target of restoring at least 30% of degraded ecosystems. The Freshwater Challenge — a voluntary, country-led partnership — has an even more ambitious target, aiming to restore 350 Mha of wetlands by 2030.

However, tracking progress toward these goals is difficult due to inconsistent global data. Wetlands International assessed 30 restoration projects across 17 countries, covering over 200,000 hectares (ha) restored between 2000 and 2022 — representing only a subset of global efforts. Comprehensive global data on restoration activities over time remains unavailable. The U.N. Environment Programme is currently compiling data on the global extent of inland vegetated wetlands to help monitor changes in wetland extent and guide future restoration strategies.

7550: Peatland restoration, as measured by the total gross area of degraded peatlands that have been rewetted

Status: Insufficient Data
Historical Data Methodology and Challenges:

Peatland restoration targets were adapted from Humpenöder et al. 2020 and Roe et al. 2021, who assume that 0 Mha of peatlands globally were rewetted as of 2015. Rather than suggesting that peatland restoration is not occurring — there is evidence of rewetting, for example, in Indonesia, Norway and Russia — this assumption speaks to the lack of global data on peatland restoration.

Reestablishing peatland hydrology through rewetting represents just one form of peatland restoration, and this intervention, alone, does not guarantee the full recovery of these ecosystems’ predrainage species composition and diversity, or their ecological structures and functions. Additional indicators — for example, those focusing on vegetation species or other land cover characteristics — are needed to assess biodiversity outcomes.

Target Methodology:

Peatland restoration targets are additional to any restoration that occurred prior to 2020, and these targets are cumulative from 2020 to 2050.

  • Targets to limit warming to 1.5°C: Roe et al. 2021 define the bottom-up, cost-effective mitigation potential for avoided GHG emissions from the restoration of degraded peatlands (0.59 GtCO2e/yr from 2020 to 2050) as the difference in the global area of rewetted peatlands between two SSP2-RCP2.6 scenarios modeled by Humpenöder et al. 2020, using MAgPIE, in 2035. The first scenario assumes land-based climate policies that include peatland protection and restoration, while the second assumes land-based climate policies that include only peatland protection. The resulting area is roughly 16 Mha of degraded peatlands restored by 2035.

    For our 1.5°C-aligned targets, we generally followed the ramp-up assumptions in the scenario modeled by Humpenöder et al. 2020, that includes peatland protection and restoration policies, which entail restoring approximately 15 Mha by 2030 and 20 Mha by 2050. Note that our ramp-up assumptions involve restoring 16 Mha by 2035, which ensures alignment with the sector’s total contribution to 1.5°C pathways (13.8 GtCO2e/yr), as estimated by Roe et al. 2021. We set a second, 1.5°C-aligned target — more ambitious, than Roe et al. 2021 — because some studies argue that restoring nearly all degraded peatlands by around mid-century will be required to limit warming to 1.5°C or below, as emissions from drained peatlands may otherwise consume a large share of the global carbon budget associated with this temperature limit. However, as the IPCC 2022 notes, restoring all degraded peatlands may not be possible (e.g., those upon which cities have been constructed, that are subject to saltwater intrusion, that have experienced significant subsidence or that have already been converted into plantation forests). While it remains to be determined with certainty what percentage can be feasibly rehabilitated, particularly at costs of up to $100 per ton of carbon dioxide, several papers find that restoring roughly 50% of degraded peatlands is needed to help deliver AFOLU’s contribution to limiting global temperature rise to 1.5 degrees C (e.g., Searchinger et al. 2019; Roe et al. 2019). We followed these studies and set a 1.5 degrees C-aligned target, more ambitious than Roe et al. 2021, for 2050. The lower bound of this range involves restoring 20 Mha, as estimated by Humpenöder et al. 2020, while the upper bound of this range entails restoring roughly half of degraded peatlands, which the UN Environment Programme (UNEP) recently estimated at 57 Mha globally.
  • Targets to minimize biodiversity loss: Similarly, to minimize biodiversity loss, we set targets that call for rewetting all degraded peatlands, currently estimated at 46 Mha by Humpenöder et al. 2020 and 57 Mha by UNEP 2022.
Progress Assessment Methodology:

Outcome indicators in this system experience high interannual variability in historical data due to both anthropogenic and natural causes. Accordingly, 10 years instead of 5 years should be used to calculate the linear trendline where possible. Global data for peatland restoration, however, is insufficient to assess progress.

Peatlands are a type of freshwater wetland ecosystem characterized by waterlogged organic soils composed of dead and decaying plant material. Covering just 3.8% of the planet’s land, peatlands are global hotspots for carbon sequestration and long-term storage. They also hold 10% of global freshwater resources, help maintain water quality and support endemic and endangered species, including orangutans, bonobos and western lowland gorillas.

Despite their critical importance, around 12% of the world’s peatlands are degraded. Peatland degradation, excluding fires, contributes to 4% of total global anthropogenic emissions. Even if degradation ceased today, emissions from these areas could persist at roughly 1.9 gigatons of carbon dioxide equivalent (Gt CO2e) per year for decades or longer.

