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.

Freshwater ecosystems support an exceptional diversity of life, from fish, amphibians and mollusks to invertebrates and aquatic plants. Despite covering less than 1% of the Earth’s surface, these ecosystems contain around 10% of all described species and one-third of vertebrates. They also deliver vital services to millions of people, including providing clean water, food and climate regulation.

However, since 1970, monitored populations of freshwater species have declined by 85%, largely due to habitat loss and degradation, as well as overfishing and overexploitation, pollution, climate change and invasive species. Even though these species have tremendous value, they have received less global attention than their terrestrial or marine counterparts, threatening a missed opportunity to protect these unique and essential forms of life while we still can.

The latest science demands an urgent halt to and reversal of freshwater biodiversity loss. Preventing the overfishing and overexploitation of freshwater species and promoting their sustainable use are key elements of Target 5 of the Kunming-Montreal Global Biodiversity Framework, as well as other global agreements such as the U.N. Sustainable Development Goals.

However, several barriers limit the world’s ability to make progress toward these objectives. For instance, fragmented and inadequate fishery management and governance structures often underrepresent fishers themselves in decision-making processes, which limits effectiveness. Weak policy enforcement and unavoidable impacts from other sectors (for example, water use for agriculture) also further limit the ability to sustainably manage fisheries and prevent overexploitation. Therefore, strengthening local and transboundary governance, improving fisher participation and supporting community-based management will be essential.

Lack of available, geographically representative data on things like catch levels, fishing intensity and prevalence of illegal activities in freshwater fisheries is another major challenge that has inhibited progress. Ever-changing contexts that are further exacerbated by climate change require data to be constantly reevaluated to adequately inform policy, while data deficiencies, along with unattainable data requirements, limit our ability to monitor and assess freshwater species. Furthermore, limited freshwater species and fishery data can mean that many people might not even know that the unique biodiversity in their own country, state or backyard is disappearing.

Ultimately, the world needs a coordinated, well-funded and global effort that prioritizes the conservation of freshwater species by halting overfishing and overexploitation and ensuring that their use is sustainable. This should include policy that incentivizes sustainable use of freshwater species, co-management efforts and compliance with international treaties.

Tracking progress on global outcomes

7651: Extinction risk for overexploited freshwater species, as measured by the number of species threatened with biological resource use on the IUCN Red List

Status: Wrong Direction
Historical Data Methodology and Challenges:

Data sourced from the IUCN Red List of Threatened Species maintained by the International Union for Conservation of Nature (IUCN) (IUCN 2024). The IUCN Red List is the most extensive resource for information on the global conservation status of animal, fungi and plant species. The IUCN Red List serves as an essential measure of the state of global biodiversity but is reliant on the availability of experts, time and resources to invest in the process. Data includes all species across fully or partially terrestrial ecosystems living in Freshwater (= inland waters). Data focuses on species facing the "biological resource use" threat category, which encompasses the effects of intentional and unintentional harvesting, as well as the persecution or control of specific species. Data included only for freshwater species that are categorized as Critically Endangered, Endangered and Vulnerable, in order of decreasing risk of extinction. The best estimate formula outlined in Baillie et al. 2004 was applied to the raw data to assess extinction risk: Critically Endangered (CR), Endangered (EN) and Vulnerable (VU) / (total assessed — Extinct (EX) — Extinct in the wild (EW). Notably, the raw data contains many data gaps, resulting in at times very infrequent and likely incomplete annual observations for these categories. Data is also missing for the years 2001, 2002 and 2005. Observations begin in 1996 with 2 distinct species and steadily increase over the next decades until 2025, when the total cumulative number of distinct species monitored under biological threat reaches 5,536. Users should note that the IUCN Red List covers just 7% of the world’s described species, and that many fungi, plants, invertebrates and other groups suffer significant gaps.

Target Methodology:

Reducing extinction risk for overexploited freshwater species is particularly relevant for minimizing biodiversity loss. But there is no scientific consensus on what constitutes a sufficiently ambitious target to meet global biodiversity goals. Accordingly, we can only indicate the direction of change required — that the extinction risk for overexploited freshwater species must decline — as informed by Target 4 and Target 5 of the Kunming-Montreal Global Biodiversity Framework. The benefits of this directional target for freshwater ecosystems are also elaborated in Tickner et al. 2020 and Su et al. 2021.

