MAAP #22X: AI to detect gold mining deforestation across the Amazon – 2024 update

Intro Image. Amazon Mining Watch interactive map.

As gold prices continue to increase (over 30% during the last 12 months), small-scale gold mining activity has emerged as one of the major deforestation drivers across the Amazon

It often targets remote areas, thus impacting carbon-rich primary forests within protected areas and Indigenous territories. Moreover, in many cases, we presume that this mining is illegal based on its location within conservation areas (such as protected areas and Indigenous territories) and outside mining concessions.

Given the vastness of the Amazon, however, it has been a challenge to accurately monitor mining deforestation across all nine countries of the biome in a timely manner.

In MAAP #212, we presented the initial results of the new AI-based dashboard (known as Amazon Mining Watch) designed to address this issue. AMW is a partnership between Earth Genome, Amazon Conservation, and the Pulitzer Center’s Rainforest Investigations Network.

This online tool (see Intro Image) analyzes satellite imagery archives to estimate annual mining deforestation footprints across the entire Amazon, from 2018 to 2024 (Note 1). Although the data is not designed for precise area measurements, they can be used to give general estimates. The algorithm is based on 10-meter resolution imagery from the European Space Agency’s Sentinel-2 satellite and produces 480-meter resolution pixelated mining deforestation alerts.

By analyzing the annual mining deforestation footprints across years (since 2018), we are able to detect annual trends and estimate the overall cumulative impact. Here, we present an update focused on the newly added 2024 data.

This data reveals that gold mining is actively causing deforestation in all nine countries of the Amazon (see Base Map below). The countries with the highest levels of new gold mining deforestation in 2024 are 1) Brazil, 2) Guyana, 3) Suriname, 4) Venezuela, and 5) Peru.

As a note regarding future steps, the Amazon Mining Watch partnership is currently working to enhance the functionality of the dashboard, to increase the frequency of the information produced (quarterly mining alerts), and facilitate the production of targeted, high-quality reports on key monitoring areas anywhere in the Amazon. The AMW will be a one-stop shop platform including real-time visualization of: 1) AI-based detection of mining deforestation across all nine Amazonian countries; 2) Hotspots of urgent mining cases, including river-based mining; and 3) the socio-environmental costs of illegal gold mining with the Conservation Strategy Fund (CSF) Mining Impacts Calculator.

Base Map. Mining deforestation footprints, 2018-2024. Data: AMW, Amazon Conservation/MAAP.

MAJOR FINDINGS

Amazon & National Scale Patterns

The Base Map below presents the gold mining footprint across the Amazon, as detected by the AMW algorithm. This data serves as our estimate of gold mining deforestation.

Yellow indicates the accumulated mining deforestation footprint for the years 2018- 2023; that is, all areas that the algorithm classified as a mining site vs other types of terrain, such as forest or agriculture. Red indicates the new mining areas detected in 2024.

Three major Amazon gold mining regions stand out: southeast Brazil (between the Tapajos, Xingu, and Tocantis Rivers), Guyana Shield (Venezuela, Guyana, Suriname, and French Guiana), and southern Peru (Madre de Dios).

 

 

 

 

Graph 1. Amazon mining deforestation footprint. Data: AMW

Graph 1 quantifies the spatial data detected by the AMW algorithm

The cumulative mining deforestation footprint in 2024 was 2.02 million hectares (4.99 million acres)

For context, the initial mining deforestation footprint was around 970,000 hectares in 2018, the first year of Amazon Mining Watch data.

Between 2019 and 2024, we estimate that the gold mining deforestation grew by 1.06 million hectares (2.61 million acres).

Thus, over half (52.3%) of the cumulative footprint has occurred in just the past six years.

 

 

 

 

Graph 2 shows that, of the total accumulated mining (2.02 million hectares), over half has occurred in Brazil (55.3%), followed by Guyana (15.4%), Suriname (12.4%), Venezuela (7.3%), and Peru (7.0%).