The success of peatland restoration, however, depends on the type of degradation these ecosystems experienced (e.g., drainage, burning or cutting). Rewetting peatlands drained by agriculture, for example, can significantly reduce or even halt carbon losses, as well as enable carbon sequestration. While restoring these ecosystems’ water tables can also increase methane emissions initially, rapid rewetting is critical to avoid future greenhouse gas emissions.

For some degraded peatlands, rewetting can help reduce the potential for fires, recover habitat for wetland species and reestablish ecological functions and services. But for others, such efforts can lead to entirely new peatland ecosystems that bear little resemblance to their near-natural counterparts, even several decades after their water tables were restored. Such disparate results indicate gaps in our collective understanding of the factors that determine successful peatland restoration for biodiversity, as well as the need for additional interventions like removing encroaching trees and shrubs or reintroducing peatland vegetation.

Nonetheless, rewetting 15 million hectares (Mha) of peatland — more than a quarter of all degraded peatlands worldwide — by 2030, 16 Mha by 2035 and 20 Mha to 29 Mha by 2050 can help keep the Paris Agreement limit within reach. Minimizing biodiversity losses would call for even greater ambition and action — rewetting 46-57 Mha hectares of degraded peatlands. Although data is insufficient to assess progress toward these targets, available evidence suggests that current efforts to restore peatlands are likely not at the pace and scale required.

7551: Mangrove restoration, as measured by gross direct gains in mangrove extent

Status: Well Off Track
Historical Data Methodology and Challenges:

Murray et al. 2022 estimate gross area of mangrove gain from 1999 to 2019, defining gain as mangrove establishment in areas where mangroves were not present in 1999. They also estimate that the vast majority of mangrove gain from 1999 to 2019 was due to natural, broad-scale coastal processes, with only 8% (approximately 15,000 hectares) likely attributable to direct human interventions, such as mangrove planting and other restoration activities, including those that reestablish tidal regimes. We therefore used this proportion of mangrove gains (i.e., “direct” gains attributable to human interventions) as a proxy for mangrove restoration.

However, there are limitations to using these “direct” mangrove gains as a proxy for mangrove restoration. As with forests, mangroves grow gradually, and therefore mangrove gain is more challenging to monitor on shorter time scales, as gain may not be detected until mangrove trees reach a certain level of maturity. Therefore, recently established mangroves may not be included in these estimates. Moreover, the establishment of mangrove trees does not always indicate the recovery of these ecosystems’ species composition and diversity, or their ecological structures and functions. And, in some cases, the addition of mangrove trees can have negative consequences (e.g., the loss of other tidal wetland ecosystems like salt marshes or seagrass) or short-lived gains if tree planting is not implemented appropriately. Therefore, this proxy may include mangrove gain that would not be considered mangrove restoration. A detailed assessment of the accuracy of this data can be found in Murray et al. 2022.

A final limitation of relying on gross gains in ecosystem extent to approximate restoration is that they only measure changes in land use — for example, from abandoned oil palm plantations or aquaculture ponds to mangrove forests. The addition of mangrove trees within existing, degraded mangroves represents another form of restoration, but it is not included in the Murray et al. 2022 data.

Progress Assessment Methodology:

Outcome indicators in this system experience high interannual variability in historical data due to both anthropogenic and natural causes. Accordingly, 10 years instead of 5 years should be used to calculate the linear trendline where possible. Following Boehm et al. 2021 and due to data limitations, however, the average annual rate of change across the most recently available time period (1999-2019) was used to estimate the historical rate of change, rather than a linear trendline.

Mangroves are within the intertidal zone, the area where the ocean meets the land between high and low tides. They primarily thrive in saline water, although some freshwater mangroves have recently been discovered in the Amazon delta. Mangrove forests are among the world’s most carbon-dense ecosystems, storing at least twice as much carbon per hectare as boreal, temperate and tropical forests. They also provide nursery grounds for fisheries and habitats for many endemic and endangered species.

Restoring degraded mangrove forests not only enhances their ability to sequester and store carbon, it may also reduce greenhouse gas emissions that would otherwise continue for decades following certain disturbances, such as drainage for aquaculture ponds. If implemented following ecological restoration principles, these efforts can also help reverse biodiversity losses by recovering species’ habitats, as well as reestablishing mangroves’ ecological functions and services. Long-term restoration success requires prioritizing climate resilience — selecting storm-tolerant species, improving river connectivity for sediment delivery and ensuring sites allow for inland migration.

Progress made in restoring these coastal wetlands remains lackluster. Best available estimates of global gains in mangrove extent indicate that these forests expanded across just over 180,000 hectares (ha) between 1999 and 2019. But direct human interventions like planting mangroves or reestablishing tidal regimes accounted for just 8% of these total gains (15,000 ha).