Progress Assessment Methodology:

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

An estimated 1 million species globally are threatened with extinction, and many of them will disappear within decades. Overexploitation — when species are used, either directly or indirectly, at a faster rate than they can be replaced — is an immediate driver of population declines and increased extinction risk. 

Overexploitation represents a major threat to freshwater ecosystems. To combat it, the use of and trade in wild freshwater species should be conducted legally, sustainably and safely, from exploitation and harvest through consumption. 

Tracking the total number of species threatened with overexploitation is essential to understanding the scope of the threat. This includes whether a species is directly exploited or if it is a byproduct of other activities, such as being inadvertently caught as bycatch by commercial fisheries. 

The impact of these threats extends beyond a single species and can often result in “collateral damage” to nontarget species and their habitats. Furthermore, the national and international wildlife trade for commercial, subsistence or cultural purposes remains an underestimated threat to endemic freshwater species. This trade is not limited to live animals but also includes specimens harvested for meat, skins, shells, medicinal products or other derivatives — contributing to the overexploitation of certain freshwater species, such as turtles and tortoises.

The IUCN Red List of Threatened Species evaluates extinction risk, as well as identifies which species are threatened by “biological resource use,” or consumptive use of wild resources, including deliberate or unintentional harm or efforts to control or remove species. While this indicator lacks systematic monitoring, historical data is available if interpreted with appropriate caveats, such as increasing assessment effort. The IUCN Red List maintained by the International Union for Conservation of Nature (IUCN) is also limited in scope, as not all species across all regions have been assessed, and the list is known to represent some taxa better than others.

However, among identified threats to listed species (e.g., agriculture and aquaculture, pollution, energy production and mining), terrestrial and freshwater species threatened with “biological resource use” amassed the most records to date. The proportion of species threatened by overexploitation has increased over time, and this trend is expected to continue. For example, in 2012 overexploitation threatened 24% of assessed freshwater species with extinction, and in 2025 this percentage had risen to 63%. This number is likely much higher in reality, as many freshwater species are not yet assessed by the IUCN Red List, and a large number are still unknown to science.

7595: Proportion of freshwater species that are depleted, as measured by the IUCN Green Status of Species

Status: Wrong Direction
Historical Data Methodology and Challenges:

Data was filtered on the IUCN Red List database by: System: Freshwater (= inland waters); Filter On: Green Status. The IUCN Green Status of Species framework was developed by the International Union for Conservation of Nature (IUCN) to measure conservation success of species. It is a new global framework that assesses and measures species recovery and the impact of conservation over time. The “Green Score” ranges from 0–100%, showing how far a species is from its "fully recovered" state. Only a small number of species are currently assessed by the Green Status of Species. Of the six classes of freshwater species currently assessed, only three are represented by more than a single species (fishes, amphibians, birds). The proportion is calculated by dividing the number of depleted species by the number of species assessed per year.

Target Methodology:

The proportion of freshwater species that are depleted is particularly relevant for minimizing biodiversity loss. But there is no scientific consensus on what constitutes a sufficiently ambitious target to meet global biodiversity goals. Accordingly, we can only indicate the direction of change required — that the proportion of freshwater species that are depleted must decline as informed by Target 4 of the Convention on Biological Diversity Kunming-Montreal Global Biodiversity Framework, Target 1.3 of the Convention on Migratory Species’ Samarkand Strategic Plan for Migratory Species 2024-2032 and Target 1.3 of the Ramsar Convention on Wetlands’ Fifth Strategic Plan 2025-2034. The benefits of this directional target for freshwater ecosystems are also elaborated in Tickner et al. 2020 and Su et al. 2021.

Progress Assessment Methodology:

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

Freshwater species have long been an important source of food, medicine and materials for people across the globe. This versatility has driven unsustainable harvesting, causing population declines that destabilize ecosystems and threaten human health and well-being. Freshwater species are among the groups most sensitive to anthropogenic pressures, including overexploitation.

The IUCN Green Status of Species maintained by the International Union for Conservation of Nature (IUCN) is a global framework that assesses and measures species recovery and the impact of conservation over time. A complement to the IUCN Red List of Threatened Species, which assesses species’ extinction risk, it enables more systematic and comprehensive tracking of the extent to which species populations have recovered.