Graph 2. Gold mining deforestation across the Amazon, by country. Data: AMW, Amazon Conservation/MAAP

Graph 3 digs deeper into the AMW data, revealing additional trends between years. This data highlights the annual changes in detected mining deforestation. Note the trend across the entire Amazon at the top in green for overall context, followed by each country. Note that Brazil (orange line) accounts for much of the annual mining (over 50%).

In 2024, we documented the new gold mining deforestation of 111,603 hectares (275,777 acres). This total represents a decrease of 35% relative to the previous year 2023 and 45% relative to the peak year 2022.

The countries with the highest levels of new gold mining deforestation in 2024 were 1) Brazil (57,240 ha), 2) Guyana (19,372 ha), 3) Suriname (15,323 ha), 4) Venezuela (9,531 ha), and 5) Peru (6,020 ha). However, all five of these countries saw a major decrease in 2024, between 33% (Brazil and Suriname) and 46% (Peru).

Graph 3. Annual changes in new mining deforestation. Data: AMW
Figure 1. Protected areas & Indigenous territories impacted by mining deforestation. Data: AMW, ACA/MAAP.

Protected Areas & Indigenous Territories

We estimate that 36% of the accumulated mining deforestation in 2024 (over 725,000 hectares) occurred within protected areas and Indigenous territories (Figure 1; Note 2), where much of it is likely illegal.

Notably, the vast majority of this overall mining deforestation in protected areas and Indigenous territories has occurred in Brazil (88%).

 

 

 

 

 

 

 

 

 

Figure 2a. Top 10 impacted protected areas & Indigenous territories. Data: AMW, ACA/MAAP.

Figure 2a illustrates the top ten for both protected areas and Indigenous territories, in terms of both accumulated mining deforestation footprint and new mining deforestation in 2024. Figures 2b-d show zooms of the three main mining areas: southeast Brazil (2b), Guyana Shield (2c), and southern Peru (2d).

The top nine most impacted protected areas (in terms of accumulated footprint) are all in Brazil, led by Tapajós Environmental Protection Area. This area has lost over 377,000 hectares, followed by Amanã and Crepori National Forests, Rio Novo National Park, Urupadi, Jamanxim, and Itaituba National Forests, Jamanxim National Park, and Altamira National Forest. The top ten is rounded out by Yapacana National Park in Venezuela.

The three most impacted Indigenous territories are also in Brazil: Kayapó, Mundurucu, and Yanomami. Together, these three territories had a mining footprint of nearly 120,000 hectares. Fourth on the list is Ikabaru in Venezuela, followed by three in southern Peru (San Jose de Karene, Barranco Chico, and Kotsimba) with mining impact of over 17,000 hectares. Rounding out the top ten are Sai Cinza and Trincheira/Bacajá in Brazil, and San Jacinto in Peru.

We also estimate the expansion of over 38,000 hectares of new mining deforestation in protected areas and Indigenous territories in 2024. The protected area with the highest levels of new mining deforestation in 2024 was Tapajós Environmental Protection Area (nearly 19,000 hectares), followed by Amanã and Urupadi National Forests in Brazil, Rio Novo and Jamanxim National Parks in Brazil, Crepori National Forest in Brazil, Campos Amazonicos National Park in Brazil, Yapacan National Park in Venezuela, Guyane Regional Park in French Guiana, and Brownsberg Nature Reserve in Suriname.

Finally, the Indigenous territory with the highest levels of new mining deforestation in 2024 was Kayapó in Brazil (over 2,100 hectares), followed by Ikabaru in Venezuela, Yanomami, Aripuana, and Mundurucu in Brazil, Baramita in Guyana, Kuruáya in Brazil, Isseneru and Kamarang Keng, San Jose de Karene in Peu. It is worth noting that Kayapó, Mundurucu, and Yanomami territories in Brazil all experienced declines in the mining deforestation rate in 2024. For example, Yanomami went from its peak in 2021 to the lowest on record in 2024.

