Human-driven overexploitation of wild species — including legal and illegal logging, hunting and trade — is a major driver of biodiversity loss and species extinction. Reversing this trend requires better monitoring of wild populations, stronger protection of threatened species, sustainable management of species use and effective regulation of wildlife trade.

Our planet is in the middle of a mass extinction event. Unlike past mass extinctions triggered by natural events such as volcanic eruptions or asteroid impacts, this one is driven by humans.
 

Overexploitation and wildlife trade are major drivers of species extinction

Overexploitation of wild species is a primary driver of species loss, directly putting 26.6% of all assessed species at risk of extinction. Overexploitation occurs when resources are used faster than they can be replaced. Major drivers of legal and illegal overexploitation of terrestrial species include logging, hunting for consumption or trophies, and harvesting species for the illegal wildlife trade. Uses also include consuming species for food, traditional medicine and luxury goods.
 

Wildlife populations and threatened species are declining

From 1970 to 2020, wildlife populations shrunk in size by 73%. Iconic species like the African elephant, pangolins and medicinal plants are all threatened with extinction by humans.

On top of directly and indirectly causing biodiversity loss and compromising ecosystem function, overexploitation also puts human health at risk. When more people come in direct contact with wild species and poachers, local sellers and consumers incorrectly handle sick animals or infected wild products. This leads to a higher risk of zoonotic infections such as hantavirus, rabies or avian influenza (bird flu). Overexploitation can also exacerbate other environmental problems, such as increasing the risk of invasive alien species on land through the transport of nonnative species into new ecosystems.
 

Legal and illegal wildlife trade remain inadequately regulated

International agreements such as the Convention on International Trade in Endangered Species of Wild Fauna and Flora aim to ensure that the use and trade of wild species is regulated and does not threaten their survival. However, despite current efforts to regulate the sustainable use of species, protect their habitats and monitor their health, current efforts remain critically off track to stop the overexploitation of terrestrial species.
 

What it will take to halt overexploitation and ensure sustainable use

Halting overexploitation and allowing threatened species to recover will require efforts to better monitor species’ populations, protect them in their natural habitats, and manage the use of species and ecosystems in a way that does not threaten their survival. This will require addressing the social, economic and regulatory barriers currently preventing sustainable use.

Tracking progress on global outcomes

11887: Extinction risk for overexploited terrestrial species, as measured by the number of terrestrial species threatened with biological resource use on the IUCN Red List

Status: Wrong Direction
Historical Data Methodology and Challenges:

The data reported for this indicator is sourced from the IUCN Red List of Threatened Species. The database is filtered to include all species within the following Red List Categories: “Critically Endangered,” “Endangered,” and “Vulnerable,” and are in the “Terrestrial” system. Specifically, the dataset focuses on species threatened with extinction 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.

Target Methodology:

Reducing extinction risk for overexploited terrestrial species is particularly relevant for minimizing biodiversity loss. Díaz et al. 2020 set a “high ambition” target of reducing extinction risks for 20% of threatened species by 2030 and for 50% of species by 2050, as well as a “very high ambition” target of reducing extinction risks for more than 50% of threatened species by 2030 and for all species by 2050. But these targets are neither specific to terrestrial species nor to specific threat types (e.g., biological resource use), and they also do not specify by how much extinction risks are reduced. Consequently, we cannot use them as a basis for establishing a quantitative, timebound target for reducing extinction risks for overexploited terrestrial species threatened specifically by biological resource use. Instead, we can only indicate the direction of change required — that the extinction risk for overexploited terrestrial species must decline — as informed by Díaz et al. 2020.

Progress Assessment Methodology:

Outcome indicators in this system experience high interannual variability in historical data due to both anthropogenic and natural causes. To account for this variability, 10 years rather than 5 years are used to calculate the linear trendline where possible. With an increasing rate of threatened species, this indicator is moving in the wrong direction.

An estimated 1 million species are threatened with extinction, many of which could disappear in the next few decades. Overexploitation — when resources are used, either directly or indirectly, at a faster rate than they can be replaced — is a major driver of population declines and species’ extinction risk. Extreme use by humans, like that of species coveted for the illegal wildlife trade, has driven declines in population sizes by 62% where trade occurs.