The IUCN Green Status of Species measures freshwater species depletion by assessing how far populations have declined from their historical range, viability and ecological function, providing a recovery-based lens that captures long-term biodiversity loss beyond extinction risk alone. Identifying a clear natural baseline remains challenging but is essential for accurately tracking depletion levels.

Assessments require significant expert input, time and resources, including conducting an IUCN Red List assessment in parallel. Freshwater species are often underrepresented in the IUCN Red List, which contributes to persistent data gaps. Although only 39 freshwater species have been assessed under the IUCN Green Status of Species, the proportion of species characterized as depleted increased from 3% in 2011 to 100% in 2025.

Given the limited data available, each additional assessment by the IUCN Green Status of Species can significantly shift the proportion of freshwater species classified as depleted, a trend expected to continue. Nonetheless, there is growing attention on freshwater species, and more freshwater species are being assessed than ever before, creating an opportunity to fill knowledge gaps.

7654: Overfishing pressure, as measured by the share of inland water fisheries with moderate and high pressure rankings by the Sustainable Watershed and Inland Fisheries Index

Status: Insufficient Data
Historical Data Methodology and Challenges:

Criteria for pressure categories are evaluated on a numeric scale of 1 (low pressure) to 10 (high pressure), where low pressure refers to those with a score of 1–3, moderate pressure a score of 4–7 and high pressure a score of 8–10.

Target Methodology:

Reducing overfishing pressure is particularly relevant for minimizing freshwater biodiversity loss and enabling sustainable development. But there is no scientific consensus on what constitutes a sufficiently ambitious target to meet global biodiversity and equity goals. Accordingly, we can only indicate the direction of change required — that overfishing pressure must decline — as informed by the Kunming-Montreal Global Biodiversity Framework (Target 5 and Target 10) and complemented by SDG 15.7. The benefits of this directional target for freshwater ecosystems are also elaborated in Tickner et al. 2020 and Su et al. 2021.

Population growth and shifting consumption patterns drive rising demand for food. The pressure is especially acute in food-producing ecosystems, including freshwater ecosystems. This global risk is reflected in multiple international development and biodiversity targets, including Target 14.4 of the U.N. Sustainable Development Goals and Target 5 of the Kunming-Montreal Global Biodiversity Framework.

As demand for food grows, the pressure to increase catches from inland fisheries intensifies, often exceeding sustainable limits and driving practices that threaten long-term productivity and biodiversity.

These unsustainable practices can include overfishing and destructive fishing methods, illegal fishing, the transport, trade or sale of illegally or unsustainably sourced species through domestic and international markets, and associated pressures from pollution and bycatch, which can cause unintended harm to nontarget species.

In marine systems, which are better studied than freshwater, these pressures primarily stem from companies based in high-income countries; however, small-scale fisheries can also contribute to unsustainable practices. Assessing evidence of overexploitation is further complicated by underreporting, as estimates suggest that many freshwater catches may be 65% higher than officially reported.

The Food and Agriculture Organization’s report “State of World Fisheries and Aquaculture 2026” revealed that among major inland water basins crucial to inland fisheries, 40% experienced moderate pressure and 13% experienced high pressure in 2024 — down from 55% experiencing moderate pressure and 17% experiencing high pressure in 2022.

While this trend is promising, a significant proportion of inland fisheries globally are experiencing moderate or high pressure. It is therefore essential to continue improving management practices in inland fisheries. Worldwide, inland fisheries are highly diverse, spanning a range of species and fishing methods. Many of the world’s inland fisheries are concentrated in resource-constrained countries, with 90% of global inland fishery catch coming from developing countries across Asia and Africa. Limited resources pose challenges for effectively monitoring and managing these fisheries, further compounded by the transboundary nature of many rivers.

Key enablers and barriers to change

7625: Extreme poverty in biodiversity hotspots, as measured by the share of the population living below the extreme poverty line in countries with biodiversity hotspots

Historical Data Methodology and Challenges:

This indicator measures the share of the population living below the global extreme poverty line ($3.00/day at 2021 purchasing power parity) in countries containing biodiversity hotspots, used as a proxy because poverty data specific to hotspot areas is not available. The list of countries containing biodiversity hotspots is obtained by overlaying the Biodiversity Hotspots v2016.1 shapefile with Natural Earth 1:50m country boundaries. Any country overlapping a hotspot is included, for a total of 157 countries (120 with World Bank poverty data) across the 36 biodiversity hotspot areas recognized by Conservation International and the Critical Ecosystem Partnership Fund.