Most impacted areas in eastern Brazilian Amazon

Figure 2b. Most impacted areas in eastern Brazilian Amazon. Data: AMW, Amazon Conservation/MAAP.

Most impacted areas in the Guyana Shield

Figure 2c. Most impacted areas in the Guyana Shield. Data: AMW, Amazon Conservation/MAAP.

Most impacted areas in the southern Peruvian Amazon

Figure 2d. Most impacted areas in the southern Peruvian Amazon. Data: AMW, Amazon Conservation/MAAP.

Conclusion & Policy Implications

Despite a recent downward trend in mining across the region, small-scale mining continues to be a major driver of deforestation and ecosystem degradation in the Amazon.

Our analysis shows that over one-third of this mining occurs within protected areas and Indigenous territories, the vast majority in Brazil. However, since the return of the Lula administration in 2023, Brazil has been ramping up enforcement efforts. This has contributed to the rapid decrease in area lost to mining across the Amazon, given Brazil’s outsized contribution to regional figures. This highlights again the importance of protected areas and Indigenous territories as a crucial policy instrument for the protection of the region’s ecosystems.

Although advances have been made in reducing illegal mining from protected areas in southern Peru, it continues to impact several Indigenous territories (MAAP #208, MAAP #196), particularly those surrounding the government-designated Mining Corridor. In fact, the most affected Indigenous territory in Peru, San Jose de Karene, has already lost over a third of its total area to illegal gold mining.  These territories are part of a regional organization known as FENAMAD, which has been supporting legal actions to help the government make decisions for a rapid response to illicit activities (such as illegal mining) that affect indigenous territories. This process led to the execution of five government-led operations between 2022 and 2024, in three communities: Barranco Chico, Kotsimba and San José de Karene (MAAP #208).

In Ecuador, mining deforestation continues to threaten numerous sites, including protected areas and Indigenous territories, along the Andes-Amazon transition zone (MAAP #206, MAAP #221, MAAP #219). An upcoming series of reports will detail these threats.

AMW is an emerging and powerful new tool, but it does have some caveats. One is that any mining activity less than 500 square meters may not be accurately detected. For example, we have been monitoring small-scale mining in several protected areas, such as Madidi National Park in Bolivia and Puinawai National Park in Colombia, that are not yet detected by the algorithm. In these cases, direct real-time monitoring with satellites is still needed. These areas will soon be added to the AMW as mining “Hotspots” (MAAP#197).

This is also the case for river-based mining that does not cause a large footprint on the ground. Imagery with very high resolution has revealed active river barge mining in northern Peru (MAAP #189) and along the Colombia/Brazil border (MAAP#197). These areas will also soon be added to the AMW as mining “Hotspots”.

As effective as enforcement might be, it will have to compete in 2025 with an activity that is more lucrative than ever, with the price of gold now over 3,000 US$ an ounce, driven by global economic uncertainty. While the threat has receded, it is likely to roar back in at the first opportunity or sign that enforcement is lowering its guard. Tools such as the Amazon Mining Watch, which will eventually publish quarterly updates of newly detected mining deforestation areas, can help governments and local community defenders alike to spot new fronts of gold mining and take action as fast as possible, as well as to valuate socio environmental damages to assess the required (financial) efforts to restore damages caused by illegal mining.

The only tool of this kind to be truly regional in coverage, the AMW can also help foster regional cooperation, in particular in transfrontier areas where a lack of interoperability between official monitoring systems might hamper interventions that are aimed at combating a phenomenon that is linked to other nature crimes and is mostly controlled by international organized crime. 

In the coming years, the MAAP and AMW teams will continue to publish both quarterly and annual reports of the dynamic mining situation in each country and across the Amazon.

Notes

1. Note that in this report, we focus on mining activity that causes deforestation. The vast majority is artisanal or small-scale gold mining, but other mining activities have also been detected, such as iron, aluminum, and nickel mines in Brazil and Colombia. Additional critical gold mining areas in rivers that are not yet causing deforestation (such as in northern Peru, southeast Colombia, and northwest Brazil; see MAAP #197), are not included in this report. This information is not yet displayed in Amazon Mining Watch, but future updates will include river-based mining hotspots. 