Tracking the extinction risk for overexploited terrestrial species, as measured by the number of species threatened with “biological resource use” on the International Union for the Conservation of Nature (IUCN) Red List, provides a useful estimate of unsustainable human activity. As defined by the IUCN Red List, biological resource use includes activities like hunting, gathering, logging and fishing. This includes the direct use from harvesting (such as poaching), the by-product of an action (e.g., accidental catch of other species and the intentional killing for control (e.g., pest management). Species listed under this designation may be used by humans sustainably or unsustainably. Therefore for this indicator, terrestrial species considered “overexploited” are those threatened with extinction and that have biological resource use listed as a threat contributing to their decline.

Using these parameters, the total number of terrestrial species threatened by overexploitation has steadily increased over time. In 2016, 3,400 species were threatened with extinction from overexploitation; in 2025, that number reached roughly 19,000. In total, approximately 14% of species assessed for the IUCN Red List are threatened by overexploitation. Given that over 84,000 species have yet to be assessed by the IUCN Red List to reach its goal of assessing at least 260,000 species, the total number of overexploited species is likely underestimated.

The extinction risk for threatened species needs to be reduced by at least 20% by 2030 and by 50% by 2050. While this target is for all species threatened with extinction — not just those specifically threatened by overexploitation — we can apply similar goals. Current trends indicate that efforts to stop overexploitation are not only falling short but heading in the wrong direction.

The drivers of overexploitation are both difficult to address and present in every ecosystem. Complex ecological, social, financial and regulatory barriers prevent effective monitoring and regulation, leading to unsustainable use and, ultimately, extinction.

11864: Illegal wildlife trade, as measured by total illegal wildlife trade incidents for terrestrial species

Status: Wrong Direction
Historical Data Methodology and Challenges:

Data was downloaded from the TRAFFIC Wildlife Trade Portal by selecting “all species” and across “all types of incidents.”

The portal contains only a selection of wildlife trade data managed by TRAFFIC. Some records — and certain data fields — have been simplified or removed for public use. Data is presented cumulatively over the years.

Target Methodology:

Reducing overexploitation of wild terrestrial species in an effort to reduce extinction risks for these species is particularly relevant for minimizing biodiversity loss. Díaz et al. 2020 set a “high ambition” target of reducing extinction risks for 20% of threatened species by 2030 and for 50% of species by 2050, as well as a “very high ambition” target of reducing extinction risks for more than 50% of threatened species by 2030 and for all species by 2050. But these targets are not specific to terrestrial species, wild terrestrial species, nor to specific threat types (e.g., biological resource use), and they also do not specify by how much extinction risks are reduced. Consequently, we cannot use them as a basis for establishing a quantitative, timebound target for reducing the overexploitation of wild terrestrial species. Instead, we can only indicate the direction of change required — that the overexploitation of wild terrestrial species must decline — as informed by Díaz et al. 2020.

Progress Assessment Methodology:

Outcome indicators in this system experience high interannual variability in historical data due to both anthropogenic and natural causes. To account for this variability, 10 years rather than 5 years are used to calculate the linear trendline where possible. The cumulative number of recorded illegal wildlife trade incidents grew by about 2,700 incidents per year from 2016 to 2025, signaling that this indicator continues to move in the wrong direction.

From ivory carvings to exotic pets and ingredients used for medicine and cosmetics, wildlife products and live organisms fuel a global trade — through both legal and illegal means — that often overexploits species.

Wildlife crime has become one of the largest and most profitable criminal activities, with the black market for illegal wildlife products valued at around $20 billion a year. Much of this trade is driven by demand for fashion, exotic pets, traditional medicine, wild food and adornments. Combating the illegal wildlife trade — including decreasing demand for products and preventing the transport of wild species — is critical to reducing overexploitation.

Around 2,211 assessed species are threatened by international trade. While some species are protected by international agreements like the Convention on International Trade in Endangered Species of Wild Fauna and Flora, the use of many populations remains unregulated or unsustainable.