The global value for each year is the total poverty population (poverty headcount (%) × total population) across the hotspot countries that reported poverty data that year, divided by the total population of those same reporting countries.

China is excluded because its large population caused abnormal swings in the global value as it entered and left the set of reporting countries. Data for 2025 is not included because only four countries have reported poverty data so far.

Addressing poverty is crucial for preventing the overexploitation of species. Economic insecurity can drive communities to rely more heavily on natural resources for immediate survival, often resulting in unsustainable harvesting.

Some solutions jointly fight poverty and the unsustainable use of freshwater resources, including implementing fair trade practices where products are traded internationally; supporting local economies; and ensuring sustainable pricing that reflects the true value of natural resources. Reducing poverty can also lead to more sustainable resource management by enabling better access to education, alternative livelihoods and stronger community engagement in conservation efforts.

According to the World Bank’s Poverty and Inequality Platform, the total population living in poverty has decreased over time. In 1981, more than 2.1 billion people were living below the extreme poverty line (a threshold of less than $3.00 per day in 2021 dollars). As of 2024, this number had decreased to around 847 million people. Across countries with biodiversity hotspots, the percentage of people living below the global poverty line has also declined, from 24% in 2000 to 6.2% in 2024.

While these trends are positive, they are not necessarily directly attributable to biodiversity outcomes and likely reflect wider socioeconomic changes occurring alongside, rather than because of, conservation gains.

To meet global conservation goals and halt unsustainable resource use, the drivers of species overexploitation need to be addressed, including poverty. As a result, future efforts must work toward global poverty alleviation.

7626: National policies incentivizing sustainable species use, as measured by people living in countries with at least one policy instrument incentivizing sustainable use of freshwater species

7640: Share of fished freshwater species with a stock assessment

Historical Data Methodology and Challenges:

Data from stock assessments is available for marine species but mostly missing for freshwater species. Although global freshwater fish catches have remained largely static, reliable data on catch levels is also largely lacking. FAO’s FishStat database contains records for freshwater species, including global annual stock assessments. We deleted duplicate species to arrive at a total number of unique freshwater species contained in the database, and then tracked yearly values. A limitation of the methodology is that many records indicated a zero value, which we assumed to mean there was no assessment for that species; however, this could also have meant zero fish were left in that stock.

While many marine fisheries management plans have reduced catch levels and allowed stocks to rebuild, they could not have done so without stock assessments. A stock assessment provides an overview of the state of fishery resources to inform policy, decision-making, management and monitoring for long-term sustainability.

Although catch rates of freshwater fish are rising globally, available data on catch levels — especially for small-scale fisheries — is still limited. This lack of geographically representative data limits the ability of authorities to monitor illegal activities in the rare cases where an inland fishery has regulations, and for fisheries managers to understand potential collapses and what actions are required to protect or recover overexploited populations. Most of the world’s fish species remain under- or unassessed: An estimated 40% of wild fish that are caught are not identified or reported at the species level, drastically limiting the ability to manage fisheries sustainably.

Stock assessments tend to concentrate on high‑volume or economically important fisheries. Within this subset, approximately three‑quarters of globally fished species (75% of 336 unique species with available assessments) are now covered by formal stock assessments, increasing from 47% in 2000. However, global stock assessment data rarely distinguishes between marine and freshwater species, meaning inland fisheries are often poorly represented. As a result, freshwater species remain largely absent from global fisheries management frameworks, reflecting persistent data gaps and limited monitoring of inland fisheries.

Accordingly, while monitoring of fish stocks does appear to be increasing over time, this trend does not mean the world is on track for maintaining and sustaining healthy fish stocks, especially given the underrepresentation of inland fisheries in global policy and elsewhere.

7554: Co-managed freshwater fisheries, as measured by the proportion of global catch covered by national co-management agreements

Historical Data Methodology and Challenges:

Data presented is based on co-management policies and the amount of catch governed for half the global small-scale fisheries catch.

Fragmented governance and management of freshwater ecosystems and fisheries, as well as a lack of representation of fishers themselves in decision-making processes, are significant barriers to sustainable use of freshwater resources.