2. Our data source for protected areas and Indigenous territories is from RAISG (Amazon Network of Georeferenced Socio-Environmental Information), a consortium of civil society organizations in the Amazon countries. This source (accessed in December 2024) contains spatial data for 5,943 protected areas and Indigenous territories, covering 414.9 million hectares across the Amazon.

Acknowledgments

This report was made possible by the generous support of the Gordon and Betty Moore Foundation.

We thanks colleagues from partner organizations around the Amazon for helpful comments on the report, including: Earth Genome, Conservación Amazónica (ACCA & ACEAA) & Federación Nativa del Río Madre de Dios y Afluentes (FENAMAD), Fundación EcoCiencia, Fundación para la Conservación y el Desarrollo Sostenible (FCDS), and Instituto Centro de Vida (ICV) & Instituto Socioambiental (ISA).

This report was made possible by the generous support of the Gordon and Betty Moore Foundation.

MAAP #224: Illegal Deforestation in the Colombian Amazon – Chiribiquete National Park & Llanos del Yarí – Yaguará II Indigenous Reserve

Graph 1. Deforestation in the Colombian Amazon, 2013-2024. Data: IDEAM, UMD/GFW

The Colombian Environment Ministry recently announced that, after the country experienced its lowest deforestation in over 20 years in 2023, forest clearing rose 35% in 2024 (Graph 1). In addition, the Ministry reported an increase in medium-sized clearing, indicating relatively organized and funded operations (Note 1).

Over the past 10 years, 60% of the national deforestation has occurred in the Colombian Amazon. As Graph 1 indicates, there was a large increase in 2017 following the peace accords with the guerrilla group FARC, and a subsequent decrease in 2022 and 2023 (Note 2). Initial estimates indicate an increase for 2024 (Note 3). Overall, there have been nearly 1,200,000 hectares of deforestation across the Colombian Amazon over the past 10 years.

Much of the clearing in the Colombian Amazon is likely illegal (Law of 2021), occurring in national protected areas and Indigenous reserves.

Base Map: Focal area of the report. Data: ACA/MAAP, FCDS.

Here, we highlight recent 2024-25 deforestation in two key areas in the core of the Colombian Amazon: Chiribiquete National Park (Parque Nacional Natural Serranía de Chiribiquete) and the adjacent Llanos del Yarí – Yaguará II Indigenous Reserve (Resguardo Indígena Llanos del Yarí – Yaguará II). See the Base Map for additional context.

These areas are affected by several deforestation pressures, such as the expansion of road infrastructure, extensive livestock farming, pasture expansion, land grabbing, and illicit crops (coca). These pressures often interact, with access roads facilitating livestock farming and pasture expansion, which then facilitates land grabbing.

These drivers have led to the deforestation of over 7,100 hectares in Chiribiquete National Park since its most recent expansion in 2018 (see Annex 1).

Most recently, we estimate the deforestation of 525 hectares in Chiribiquete National Park (concentrated in the northern sector) during 2024-25, plus an additional 856 hectares in Llanos del Yarí – Yaguará II Indigenous Reserve. Note that most of the deforestation follows access roads.

Below, we illustrate the key cases of recent deforestation in both areas, highlighting the role of access roads as facilitators of illegal clearing. These case studies feature satellite images and overflight photos.

Any deforestation in these areas is noteworthy not only due to its impacts on primary forests, biodiversity, and Indigenous groups, but also on carbon reserves. In an upcoming report, we reveal that Chiribiquete National Park is one of the Amazon’s most important and significant carbon sinks.

This report was conducted in collaboration with our Colombian partner Foundation for Conservation and Sustainable Development (Fundación para la Conservación y el Desarrollo Sostenible – FCDS), and with financial support from the Overbrook Foundation.

Illegal Deforestation Cases

Zoom 1. Chiribiquete National Park. Data: ACA/MAAP, FCDS.