Databases such as TRAFFIC’s Wildlife Trade Portal are useful to help monitor the illegal trade of species, which can be used as a proxy for overexploitation. The database shows wildlife incident data (e.g., seizures and poaching) collected from public, open source data, such as government reports or law enforcement records. While current incident data are not necessarily a direct measure of the full wildlife trade, as the number of recorded incidents can increase with improved tracking, enforcement or regulation, it demonstrates some of the illegal uses of species by humans.

TRAFFIC’s Wildlife Trade Portal shows that illegal trade of species has been increasing, the cumulative number of recorded incidents rose from approximately 16,000 in 2016 to approximately 39,000 in 2025, an average increase of about 2,700 per year. Comprehensive monitoring of the illegal wildlife trade, especially for threatened terrestrial species, is critical for understanding where and why they face overexploitation.

Key enablers and barriers to change

12852: Wildlife crime enforcement

Wildlife crime — including illegal poaching, injuring, killing or trading species — has grown significantly over time. The illegal wildlife trade is now one of the most lucrative illegal industries in the world, worth an estimated $20 billion a year as of 2023. While some activities to illegally take species are opportunistic, most are run by organized crime. Illegal wildlife trade is also increasingly converging with other illicit markets, including human trafficking and drug trafficking, exacerbating and complicating the problem.

Law enforcement is a primary deterrent to wildlife crime and the overuse of terrestrial species. Enforcement and monitoring by legal entities or local communities can help reduce the poaching of certain species. However, enforcement must be carefully designed to account for unintended consequences. If poorly designed, enforcement can drive up prices for hard-to-get products and increase the involvement of organized crime that has learned how to operate in high enforcement areas.

As a result, effective enforcement and avoiding unintended consequences require sufficient resources to cover personnel, training, equipment and additional costs. These efforts should likely be paired with other interventions, such as demand-reduction programs or cross-border coordination among enforcement agencies. For illegal trade to be profitable, criminals must bypass domestic laws, regulations and enforcement actions, which means that corruption is often necessary for its success. Therefore, both agents and government systems must be free from corruption to effectively combat wildlife crime.

While there is no available data, the International Consortium on Combating Wildlife Crime (ICCWC) sets a broad goal of increasing detection, disruption and detention of wildlife criminals by 2030. It outlines 10 measures of success, including the number of criminal networks disrupted through ICCWC-supported initiatives and the number of countries with improved capacity to conduct specialized investigative techniques such as financial investigations.

12853: Lower levels of corruption, as measured by the share of countries with biodiversity hotspots 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 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 land sector, but the data does not specifically measure corruption within the land sector. Rather, this data assesses overall government corruption, which can vary among sectors within the same country.

Countries that scored 0.6 or above 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 through expert judgment by Systems Change Lab and WJP researchers. For this indicator, only countries with biodiversity hotspots are included.

Data is available beginning in 2012. However, the number of countries included in each year varies: 97 countries (73 with biodiversity hotspots) in 2012 and 2013, 99 countries (75 with biodiversity hotspots) in 2014, 102 countries (78 with biodiversity hotspots) in 2015, 113 countries (86 with biodiversity hotspots) in 2016-2018, 126 countries (95 with biodiversity hotspots) in 2019, 128 countries (95 with biodiversity hotspots) in 2020, 139 countries (100 with biodiversity hotspots) in 2021, 140 countries (100 with biodiversity hotspots) in 2022, 142 countries (101 with biodiversity hotspots) in 2023 and 2024, and 143 countries (101 with biodiversity hotspots) in 2025. To maintain a more consistent country sample, Systems Change Lab presents data from 2021 onward. The numerator reflects the number of countries that scored 0.6 or above while the denominator includes all countries with scores in a given year.

Effectively halting the overexploitation of species depends on not only governments’ strengthening national policies, laws and regulations to protect terrestrial ecosystems but also their willingness to act with integrity and apply these policies consistently — including to those with political and economic power. Yet in many countries, corruption facilitates illegal activities that drive overexploitation and the illegal wildlife trade.