Global efforts to restore another 240,000 ha of mangrove forests by 2030 are well off track and will require these direct gains, which increased by an average of roughly 750 ha per year during this 20-year period, to accelerate more than tenfold. Similarly, estimates of mangrove restoration indicate that progress made in reestablishing these coastal wetlands over the last two decades falls well short of the direct gains needed through 2030 to help combat the climate crisis, and minimizing biodiversity losses would call for even greater ambition: restoring 810,000 ha of deforested and degraded mangroves.

7556: Salt marsh restoration, as measured by gross direct gains in salt marsh extent

Status: Right Direction
Historical Data Methodology and Challenges:

Murray et al. 2022 estimate gross area of tidal marsh gain from 1999 to 2019, defining gain as tidal marsh establishment in areas where tidal marshes were not present in 1999. The vast majority of these gains, however, are due to natural, broad-scale coastal processes like the colonization of new sediments or inland migration, with only 30% likely attributable to direct human interventions like marsh grass planting and other restoration activities, including those that reestablish tidal regimes. We therefore used this proportion of tidal marsh gains (i.e., “direct” gains attributable to human interventions) as a proxy for tidal marsh restoration. We calculated the most recent data point for tidal marsh restoration by taking 30% of the total gross tidal marsh area gained from 1999 to 2019 (116,000 ha), which equals 35,000 ha.

Critically, the establishment of tidal marsh vegetation does not always indicate the recovery of these ecosystems’ species composition and diversity, or their ecological structures and functions. And, in some cases, the addition of tidal marsh vegetation can lead to negative consequences like the spread of invasive, alien species or the loss of tidal mudflats. Therefore, this proxy may include tidal marsh gains that would not be considered tidal marsh restoration. A detailed assessment of the accuracy of this data can be found in Murray et al. 2022.

A final limitation of relying on gross gains in ecosystem extent to approximate restoration is that they only measure changes in land use — for example, from abandoned rice paddies to tidal marshes. The addition of tidal marsh vegetation within existing, degraded tidal marshes represents another form of restoration, but it is not included in the Murray et al. 2022 data.

Target Methodology:

1.5°C-compatible targets for restoring salt marshes are not available, while those focused on minimizing biodiversity loss are either outdated (e.g., Griscom et al. 2017 rely on data published more than two decades ago to estimate a technical potential for salt marsh restoration), not global in scope (e.g., Jankowska et al. 2022 scale U.S. data on the area available for salt marsh restoration in the United States to the global level), or lack sufficient data to translate into a quantitative target (e.g., Díaz et al. 2020 call for a 20% net gain in area by 2050 but do not specify a baseline year). Accordingly, we do not present a quantitative target. Instead, we can only indicate the direction of change required — that salt marsh restoration must increase — as informed by this literature as well as IPBES 2019 and IPCC 2022.

Progress Assessment Methodology:

Outcome indicators in this system experience high interannual variability in historical data due to both anthropogenic and natural causes. Accordingly, 10 years instead of 5 years should be used to calculate the linear trendline where possible. Following Boehm et al. 2021 and due to data limitations, the average annual rate of change across the most recently available time period (1999-2019) was used to estimate the historical rate of change, rather than a linear trendline.

While mangroves primarily grow along tropical shorelines, salt marshes tend to replace these coastal wetlands across temperate and boreal shores. Salt marshes provide habitat for diverse species and offer critical ecosystem services, including coastal protection and carbon sequestration.

Despite their ecological importance, salt marshes have experienced significant declines in their ability to provide these services due to centuries of disturbance. Large areas have been lost due to human activities such as pollution and conversion to agricultural, urban or industrial land.

Salt marsh restoration can enhance carbon sequestration and storage and avoid greenhouse gas emissions that would have otherwise continued for decades after certain disturbances, like the drainage of these coastal wetlands for urban development projects. If implemented following ecological restoration principles, these efforts can also help reverse biodiversity losses (e.g., by recovering critical habitats for species, including refuges for migratory birds and nurseries for fisheries) and reestablish marshes’ ecological functions and services.

Ensuring the long-term survival of these restored ecosystems will also require measures to adapt to intensifying climate impacts, particularly sea level rise. For example, increasing river connectivity can ensure the delivery of sediment, which marshes need for accretion to keep pace with rising tides. Similarly, ensuring that these coastal wetlands have space for inland migration can also help prevent them from drowning.

Best available estimates of global gains in salt marsh extent indicate that these ecosystems expanded across nearly 120,000 hectares (ha) between 1999 and 2019, though direct human interventions like planting marsh vegetation or reestablishing tidal regimes accounted for just 30% of these total gains (35,000 ha). This data indicates that efforts to restore these ecosystems are heading in the right direction.

7576: Lake restoration, as measured by total gross gains in lake surface extent

Status: Insufficient Data
Target Methodology:

Lake restoration is particularly relevant for minimizing biodiversity loss. But there is no scientific consensus on what constitutes a sufficiently ambitious target for lake restoration to meet global biodiversity goals. Accordingly, we can only indicate the direction of change required — that lake restoration must increase — as informed by Pereira and Mulligan 2023 and Tickner et al. 2020.