Co-management constitutes a partnership arrangement in which the government, the community of local resource users (fishers), external agents (nongovernmental organizations, research organizations), and sometimes other fisheries and resource stakeholders (boat owners, fish traders, credit agencies or money lenders, tourism operators, etc.) share the responsibility and authority for decision-making over a fishery’s management.

Top-down approaches to fisheries management have frequently failed to prevent fish populations from overexploitation, and in many marine contexts have exacerbated socioeconomic issues and biodiversity loss through mismanagement. An adaptive and collaborative framework such as co-management can help overcome such barriers.

According to the “Illuminating Hidden Harvests” report, among assessed global freshwater and marine small-scale fisheries, 40% of the global catch in 2023 was derived from small-scale co-managed fisheries implemented by national agreements. However, fisheries experts concluded only half of these agreements demonstrated the high level of fisher participation required for true co-management. The report also highlights that co-management is more commonly seen in local agreements, where it accounts for 90% of local catch. Nevertheless, expert-derived high fisher participation in local co-management arrangements remains relatively low, with only 40% of local fisheries demonstrating high levels of fisher participation.

The findings indicate that policies mandating co-management processes in fisheries does not always culminate in co-management in practice. Further, given that the study combines data on marine and freshwater fisheries and species, understanding of the levels of fisher participation in co-management of freshwater fisheries specifically remains limited outside specific regional contexts (e.g., the Brazilian Amazon), representing a knowledge gap.

Co-management in fisheries is widely considered to be one of the primary factors influencing the governance and management effectiveness of fisheries. Research shows that with suitable institutional frameworks, strong leadership and social cohesion, co-management can lead to improved ecological and social outcomes in marine systems.

Although local co-ownership and co-management are the ultimate goals for many small-scale fisheries, a standardized definition of co-ownership, alongside the availability of comprehensive data on small-scale fishery governance, ownership and management, is limited. By combining relevant information about how freshwater fisheries are governed and managed, countries will be able to share best practices and assess their own standing on the global scale.

7571: Freshwater Key Biodiversity Areas covered by protected areas

Historical Data Methodology and Challenges:

Data was directly extracted from Sustainable Development Goal 15.1.2, “Average proportion of Freshwater Key Biodiversity Areas (KBAs) covered by protected areas (%).”

Key Biodiversity Areas (KBAs) are “the most significant sites on Earth for nature,” identified because they are “crucial for maintaining the health of our planet and ensuring various species can survive.” They play a vital role in conservation — particularly for freshwater ecosystems, which often support high numbers of endemic and threatened species that are highly localized and depend on specific habitats, such as fish nurseries and breeding or spawning grounds.

KBAs are located around the world, but many remain outside formal protected and conserved areas. Identifying and delineating KBAs is a continuous process. As of 2024, 44% of freshwater KBAs were estimated to be fully or partially covered by protected and conserved areas, improving since 2000, when 27% of freshwater KBAs were estimated to be covered by protected and conserved areas.

KBAs help focus conservation efforts, and possibly legal protection, on habitats that are most at risk from threats such as pollution, damming, water extraction and invasive species. KBAs are identified based on specific criteria related to their genetic, species and ecosystem composition.

Conservation, restoration and sustainable use of freshwater ecosystems are central to Goal 15 of the U.N. Sustainable Development Goals. KBAs and protected areas are important approaches to help ensure the sustainable use of unique freshwater biodiversity. However, habitat protection alone is inadequate, especially for areas connected to larger systems, and recovery plans may be necessary for some overexploited species.

7552: Total finance available for strengthening local and global institutional capacity to address illegal, unreported and unregulated fishing in freshwater ecosystems

Despite limited global data, illegal, unreported and unregulated (IUU) fishing is a significant pressure in inland waters. This threat can undermine sustainable fisheries management and biodiversity conservation, and impact livelihoods at national and regional levels. For inland fisheries, IUU fishing remains a complex issue because of difficulties in defining the legality of freshwater fishing. Many developing countries lack the resources and infrastructure to effectively monitor and control fishing activities within their waters. As a result, enforcement is sporadic or absent, allowing IUU fishing to operate with low risk of detection, which in turn exacerbates the effects of overfishing and the depletion of freshwater species.