Chiribiquete National Park: Sector el Camuya

Zoom 1 shows the deforestation of 198 hectares during 2024 and early 2025 (indicated by red circles), along the Tunia-Ajaju road in the northwest sector of Chiribiquete National Park.

This road extends 45.3 kilometers into the park.

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Photo 1A. Data: FCDS.

In January 2025, FCDS conducted a low-altitude overflight over this sector (see Photos 1A-C).

These photos bring an added level of spatial resolution and perspective, providing greater insight into the cause of the recent deforestation.

Photo 1A highlights deforestation associated with the opening of access roads in the park.

 

 

 

 

 

 

Photo 1B. Data: FCDS.

Photos 1B-C illustrate more clearly the fresh deforestation for expansion of the agricultural frontier.

 

 

 

 

 

 

 

 

 

Photo 1C. Data: FCDS.

 

 

 

 

 

 

 

 

 

 

 

Zoom 2. Chiribiquete National Park. Data: ACA/MAAP, FCDS.

Chiribiquete National Park: Sector El Palmar

Zoom 2 shows the deforestation of 179 hectares during 2024 and early 2025 (indicated by red circles), along the Cachicamo-Tunia road in the northern sector of Chiribiquete National Park.

This road extends 21 kilometers inside the park.

 

 

 

 

 

 

 

 

 

 

Zoom 3. Chiribiquete National Park. Data: ACA/MAAP, FCDS.

Chiribiquete National Park: Sector Norte

Zoom 3 shows the deforestation of 148 hectares during 2024 and early 2025 (indicated by red circles) along or near new access roads in the northeast sector of Chiribiquete National Park.

We estimate the construction of 15.2 kilometers inside the park during this period (also indicated by red circles).

 

 

 

 

 

 

 

 

 

 

Zoom 4. Yarí – Yaguará II Indigenous Reserve. Data: ACA/MAAP, FCDS.

Yarí – Yaguará II Indigenous Reserve 

Zoom 4 shows the major deforestation of 1,070 hectares during 2024 and early 2025 along or near a new illegal road in the northern part of Yarí – Yaguará II Indigenous Reserve.

This road extends 22 kilometers inside the reserve.

 

 

 

 

 

 

 

 

 

 

 

Photo 4D. Data: FCDS.

In January 2025, FCDS conducted a low-altitude overflight over this area, confirming and documenting the new patches of deforestation (see Photos 4D-E).

As noted above, these photos bring an added level of spatial resolution and perspective, providing greater insight into the cause of the recent deforestation.

Both Photos 4D-E indicate the expansion of livestock agricultural activities.

 

 

 

 

 

 

 

Photo 4E. Data: FCDS.

 

 

 

 

 

 

 

 

 

 

 

Policy Implications

The recent deforestation in protected areas and Indigenous territories described above highlights the shortcomings of several current policies of the State of Colombia, which have failed to stem the expansion of cattle ranching and illicit crops as a first step towards land grabbing and permanent deforestation. Several steps could be taken to overcome that failure:

  • Improved coordination between public entities concerned with law enforcement against drivers of deforestation, shortening investigation processes and leading to more effective and comprehensive responses.
  • The inclusion of targets for the reduction of deforestation and the mitigation of impacts on natural forests in agreements for the cessation of hostilities and the de-escalation of the conflict between the national government and armed groups.
  • Monitoring and regulation of public investments for the expansion of livestock farming by local and national governments, to reduce public incentives for deforestation.

Annex 1.

Annex 1. Data: FCDS

Notes

1 Griffin, O (2025) Colombia deforestation rose 35% in 2024, minister says

https://www.reuters.com/business/environment/colombia-deforestation-rose-35-2024-minister-says-2025-02-20/

2 Based on data from Colombia’s Institute of Hydrology, Meteorology and Environmental Studies (Instituto de Hidrología, Meteorología y Estudios Ambientales – IDEAM), a government agency of the Ministry of Environment and Sustainable Development.