Lakes are vital ecosystems that provide a wide range of essential services, including supplying safe drinking water, regulating and storing freshwater resources, offering flood protection and drought mitigation, and supporting fisheries and food security. In North America, for instance, more than 30 million people rely on the Great Lakes for their drinking water. Meanwhile, Lake Baikal in Siberia — which holds about a fifth of the world’s freshwater — provides drinking water and aquatic food to approximately 2.5 million people.

Freshwater lakes around the world are facing increasing threats from climate change and other human activities. These impacts, including increasing frequency and severity of lake heatwaves, are already having profound global impacts. In addition, agricultural runoff, wastewater discharge and industrial pollution are introducing excess nitrogen and phosphorus into water bodies, leading to eutrophication — a process in which elevated nutrient levels stimulate excessive algal and plant growth. Combined with rapid warming, these processes drive the growth of harmful algal blooms, which can harm human health, livestock and aquatic ecosystems.

In response, freshwater lake restoration has become a growing global priority. In March 2022, the United Nations Environment Assembly adopted the first-ever resolution on sustainable lake management. Similar regional or transboundary efforts are also emerging. For example, in 2024, Burundi, the Democratic Republic of the Congo, Tanzania and Zambia launched a five-year project to address the threats to the biodiversity of the Lake Tanganyika Basin, including an effort to restore degraded landscapes.

The success of lake restoration will depend on addressing land-based drivers of degradation, which introduce nutrients and pollutants into lakes. Specific restoration measures can also include managing hydrology, constructing wetlands, restoring floodplains, reintroducing native species and controlling invasive species. Together, these strategies can help rebuild the function and resilience of freshwater lakes.

At present, however, there is still no comprehensive global dataset to track restoration progress across freshwater lakes worldwide.

7616: River restoration, as measured by the number of removed river barriers

Status: Insufficient Data
Historical Data Methodology and Challenges:

A comprehensive dataset is not available for this indicator. Data is displayed for the EU only and is sourced from Dam Removal Europe.

Target Methodology:

1.5 degrees C-compatible targets for river restoration are not available. Similarly, there is no scientific consensus on what constitutes a sufficiently ambitious target for freshwater biodiversity conservation, and the literature generally lacks quantitative and time-bound targets for this indicator. Accordingly, we can only indicate the direction of change required — that river restoration must increase — as informed by Tickner et al. 2020 and Lininger and Lave 2024.

Progress Assessment Methodology:

Outcome indicators in this system experience high interannual variability in historical data due to both anthropogenic and natural causes. Accordingly, 10 years instead of 5 years was used to calculate the linear trendline where possible.

Rivers face pressures from a range of human activities that degrade water quality, disrupt natural flows and harm biodiversity. While some rivers remain free-flowing, many others have undergone damming and other extensive modifications for things like hydroelectric power generation, irrigation, flood control and navigation. A 2019 global study found that although 96% of the world’s rivers remained free-flowing over their entire length as of 2019, this share falls dramatically when looking at the 246 rivers longer than 1,000 kilometers (621 miles). Only 37% of those rivers still maintain a direct connection from source to sea.

Dams, levees and weirs provide important societal benefits, including through hydropower — a source of clean, firm power — and enabling water storage, diversion and regulation for agricultural, industrial and domestic use. However, disrupting river connectivity can also have many adverse social and environmental impacts. For example, dams can impede the migration of aquatic species by creating physical barriers and altering the hydrological cues on which they depend. The construction of dams, levees and other water infrastructure projects has also displaced communities and reduced sediment flow, contributing to coastal delta instability and erosion and diminishing the productivity of estuaries on which millions of people depend. Additionally, reservoirs created by dams release greenhouse gas emissions due to decomposing organic material, contributing over 5% of global anthropogenic methane emissions in 2020.

Restoring free-flowing rivers is vital for biodiversity conservation and ecosystem health. A key strategy is reconnection, which involves removing or modifying infrastructure that disrupts the natural interaction between rivers and their floodplains or impedes longitudinal flows. Fish passes and ladders are also commonly used as restoration measures, although their effectiveness can vary widely. Additional activities include reestablishing broader ecological processes like riparian vegetation and reducing stormwater or agricultural runoff. Addressing other stressors, such as the spread of nonnative species and pollutant inputs, is also critical.

Many river restoration efforts are driven by the implementation of national legislation, particularly in China, the European Union and the United States. However, transboundary cooperation is often essential for successful river restoration. For example, the Mura-Drava-Danube Biosphere Reserve, a protected area designated by the UN Education, Scientific and Cultural Organization that spans Austria, Croatia, Hungary, Serbia and Slovenia, is implementing a large-scale restoration project involving over a dozen institutions and organizations across five countries. Similarly, existing initiatives such as the Mekong Cooperation Framework — an intergovernmental organization facilitating regional dialogue and cooperation among Cambodia, Lao People’s Democratic Republic, Thailand and Vietnam — can serve as important platforms for knowledge exchange and joint management in future river restoration efforts.