To facilitate implementing sustainable freshwater fisheries practices globally, increased funding is needed to improve monitoring and surveillance, as well as to better enforce local governance. Ultimately, increasing financial support for both local and global institutional capacity strengthening is essential to limit IUU fishing, ensuring the sustainability of fish stocks and the continued well-being of communities dependent on freshwater resources.

There is currently no data available, due to the diversity of fishery types and the challenges of aggregating information to a global level in freshwater ecosystems. Future monitoring efforts are therefore needed to enable meaningful assessment of progress.

7569: 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 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, we are currently unable to assess global progress.

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 Indigenous Peoples, Afro-descendant Peoples and local communities’ access to water and enabling them to manage resources sustainably and equitably.

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.

Adapted from the Rights and Resources Initiative (RRI) land and forest tenure methodology, the RRI and 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 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 across 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.

7559: Number of freshwater species threatened by trade, as measured by the number of freshwater species threatened by biological resource use listed in the CITES appendices

Historical Data Methodology and Challenges:

Threatened freshwater species were identified on the IUCN Red List of Threatened Species using the following filters: Red List Category: Extinct in the Wild (EW), Critically Endangered (CR), Endangered (EN), Vulnerable (VU) and Lower Risk: Conservation Dependent (LR/cd); Threat: Biological resource use; Systems: Freshwater (= inland waters). Identified freshwater species from the IUCN Red List were then compared to species in the CITES Trade Database. There were 195 unique species in this time period (2000-2024). Many species appear over the course of multiple years. Species with “N” under the CITES Appendix were excluded from this dataset. The IUCN Red List and CITES Trade Database present various data challenges, such as records with missing information. These data gaps contribute to uncertainties in the reporting. Regular assessments of the risk international trade poses to all species are needed at all scales: regional, national and international. An automated approach to this was presented at the 20th meeting of the Conference of the Parties to CITES.

Direct overexploitation of wild species populations for food, medicine, and the ornamental and pet trade, among other drivers, is a major cause of biodiversity decline in freshwater ecosystems. This is highlighted in Target 5 of the Kunming-Montreal Global Biodiversity Framework, which calls for ensuring sustainable harvesting and trade of wild species by 2030.

To mitigate this threat, efforts should focus on ensuring the legality, sustainability and safety of harvesting, transportation, trade and consumption of wild fauna and flora. For example, the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) is an international agreement between governments designed to ensure that sustainable trade in wild animals and plants does not threaten species survival.

Between 2000 and 2024, CITES records show 844 instances of threatened freshwater species under Appendix I, II or III, of which 195 were identified on the IUCN Red List in 2024 as threatened with biological resource use. The CITES Appendices represent different levels of protection for species, depending on the appendix in which a species is listed.

However, research highlights gaps in our collective understanding of which species are threatened by trade. With 5.8% of Critically Endangered, Endangered, Vulnerable or Near Threatened species impacted by international trade, and around half of these species being either Critically Endangered or Endangered, regular assessments of the risks to species posed by international trade are needed.

This is especially true for freshwater species, which have historically received less attention than marine species. However, the growing inclusion of freshwater taxa in both the CITES appendices and IUCN Red List assessments, driven by new national proposals and assessments, is expected to influence this indicator going forward.

7617: Countries preventing IUU large-scale fishing, as measured by people living in countries with national, legally binding policies preventing IUU industrial or large-scale freshwater fishing

Historical Data Methodology and Challenges:

We collected the data from FAOLEX (the interactive online database of the Legal Office of the Food and Agriculture Organization of the United Nations) by using the Advanced Search feature. We activated the "Fisheries and Aquaculture" field for the Domain and Subject filter, and then used the following search terms: “Freshwater” in the “document search box”; “constitutions,” “policies,” “legislations and regulations” in the “type of text” box; and "fishing authorization, authorization/permit, total allowable catch, enforcement and compliance, and illegal, unreported and unregulated fishing [IUU])” in the “keywords” box. We also excluded repealed (inactive) records. This search yielded nearly 900 results. Because FAOLEX does not report the number of countries represented in the dataset, we consolidated all states and territories in the raw data into their corresponding sovereign countries.

Illegal, unreported and unregulated (IUU) fishing places significant pressure on the world’s fisheries, threatening our ability to safely manage resources by fishing in violation of laws, failing to report or misreport catches, and exploiting stocks with no management measures in place.