3 Based on data from the University of Maryland/Global Forest Watch.

Acknowledgments

This report was conducted in collaboration with our Colombian partner Foundation for Conservation and Sustainable Development (Fundación para la Conservación y el Desarrollo Sostenible – FCDS), and with financial support from the Overbrook Foundation.

MAAP #211: Illegal roads and Deforestation in Indigenous Reserves & National Parks of the Colombian Amazon

Illegal roads are a major threat to the Colombian Amazon, often opening remote primary forests to the main drivers of deforestation: cattle pastures, land grabbing and coca production.

Base Map. Illegal roads causing recent deforestation. Data: MAAP/ACA, FCDS.

These illegal roads threaten protected areas (including national parks) and indigenous territories (known as Resguardos in Colombia).

In 2024, in collaboration with our Colombian partner FCDS, we have documented these impacts in two important areas in the heart of the Colombian Amazon: the Llanos del Yari-Yaguara II Indigenous Reserve and the adjacent Chiribiquete National Park (see Base Map).

Most notably, in the Llanos del Yari-Yaguara II Indigenous Reserve, we see the construction of a new road, causing massive deforestation of primary forests, both within and adjacent to the territory (856 hectares, or 2,115 acres, in total).

In Chiribiquete National Park, we see the expansion of deforestation of 64 hectares (158 acres) along an illegal road penetrating the northwest sector of this important protected area.

Below, we show satellite images for both cases.

Llanos del Yari- Yaguara II Indigenous Reserve

Since March 2023, a new 14-kilometer illegal road has been built in this area, of which 5.3 km is within the northeastern sector of the Llanos del Yari- Yaguara II Indigenous Reserve, located in the department of Guaviare. Figures 1 and 2 show that this construction has caused massive deforestation: 856 hectares (2,115 acres), of which 394 hectares are within the Reserve, between February 2023 (left panel) and March 2024 (right panel). This deforestation is presumably for new cattle pasture, facilitated by the new road. Note that Figure 1 shows the satellite images without markings, while Figure 2 adds markings for the illegal road construction and associated deforestation.

Figure 1. Deforestation along the new illegal road in the Llanos del Yari- Yaguara II Indigenous Reserve, without markings. Data: Planet, NICFI.
Figure 2. Deforestation along the new illegal road in the Llanos del Yari- Yaguara II Indigenous Reserve, with markings. Data: Planet, NICFI.

Chiribiquete National Park

In the adjacent northwest sector of Chiribiquete National Park, deforestation continues to expand along an existing illegal road, known as the Tunia-Ajaju road, located in the department of Caquetá. Figures 3-6 show the deforestation of 64 hectares (56 hectares in zone B and 8 hectares in zone C) along this road inside the national park, between March 2023 (left panel) and March 2024 (panel right). This deforestation is presumably for new cattle pastures, facilitated by the road. Note that Figures 3 and 5 show the satellite images without markings, while Figures 4 and 6 add markings for the illegal road construction and associated deforestation.

Figure 3. Deforestation along the new illegal road in Chiribiquete National Park (zone B), without markings. Data: Planet, NICFI.
Figure 4. Deforestation along the new illegal road in Chiribiquete National Park (zone B), with markings. Data: Planet, NICFI.
Figure 5. Deforestation along the new illegal road in Chiribiquete National Park (zone C), without markings. Data: Planet, NICFI.
Figure 6. Deforestation along the new illegal road in Chiribiquete National Park (zone C), with markings. Data: Planet, NICFI.

Citation

Finer M, Ariñez A (2024) Illegal roads and Deforestation in Indigenous Reserves & National Parks of the Colombian Amazon. MAAP: 211.

 

MAAP #200: State of the Amazon in 2023

The first MAAP report, published in March 2015, took a detailed look at the escalating gold mining deforestation in the Peruvian Amazon.

Figure 1. Most recent cloud-free view of the entire Amazon biome (2023, quarter 3). Data: Planet, NICFI, ACA/MAAP.