Some regional efforts are tracking progress for river restoration. For example, according to the database of Dam Removal Europe, a dataset that serves as a proxy for river restoration in Europe, over 9,000 dams have been removed across the continent as of 2024. However, there is no comprehensive dataset tracking these efforts globally, and developing a consistent global monitoring system will be critical to measure progress and guide future action.

Key enablers and barriers to change

7629: Countries with national restoration targets for freshwater ecosystems, as measured by the share of countries that have committed to the Freshwater Challenge

Historical Data Methodology and Challenges:

A total of 81 countries have made the commitment to set and implement quantifiable targets for restoring freshwater ecosystems in their national plans by the end of 2025 as part of the Freshwater Challenge. The percentage was calculated by dividing the number of member countries by 197 countries. Some countries may have established restoration targets without joining the Freshwater Challenge, meaning the indicator may underestimate the overall share of countries with such commitments.

While many countries have signed on to global commitments to restore degraded ecosystems, effectively and equitably contributing to these multinational pledges requires setting national-level targets. Such targets, in turn, can help guide domestic policymaking across ministries and levels of government, encourage action within the private sector and jump-start implementation, particularly when included within countries’ broader strategies like national biodiversity strategies and action plans under the Kunming-Montreal Global Biodiversity Framework and nationally determined contributions under the Paris Agreement.

A flagship example of a global effort focused on freshwater restoration is the Freshwater Challenge, a voluntary, country-led partnership that, among other goals, aims to restore 300,000 kilometers (km) of degraded rivers and 350 million hectares (Mha) of degraded wetlands globally by 2030. So far, 54 countries and the European Union (38% of all countries) have joined this partnership and committed to set and implement quantifiable targets for restoring and conserving freshwater ecosystems in their national plans.

To ensure that these efforts result in successful restoration, countries must also implement strong protective frameworks — including policies, legislation, enforcement and monitoring mechanisms — so that freshwater ecosystems and restored sites are not further degraded, exploited or converted. Establishing and expanding protected areas and other effective conservation measures; enacting and strengthening restoration-related policies, laws and regulations; and providing financial incentives are all critical interventions to reduce pressure on ecosystems and support their long-term recovery.

7555: Countries with at least one policy, law or regulation mandating restoration following ecosystem conversion or degradation

Historical Data Methodology and Challenges:

Data was collected from the FAOLEX database using the following filters: Domain: Water; Type of text: Policies, Legislation and Regulation; Document term: ecosystem restoration; Keywords: “inland fisheries,” “inland water,” “freshwater fishes,” “freshwater pollution.” We exclude legislation and policies that are labeled as “repealed.”

Legally binding legislation, policies and regulations related to freshwater ecosystems are essential to provide clear guidance on best practices for restoration, as well as the environmental and socioeconomic boundaries within which they must operate. Codifying such laws can also signal a nation’s commitment to freshwater ecosystem restoration.

Examples of such instruments include subsidies that incentivize ecosystem restoration, policies that reduce water pollution, water tariff reforms that require utilities to allocate a share of revenues to conservation, and public-private financing mechanisms — such as payments for ecosystem services — that help mobilize funding for freshwater restoration.

For instance, the U.K.’s Environment Act 2021 strengthened regulatory authority to hold polluters accountable, with fines directed to a Water Restoration Fund supporting local water improvement projects. The Indonesian government established the Peatland Restoration Agency in 2016 with a mandate to restore 2.6 million hectares (Mha) of degraded peatlands — an effort that by 2024 had already resulted in the restoration of 1.6 Mha of peatland.

As of 2024, 54% of countries have at least one documented legal or policy instrument focused on freshwater ecosystem restoration — up from just 13% in 2000.

7564: Countries with high and very high levels of implementation of national-level integrated water resources management policies and plans

Historical Data Methodology and Challenges:

The UN Environment Programme calculated scores based on a 33-question survey organized around four main dimensions of IWRM and an average score from 0 to 100, in increments of 10, for each dimension. Countries that had “high” and “very high” levels of implementation are presented in the data above. In 2017, 173 countries were surveyed, then 186 in 2020 and 183 in 2023.

Complex freshwater governance structures where government agencies, Indigenous governments, community groups, NGOs and private actors share overlapping authority can lead to coordination challenges when handling a shared problem. The transboundary nature of many freshwater ecosystems can also lead to competition and suboptimal coordination, which may affect restoration projects, particularly when transboundary cooperation plans are not in place.