While the exact toll of IUU fishing on freshwater ecosystems is unknown, in marine ecosystems these activities can cost developing nations billions of U.S. dollars in annual economic losses. Weak fisheries governance and IUU fishing have contributed to declines in biologically sustainable fishing practices and overexploitation of marine fish stocks. One in every five fish caught in marine and coastal ecosystems around the world every year is thought to originate from IUU fishing.

Beyond ecological impacts, IUU fishing has cascading effects on people and ecosystems alike, disrupting food webs and exacerbating food insecurity, increasing zoonotic disease outbreaks and harming nontarget species such as marine and coastal mammals and birds. These risks are particularly acute in freshwater fisheries, which support the diets and livelihoods of millions of people but are often characterized by limited monitoring, fragmented governance and weak enforcement.

Legally binding national policies are needed that establish clear rules, monitoring obligations and enforcement mechanisms to deter illegal fishing and reduce incentives for noncompliance. Without such frameworks, detection and enforcement will likely remain inconsistent, particularly in freshwater systems where monitoring capacity is often limited.

To assess national progress in addressing these risks, this analysis draws on a newly compiled dataset of national‑level, legally binding policies from FAOLEX (the database of the Legal Office of the Food and Agriculture Organization of the United Nations) that explicitly aim at preventing IUU fishing in inland and freshwater fisheries, including regulations governing industrial and large‑scale operations. As of 2024, 82% of the world’s population lives in countries with national-level legally binding policies that prevent IUU industrial or large-scale freshwater fishing, up from 21% in 2000.

This increase reflects growing recognition of the need for enforceable legal frameworks to prevent overexploitation of freshwater species. However, the existence of legally binding policies does not guarantee effective enforcement or reduced IUU fishing, particularly in freshwater systems where monitoring and management and governance capacity remain limited.

7650: 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’s 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 that 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. Another key limitation of relying on this data is that these three forms of corruption may all influence the freshwater sector, but the data does not specifically measure corruption within the freshwater sector. Rather, this data assesses overall government corruption, which can vary among sectors within the same country. Countries that scored over >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.

Protecting freshwater ecosystems depends not only on governments strengthening conservation policies but also on their willingness to act with integrity and apply the rule of law consistently, including to those with political and economic power. Yet in many countries, corruption poses a threat to these efforts, fueling illegal activities that negatively impact wild populations of freshwater species by undermining regulatory frameworks and facilitating overharvesting.

Abuses of power for private gain can occur across all levels of government. Corruption, for example, can take a variety of forms, from public officials participating in high-profile fraud, embezzlement and laundering schemes to police officers collaborating with illegal fisheries, collecting or paying bribes or extorting local businesses. In some cases, corrupt interests can become so deeply ingrained within governments that they can influence environmental policies that would legally sanction actions harming freshwater ecosystems in inland fisheries.

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.

7646: National implementation of CITES, as measured by the share of Parties meeting requirements for effective implementation of the Convention on International Trade in Endangered Species

Historical Data Methodology and Challenges:

The data for this indicator represents CITES Parties with legislation in Category 1, that is, “legislation that is believed generally to meet all four requirements for effective implementation of CITES.” It is sourced from Status of Legislative Progress for Implementing CITES. Using the number of countries with Category 1 status is a helpful indicator of progress toward increasing commitments to combat the overexploitation of wild species.

The Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) is the primary international agreement on global wildlife trade, working to help ensure the sustainable use of species.

CITES protects biodiversity by subjecting the trade of certain species to international controls, including permits. Analyses of CITES trade data reveal important insights into species composition, abundance and threat levels of traded animals. However, only 27 inland fish taxa are currently included in these protections, among them sturgeon, European eel and the Mekong giant catfish. CITES includes a database that tracks the development and implementation of legislation for countries working to meet their obligations under CITES.

In addition, CITES can recommend that countries suspend trade in particular species. Noncompliant countries are given the opportunity to adequately reform their policy. The number of Parties listed in noncompliance can therefore be used as an indicator of international efforts to combat the unsustainable trade in biodiversity.

The number of Parties to CITES significantly increased from 4 in 1974 to 184 as of 2021. However, as of June 2026, only 69% of Parties met the requirements for effective implementation of CITES, up from 64% in 2023. Thirty-four countries currently have recommendations to suspend trade. All Parties must ensure compliance to address species overexploitation.

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.

Restore freshwater ecosystems

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.

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.