The following 198 reports, over the past 8.5 years, continued to examine the most urgent deforestation-related issues across the Amazon.

For our 200th report, we provide our rapid assessment of the current state of the Amazon.

Overall, the situation is dire, with the Amazon nearing two critical deforestation-induced tipping points. The first is the widely feared conversion of moist rainforests to drier savannahs, due to decreased moisture recycling across the Amazon (see MAAP #164). The second is the more newly feared conversion of the Amazon as a critical carbon sink buffering global climate change, to a carbon source fueling it (see MAAP #144).

There is cause for hope, however. It is possible in the long term to protect the core Amazon, as nearly half is now designated as protected areas and indigenous territories, both of which have much lower deforestation rates than surrounding areas (see MAAP #183). Also, new NASA data reveals the Amazon is still home to abundant carbon reserves in these core areas (see MAAP #160 and MAAP #199).

Also on the positive news front, we recently reported a major reduction (over one-half) in primary forest loss between the current year 2023 and last year 2022 across the Amazon, especially in Brazil and Colombia (MAAP #201).

Much is made about Amazon fires in the media, but over the past several years we have revealed that the vast majority of major fires across the Amazon (namely, in Brazil, Bolivia, Peru, and Colombia) are actually burning recently deforested areas (MAAP #168). It is only during intense dry seasons that some of these fires escape and become actual forest fires.

Figure 1 shows the most recent cloud-free view of the entire Amazon biome. On the positive, one can clearly see the core Amazon still stands. On the negative, however, the expanding deforestation around the edges is evident.


Major Deforestation Fronts – 2023

In this section, we review the current major deforestation fronts across the Amazon.

Figure 2 indicates these fronts (insets A-H) in relation to deforestation hotspot data over the past 8 years during MAAP’s active monitoring timeframe (2015-2022). Below we describe each deforestation area, by country. Common drivers across numerous Amazon countries include roads (MAAP #157), agriculture (MAAP #161), cattle, and gold mining (MAAP #178).

Also note that further below, in the Annex, we show the relative order of total Amazon primary forest loss by country over the past two years: Brazil by far the highest, followed by a middle pack of Bolivia, Peru, and Colombia, followed by lower levels in Venezuela, Ecuador, Suriname, Guyana, and French Guiana.

Figure 2. Amazon forest loss hotspots, 2015-2022. Data: UMD, Planet/NICFI, ACA/MAAP.

 

Brazilian Amazon

Figure 3. Major forest loss hotspots in the Brazilian Amazon. Data: UMD, Planet/NICFI, ACA/MAAP.

Brazil continues to be, by far, the leading source of Amazonian deforestation (MAAP #187), led by three major drivers: cattle pasture expansion near roads, soy plantations, and gold mining.

Deforestation for new cattle pasture is concentrated along the extensive road networks spanning the eastern and southern Brazilian Amazon (for example, Inset A).

Deforestation for expanding soy plantations is concentrated in the southeast Brazilian Amazon (Inset B; see MAAP #161).

Gold mining deforestation impacts numerous sites, including several indigenous territories (for example, Inset C; see MAAP #178).

Bolivian Amazon

Figure 4. Major forest loss hotspots in the Bolivian Amazon. Data: UMD, Planet/NICFI, ACA/MAAP.

Bolivia has emerged as the clear second-leading source of Amazonian deforestation, with a major increasing trend over the past two years (MAAP #187).

The deforestation is concentrated in the soy frontier located in the southeast (Inset D, see MAAP #179).

Note that, increasingly, this soy deforestation is carried out by Mennonite colonies (MAAP #180). We revealed that Mennonites caused the deforestation of over 210,000 hectares since 2001, including 33,000 hectares since 2017.

Peruvian Amazon

Figure 5. Major forest loss hotspots in the Peruvian Amazon. Data: UMD, Planet/NICFI, ACA/MAAP.

Peru is the third-leading source of Amazonian deforestation (MAAP #187).