Integrated water resources management (IWRM) promotes the cross-body coordinated development and management of water, land and related resources to maximize economic and social well-being without compromising ecosystem health. It focuses on conserving water-dependent ecosystems, preserving biodiversity, maintaining water quality and restoring degraded environments while also addressing the water needs and impacts of agriculture through sustainable irrigation practices, efficient water use in crop production and mitigation of agricultural runoff. It also integrates climate change considerations into water management strategies, helping to adapt to changing precipitation patterns, extreme weather events and rising temperatures while reducing greenhouse gas emissions.

IWRM implementation has resulted in significant and diverse benefits across multiple countries and regions. For example, in Denmark it has led to improved groundwater quality and enhanced drinking water protection. India has seen improvements in rural livelihoods and downstream water quality preservation, and Bangladesh experienced poverty reduction alongside the restoration of vital wetland ecosystems.

Globally, the share of countries with high or very high levels of implementation of national-level IWRM policies and plans grew from 19% in 2017 to 26% in 2023. While this is heading in the right direction, as of 2023, 136 countries still had not made sufficient progress with IWRM implementation, despite the global call for IWRM since 1992.The limited implementation of such policies hinders sustainable water management, leading to conflicts, resource inefficiency and ecosystem degradation.

7621: Finance for restoration, as measured by total finance for nature-based solutions

Restoring critical freshwater ecosystems can help revive biodiversity, support climate mitigation and deliver a wide range of societal benefits. Yet restoration finance remains far below the levels needed to achieve these goals.

Globally consistent, annually updated data that focuses on funding dedicated to restoring converted and degraded ecosystems is currently not available. Instead, the United Nations Environment Programme (UNEP) publishes the State of Finance for Nature, which routinely estimates public and private funds flowing to nature-based solutions more broadly. The latest installment finds that total tracked finance flowing toward these measures reached roughly $220 billion in 2023 — only a 5% increase from 2022.

These investments would need to more than double to reach the $571 billion needed per year by 2030 and more than triple to $771 billion per year by 2050 to help achieve the goals of the Paris Agreement, the Kunming-Montreal Global Biodiversity Framework and Land Degradation Neutrality. In the near term, investment needs are highest for restoration — particularly mangroves, salt marshes and peatlands — with $83 billion needed annually by 2030 and $61 billion by 2050 for these three ecosystems alone, compared to just $64 billion invested across all restoration efforts, as well as those focused on sustainable land management, in 2022. At the same time, nearly $7 trillion in annual financial flows continue to actively harm nature, vastly overshadowing investments in restoration and other nature-based solutions. While the UNEP report provides critical insight into the scale of change required to accelerate restoration, data on funding specifically dedicated to restoring freshwater ecosystems remains relatively scarce.

7562: Lower levels of corruption, as measured by the share of countries scoring relatively highly on absence of corruption

Historical Data Methodology and Challenges:

The World Justice Project (WJP) Rule of Law Index measures three forms of corruption — bribery, undue influence by public or private interests, and misappropriation of public funds or other resources — across the executive, judicial and legislative branches, as well as within the police and military. Its data is constructed through general population polls and expert questionnaires to capture perceptions of and experiences with corruption in a given country. However, this approach to measuring corruption remains challenging due to definitional issues and because corruption itself is not directly observable. Systems Change Lab includes additional governance system indicators that focus on more specific structural measures that countries have implemented to reduce corruption. A key limitation of relying on this data is that these three forms of corruption may all influence the freshwater sector, but the data do not specifically measure corruption within the freshwater sector. Rather, this data assesses overall government corruption, which can vary across sectors within the same country. Countries that scored >0.6 on a scale of 0.0 (lowest) to 1.0 (highest) were included in the selection criteria as indicative of countries that have relatively low levels of corruption. This threshold was determined jointly via expert judgment by Systems Change Lab and WJP researchers. Finally, data is available beginning in 2012, but to maintain a more consistent country sample, Systems Change Lab presents data from 2021 onward. The number of countries included in each year of data varied: 139 countries in 2021, 140 countries in 2022, 142 countries in 2023 and 2024, and 143 countries in 2025. The numerator reflects the number of countries that scored >0.6, while the denominator includes all countries with scores in a given year.

The success of freshwater restoration depends not only on governments strengthening national policies, laws and regulations to protect ecosystems but also on their willingness to act with integrity and apply these policies consistently, including to those with political and economic power. Abuses of power for private gain can occur across all levels of government and can include public officials participating in fraud, embezzlement and laundering schemes.

Particularly prevalent in megaprojects commonly associated with water resource development such as hydropower, corruption can also emerge in other areas of the water sector, from water resources management to drinking water services and irrigation. Corruption can also directly undermine the success of freshwater restoration efforts. Corruption may affect restoration projects not only directly but also by diverting funding from effective cost-effective nature-based restoration in favor of large-scale flood control projects.

According to the World Justice Project Rule of Law Index, corruption is relatively low in roughly 43% of countries, a figure that has remained fairly stable in recent years. The lack of marked progress highlights the need for continued efforts to curb corruption in all its forms. Evidence suggests that in countries with significant freshwater resources — such as those in the Mekong River Basin — corruption continues to pose a challenge. 