According to the World Justice Project Rule of Law Index, as of 2025, government corruption was relatively low in roughly 36% of countries with biodiversity hotspots, a figure that has remained fairly stable in recent years. However, in Bolivia, Indonesia and the Democratic Republic of the Congo (DRC) — three countries known for their high levels of terrestrial biodiversity — corruption remains a challenge. The DRC and Bolivia received the fourth- and sixth-lowest scores, respectively; while Indonesia fared better, it still ranked in the bottom half, scoring well below the threshold used to determine lower levels of corruption within a country’s government.

12848: 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.

The unsustainable trade in terrestrial species is a significant threat to biodiversity that affects almost all major taxonomic groups. The wildlife trade is driving extinction, with around 24% of terrestrial vertebrates facing threats from it. Some of this trade is illegal, and some is legal.

The Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) aims to ensure that international trade in wild species does not threaten their survival. CITES protects biodiversity by subjecting the trade in certain species to international controls. For example, Appendix I of the agreement prohibits trade in species threatened with extinction unless exceptional circumstances apply.

CITES supports a database that tracks the development and implementation of legislation for Parties working to meet their obligations under the agreement. Countries with legislation listed as Category 1 meet all the requirements for effective implementation of the agreement. If Parties fall short of the requirements, CITES can subject them to a recommendation to suspend trade; this means a recommendation that other member countries refuse to authorize trade in CITES-listed specimens with the noncompliant Party. Noncompliant countries are given the opportunity to adequately address the recommendation and become compliant. As a result, the overall status of compliant Parties can be used as an indicator of international and national efforts to combat the unsustainable use of terrestrial species.

The number of Parties to CITES rose from 10 when it entered into force in 1975 to 185 Parties as of 2026. However, as of 2026, only 69% of Parties met the requirements for effective implementation of CITES (Category 1), and 34 countries had recommendations to suspend trade. To address the overexploitation of species, all Parties must be in compliance.

12855: Effective management of exploited species, as measured by exploited species populations managed through permitting systems or management guidelines

Unsustainable use threatens biodiversity and affects many major groups of species. The wildlife trade is a driving force of species extinction, threatening around 24% of terrestrial vertebrates. In addition to illegal wildlife trade, the underregulated trade in live species or their products also puts pressure on wild populations.

Ensuring that exploited species populations are managed through permitting systems or management guidelines can reduce their extinction risk. Permitting systems set formal frameworks to regulate how wild species or their products can be used, whereas management guidelines provide recommendations and best practices for managing species. In tandem, these mechanisms help support the sustainable use of wild terrestrial populations. However, there is currently no data tracking the proportion of species populations managed through these approaches.

12856: Locally led management of overexploited species, as measured by the share of management plans with documented leadership or co-leadership of Indigenous Peoples or local communities

Many lands held by Indigenous Peoples and local communities (IPLCs) are incredibly biodiverse and well managed. Around 36% of intact forests and 80% of the world’s biodiversity are found on Indigenous lands, encompassing many Key Biodiversity Areas. Evidence shows that these lands are sustainably managed and experience lower deforestation rates than unprotected areas.

To be effective, efforts to halt the overexploitation of terrestrial species must include IPLCs as leaders or coleaders. In part, this can be advanced by including Indigenous knowledge into biodiversity assessments and management plans. Management plans, focused on sustainable resource use and led by IPLCs, can substantially improve conservation initiatives and safeguard biodiversity. However, it is not enough to integrate Indigenous knowledge in the creation of management plans; IPLCs must have the opportunity to lead the sustainable management of natural resources.

It is therefore critical to track management plans with leadership or coleadership of IPLCs globally. However, there is no central data repository tracking the share of management plans with documented coleadership of Indigenous Peoples and/or local communities.

12847: Countries included in at least one wild meat consumption study

Wild meat plays a critical role in food security and local livelihoods, providing an important source of nutrients and additional income for local communities. In developing countries across Latin America, Africa and Asia, an estimated 150 million households harvest wild meat. These households are primarily low-income and often use wild meat as a key part of their diets. While the exact number of species used for wild meat is unknown, estimates range from several hundred to 2,000.