In the central Amazon, we have been highlighting the rapid deforestation for new Mennonite colonies (see MAAP #188). MAAP reports revealed, in real-time, Mennonite deforestation growing from zero in 2016, to 3,400 hectares in 2021, to 4,800 hectares in 2022, to 7,032 hectares in 2023.

In the southern Amazon, gold mining deforestation continues to be a major cause of deforestation, primarily in indigenous communities, protected area buffer zones, and within the official Mining Corridor (MAAP #185). Most recently, we showed that gold mining has caused the deforestation on nearly 24,000 hectares between just 2021 and 2023 (MAAP #195).

Colombian Amazon

Figure 6. Major forest loss hotspots in the Colombian Amazon. Data: UMD, Planet/NICFI, ACA/MAAP.

Colombia is the fourth-leading source of Amazonian deforestation.

Deforestation in Colombia spiked following the 2016 peace agreement between the Colombian government and the FARC guerilla group (MAAP #120), but was the only country with a notable deforestation decrease in 2022 (MAAP #187).

Forest loss is concentrated in an “arc of deforestation” surrounding numerous Protected Areas (such as Chiribiquete, Tinigua, and Macarena National Parks) and Indigenous Reserves.

In Colombia, the major direct deforestation driver is cattle pasture, but this expansion is largely caused by land grabbing as a critical indirect driver. Coca plantations also continue to be an important direct driver in certain remote areas.

Both cattle and coca are impacting protected areas, especially Tinigua and Chiribiquete National Parks (cattle); and Macrarena National Park and Nukak National Nature Reserve (coca).

Ecuadorian Amazon

Figure 7. Major forest loss hotspots in the Ecuadorian Amazon. Data: UMD, Planet/NICFI, ACA/MAAP, RAISG.

Although accounting for just 1% of total loss across the Amazon, deforestation in the Ecuadorian Amazon was the highest on record in 2022 (18,902 hectares), up a striking 80% since 2021.

There are several deforestation hotspots caused by gold mining (see MAAP #182), oil palm plantation expansion, and small-scale agriculture.

Venezuelan Amazon

There is a deforestation hotspot caused by gold mining in Yapacana National Park (see MAAP #173MAAP #156MAAP #169).

Annex: Amazon Primary Forest Loss (By Country), 2021-2022

Acknowledgments

We deeply thank the following funders for supporting MAAP over the past 10 years:
International Conservation Fund of Canada (ICFC)
Norwegian Agency for Development Cooperation (NORAD)
United States Agency for International Development (USAID)
MacArthur Foundation
Andes Amazon Fund (AAF)
Wyss Foundation
Erol Foundation
Global Forest Watch/World Resources Institute
Overbrook Foundation
Global Conservation

We also thank our key data providers:
Planet (optical satellite imagery)
University of Maryland (automated forest loss alerts)
Global Forest Watch (portal featuring integrated forest loss alerts)
NICFI monthly mosaics
CLASlite (our original forest loss detection tool)

Citation

Finer M, Mamani N, Novoa S, Ariñez A (2023) State of the Amazon in 2023. MAAP: 200.

MAAP Colombia: Chiribiquete – Deforestation Hotspots in the Colombian Amazon, part 3

MAAP #86: Deforestation Hotspots in the Colombian Amazon, part 3: Chiribiquete-Macarena

We present our third report* in a series investigating deforestation hotspots in the Colombian Amazon. Here, we focus on the “Chiribiquete-Macarena” hotspot, located between the Chiribiquete and La Macarena National Parks.

The Colombian government is finalizing plans to expand the boundaries of Chiribiquete National Park, an important step for conservation. However, we show (with high-resolution images) that deforestation is surging in the area and rapidly expanding towards these new boundaries. In fact, in 2018, deforestation has entered the newly expanded park.

MAAP #86: Deforestation Hotspots in the Colombian Amazon, part 3: Chiribiquete-Macarena

https://www.maapprogram.org/chiribiquete/

 

*The first report focused on the “Caguan” hotspot in the department of Caquetá. The second report focused on the “La Paya” hotspot in the department of Putumayo.