7575: Stronger regulatory enforcement, as measured by the share of countries scoring relatively highly on regulatory enforcement

Historical Data Methodology and Challenges:

The World Justice Project (WJP) Rule of Law Index measures the extent to which legal and administrative regulations are effectively and fairly implemented and enforced. It examines whether regulatory enforcement is subject to improper influence, administrative proceedings are conducted without unreasonable delays, due process is respected within these proceedings, and governments respect property rights. A key limitation of relying on this data is that these facets of regulatory enforcement can all impact the freshwater sector, but the data do not specifically measure effective enforcement of freshwater sector regulations. Rather, this data assesses overall regulatory enforcement, which can vary across sectors within the same country. Countries that scored >0.6 on a scale of 0.0 (lowest) to 1.0 (highest) were included in the selection criteria as indicative of countries that have relatively high levels of regulatory enforcement. This threshold was determined jointly via expert judgment by Systems Change Lab and WJP researchers. Finally, data are available beginning in 2012, but to maintain a more consistent country sample, we present data from 2021 onwards. Still, the number of countries included in each year of data varied: 139 countries in 2021, 140 countries in 2022, 142 countries in 2023 and 2024, and 143 countries in 2025. So, the numerator reflects the number of countries that scored >0.6, while the denominator includes all countries with scores in a given year.

Weak institutional capacity, particularly at local levels, often impedes countries that have established supportive restoration policies on paper — such as policy, law or regulation that mandates or incentivizes freshwater restoration, or policies on community-based water tenure rights — from implementing them in practice. Ensuring that local governments are well-resourced, adequately staffed and politically empowered to implement restoration policies, as well as enforce supportive laws and regulations, can help build much-needed capacity.

Government capacity, however, can be quite difficult to quantify — for example, it encompasses mechanisms for coordinating across ministries and at different scales of government, leadership structures, processes for allocating funds to local levels, and institutional incentives needed to deliver conservation strategies. This indicator uses aggregate scores focused on regulatory enforcement from the World Justice Project Rule of Law Index as a proxy. 

As of 2025, only 31% of 143 governments around the world boasted relatively high levels of regulatory enforcement, and this share has remained relatively stable. 

7630: Locally led restoration projects with participatory and inclusive decision-making processes

The U.N. Decade on Ecosystem Restoration highlights the importance of equitable processes and outcomes, including building the capacity of Indigenous Peoples, Afro-descendant Peoples, local communities, women and youth to take an active role in restoration.

Many freshwater resources hold important cultural and spiritual value for communities; as such, their meaningful engagement in restoration projects is essential. Research has also shown that improving equity in restoration practice can improve success rates and provide many co-benefits such as training and jobs.

Local- and community-led restoration involves thorough consultative processes that build ownership over both the project and its outcomes, support local data ownership and sovereignty, engage respectfully with local knowledge and reflect local values throughout implementation. While no global dataset currently exists to assess equity in restoration, it remains a critical ingredient for success.

7570: Countries legally recognizing community-based water tenure rights to access and use water

Historical Data Methodology and Challenges:

The data for this indicator is sourced from the Rights and Resources Initiative and the Environmental Law Institute’s “Whose Water?” report. This report uses a freshwater tenure methodology that captures the legal entitlements most essential for securing community-based freshwater tenure. Because the analysis is limited to the legal frameworks of 15 countries, a global assessment is not currently available.

Water tenure rights define how people can access, use, manage and make decisions about water resources. Secure and well-defined water rights are central to safeguarding access to water by Indigenous Peoples, Afro-descendant Peoples and local communities and enabling them to manage resources sustainably and equitably. The recognition of Indigenous water rights has also been shown to support the restoration of ecological and cultural resources by enabling a governance system that responds to these communities’ needs.

By contrast, threats to communal waters held by Indigenous Peoples, Afro-descendant Peoples and local communities can undermine water-based livelihoods and deepen water insecurity among already marginalized communities. Recognizing and establishing secure water rights for these communities is therefore critical to protecting their human and territorial rights and supporting sustainable, community-led resource management and resilient livelihoods.

Building on the Rights and Resources Initiative (RRI) land and forest tenure methodology, the RRI and the Environmental Law Institute developed a framework that defines community-based water tenure regimes as systems in which a local community has legally recognized rights to use and manage a freshwater resource and/or decide who is allowed to use it. Examples include the right to manage the rivers and lakes in their region or to set up and control small-scale irrigation systems stemming from communal freshwater sources.

In their 2020 report “Whose Water?” these partners identified 39 community-based water tenure regimes in 15 countries, providing a baseline for tracking legal recognition of community freshwater rights. The report also evaluated these regimes based on their ability to support community survival, culture, livelihoods and development — particularly for Indigenous Peoples, Afro-descendant Peoples and local communities.