Global trends indicate that growing human populations, advances in technology and access to markets are some of the factors driving increased demand for wild meat. In Peru, for example, wild meat sales increased in parallel with population growth between 1973 and 2018, although the overall contribution of wild meat to diet remained steady. However, meat selection is often concentrated on a small number of preferred species, increasing pressure on specific populations. For example, only five species of ungulates and rodents accounted for 88.5% of the biomass traded in Peru.

Monitoring wild meat consumption is essential for promoting sustainable use of wildlife and ensuring that levels of take do not exceed the capacity of local populations. Without this knowledge, species may be exploited to critical levels without detection, especially in regions where biodiversity is high and data is sparse. By tracking where species are being hunted, in what quantities and under what circumstances, we can understand the demand for these types of wildlife products, inform evidence-based policies and create regulations that balance human needs with conservation.

There is currently no comprehensive global dataset that tracks wild meat use and consumption. A related effort from WILDMEAT.org tracks the use of wild meat, as measured by hunting offtakes, consumption and market sales. Its database includes 31 consumption studies since 2000, assessing wild meat across Cameroon, the Central African Republic, the Democratic Republic of the Congo, Equatorial Guinea, Gabon, Indonesia, Laos and the Republic of the Congo. The data is currently limited to these countries, and additional work is needed to track the take and consumption of wild meat worldwide.

12854: 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.

Environmental issues and poverty are linked challenges, with some evidence suggesting that poverty can drive environmental degradation. Poverty and economic inequality have been linked to the persistence of illegal hunting, as communities with insufficient income streams or other economic opportunities may depend on wildlife resources for subsistence or income. Addressing the overexploitation of terrestrial natural resources therefore requires efforts to reduce poverty and expand economic opportunities. This is particularly important in biodiversity hotspots, where a greater number of species are at risk of overexploitation.

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.

12842: Household demand for wildlife products

Overexploitation of wild terrestrial species means addressing both supply and demand. For supply, interventions often include top-down regulations and their enforcement. However, even with these mechanisms in place, local demand for illegal products continues to contribute to overexploitation. Efforts to halt the overexploitation of terrestrial species must therefore also include drivers of household demand for wildlife products, as consumption decisions are often based on income, location, and access to alternatives.

Most efforts to decrease household demand focus on individual species, particularly mammals, and the drivers of their consumption. Researchers have classified the demand for wildlife products in five categories: experiential (e.g., recreational use like fishing), social (e.g., reputation like trophy hunting), functional (e.g., medicine), financial (e.g., profit) and spiritual (e.g., ritualistic). These demands are rooted in cultural, social and financial pressures, and interventions must shift how households view — and consequently use — wild threatened species.

Such interventions should also consider the complex dependencies of local communities on terrestrial species, as many households rely on local wildlife for food or income. Sustainable alternatives are needed to replace the use of threatened or unsustainably used species, especially for communities that are a key entry point for intervention. Examples might include community-based livestock rearing, aquaculture or ecotourism.

Through demand-reduction activities, such as raising awareness of a species’ conservation status, and availability of sustainable alternative livelihoods, household demand for wildlife products can be reduced, thereby decreasing overexploitation. However, key gaps remain in understanding the effectiveness of such initiatives — not because efforts to reduce demand are unsuccessful, but because broad methods to track and reduce demand are infrequently reported or monitored over the long term. In addition to tracking broad demand, it is necessary to evaluate demand-reduction campaigns and better understand their effectiveness.

12851: Corporations reporting on biodiversity

Historical Data Methodology and Challenges:

The data for this indicator represents the share of 4,581 assessed companies that reported on biodiversity, sourced from “The move to mandatory reporting,” KPMG Survey of Sustainability Reporting 2024. The list of N100 companies is a worldwide sample of 5,800 companies comprising the top 100 companies in 58 countries, territories and jurisdictions. For the share reported here the base is 4,581 N100 that report on sustainability and ESG matters.

Many private businesses operate supply chains that directly or indirectly drive the overexploitation of species on land through logging, agricultural expansion and the sourcing of raw materials from ecosystems under pressure. Construction, agriculture and food and beverages are the largest sectors dependent on healthy ecosystems and biodiversity, with $44 trillion of economic value moderately or highly dependent on nature. Despite this dependence on wild species, businesses are often left out when developing targets to stop overexploitation and halt the loss of biodiversity.