While the report finds that rights to use and govern freshwater exist in 14 of the 15 countries assessed, significant legislative gaps and administrative barriers continue to limit communities’ ability to effectively manage and protect their freshwater resources. Data for more countries is also needed to more comprehensively assess global trends.

7631: Countries upholding the right to free, prior and informed consent for Indigenous Peoples, Afro-descendant Peoples and local communities

In addition to protecting the substantive rights of Indigenous Peoples, Afro-descendant Peoples and local communities to their land and freshwater resources, safeguarding their procedural rights — namely, the right to free, prior and informed consent (FPIC) — is equally critical.

FPIC is a specific right for Indigenous Peoples as part of the universal human right to self-determination, allowing them to give, withhold or withdraw their consent for a project that may impact them or their territories; this consent should be given without intimidation or coercion through processes defined by the affected Indigenous communities.

FPIC is recognized prior to state approval of any project affecting their lands or territories and other resources, including water resources. The United Nations Decade on Ecosystem Restoration emphasizes the inclusive participation of all stakeholders — particularly Indigenous Peoples and local communities — throughout restoration, including through free, prior and informed consent, as essential for long-term success.

FPIC is explicitly enshrined within the United Nations Declaration on the Rights of Indigenous Peoples (UNDRIP), as well as the International Labor Organization Convention 169 on Indigenous and Tribal Peoples. The U.N. Food and Agriculture Organization also highlights FPIC as a best practice in engagement with local communities. But while more than 150 countries have adopted UNDRIP — an example of “soft law” that is not legally binding — fewer than 25 have ratified the legally binding ILO Convention.

What is more, even in countries that legally recognize communities’ right to FPIC, governments still fall short of upholding this right in practice, and global data on national level enforcement of FPIC is not currently available.

7612: Freshwater restoration monitoring, as measured by the share of restored freshwater ecosystems monitored over the long term

Restoration outcomes can be highly variable. Monitoring can help those charged with restoration identify and track progress, providing insight into where approaches are succeeding or failing so that practitioners can adjust their approach over time. Monitoring mechanisms include defining indicators to assess biodiversity and ecosystem function recovery over time, establishing baselines for those indicators, collecting long-term data and systematically reporting results.

Monitoring and evaluating freshwater restoration poses many challenges. First, there is no single definition of what constitutes “successful” restoration, which makes tracking progress difficult. Progress is further constrained by several factors, including a lack of systematic monitoring protocols, insufficient dedicated funding, and poorly quantified benefits of monitoring, contributing to perceptions of low return on investment.

In addition, monitoring freshwater restoration presents unique challenges. Rivers naturally change in their flow, physical form and ecology along their course, making it difficult to identify suitable reference sites to measure restoration outcomes. Even in freshwater ecosystems where monitoring is in place, these efforts are often biased toward monitoring vertebrates, even though invertebrates make up the majority of freshwater animal diversity.

Despite these challenges, expanding the area of land and water monitored for long-term effectiveness is critical to improving restoration success. Global data on countries establishing and maintaining restoration monitoring systems is limited, and there is no global data specifically available for freshwater restoration.

Scaling up long-term restoration monitoring systems is essential not only for tracking progress of specific projects but also for building the evidence base needed to design more effective strategies globally. Such monitoring systems can take many forms — for example, citizen science can engage communities in long-term monitoring of freshwater resources, while AI-driven monitoring can allow practitioners to process larger volumes of data than possible with conventional methods. In some cases, these technologies can be more cost-effective, safe and transboundary, among other benefits – although the benefits of novel technologies must be carefully weighed against the environmental resources they consume. Integrating Indigenous and local knowledge systems in monitoring can further strengthen freshwater restoration by providing long-term, place-based insights.

Other shift Other shifts needed to transform the system

Minimize disruptions to the timing and quantity of the water cycle

Amid disruptions from climate change, overconsumption of water in developed economies and land use change, safeguarding the water cycle is essential to ensuring a future where communities and ecosystems thrive.

Effectively halt conversion and degradation across freshwater ecosystems

Converting and degrading freshwater ecosystems undermines their ability to deliver critical services to people and nature. Effectively halting this destruction is crucial to prevent continued biodiversity loss, preserve climate mitigation benefits and support sustainable development for communities around the world.

Sharply reduce water pollution and improve water quality

Freshwater quality is declining worldwide, reducing access to clean water and increasing pressure on biodiversity. Rapid action is needed to curb human activities driving water pollution and secure a long-term supply of clean water for all.

Ensure equitable access to safe and affordable drinking water, sanitation and hygiene for all

Equitable and affordable access to clean water and safe sanitation and hygiene services are essential for human health, ecosystem protection and climate resilience. However, billions of people, particularly those with the fewest resources, are still being left behind.

Halt the overexploitation of wild, freshwater species and ensure sustainable use

Freshwater species play vital roles in keeping water clean, cycling nutrients and underpinning human food systems. Yet they are disappearing at alarming rates — a crisis that threatens to unravel ecosystems, weaken the planet’s ability to provide clean water and undermine human well-being.