Before companies can set meaningful commitments to reduce their impact on species, they first need to understand where and how their operations contribute to overexploitation. Setting standards for reporting on biodiversity is a critical first step toward such understanding. The Global Reporting Initiative (GRI) Biodiversity Standard is a subset of broader GRI standards that aim to help companies understand their impact on the economy, environment and people. The updated standards require that companies disclose their most significant biodiversity impacts across their value chains, including reporting on the direct drivers of biodiversity loss like overexploitation, climate change, land use and pollution.

GRI does not disclose the list or specific number of companies and financial institutions reporting on biodiversity, or their specific progress. However, as of 2024, KPMG reported that 49% of the 4,581 largest companies in the world were reporting on biodiversity.

Tracking corporate disclosure on biodiversity is essential to halting terrestrial overexploitation because it creates the foundation for accountability. When companies publicly report their biodiversity impacts, it enables investors, regulators and civil society to evaluate whether business practices are contributing to unsustainable levels of use. Without disclosure, the role of the private sector in driving overexploitation remains opaque and commitments to sustainable use lack the evidence base needed to measure progress.

12850: Terrestrial wild species population monitoring, as measured by the share of terrestrial species with recent, adequate population data

An estimated 50,000 wild species are used by humans for food, medicine and energy, among other purposes. Some are sustainably used, but overexploitation remains a primary threat to wild species across terrestrial ecosystems, pushing many toward extinction. For some species good estimates of population trends exist, but many others lack data on their populations and how they are changing over time. Without this information, overexploitation cannot be detected, prevented or reversed. Because depletion can remain invisible until populations collapse, and because decision-makers do not always know which species are overharvested, sustainable use can only be confirmed and managed where established population baselines exist.

New technologies are making it feasible to extend monitoring to the species and places that have previously been missed. Motion-triggered camera traps paired with machine-learning identification, passive acoustic monitoring, environmental DNA sampling, telemetry, artificial intelligence and the integration of satellite imagery are examples of methods that could allow for broad, repeatable measures of population change at lower cost. However, even with improved technologies, comprehensive, continuous baseline monitoring of terrestrial species is still lacking.

Establishing baselines and monitoring the health of terrestrial populations will require scaling affordable sensor networks, sustaining open data infrastructure and standardizing methods for cross-ecosystem comparability. Progress on this indicator means steadily increasing the number of terrestrial species with recent, adequate population data, so that overexploitation can be identified, monitored and addressed before populations disappear. These monitoring efforts could ultimately be combined with data on genetic diversity to ensure that populations are a sufficient size, remain healthy and adapt to environmental changes.

Other shift Other shifts needed to transform the system

Effectively halt deforestation, other forms of conversion, and degradation across terrestrial ecosystems

Not only is land-use change across forests, peatlands, grasslands and coastal wetlands the leading direct driver of terrestrial biodiversity loss, but it also releases substantial emissions and weakens these ecosystems’ ability to sequester carbon.

Restore deforested and degraded terrestrial ecosystems

Restoring deforested and degraded ecosystems — including forests, peatlands, grasslands and coastal wetlands — can help limit global warming and reverse biodiversity loss. Done right, reforestation and other forms of ecosystem restoration can also deliver far-reaching, sustainable development benefits for communities around the world.

Sustainably manage terrestrial ecosystems to reduce GHG emissions and enhance carbon removals

Unsustainable management of terrestrial ecosystems, particularly forests, grasslands, savannas and shrublands, is exacerbating the climate and biodiversity crises. When tailored to local contexts and implemented appropriately, improved management practices can reduce emissions, increase carbon sequestration and bolster climate resilience, all while supporting productivity and local livelihoods.

Sharply reduce pollution in terrestrial ecosystems

Sharply reducing pollution in forests, grasslands, peatlands and coastal wetlands is essential to halt biodiversity loss, maintain ecosystem services and protect human health. Key contaminants include heavy metals, persistent organic pollutants such as PFAS, pesticides, nutrient pollution, plastics and artificial light.