Amazon Fire Tracker 2020: Over 200 Major Fires As Of Aug 10

Photo of Brazil Fire 76 on July 31 2020Our innovative new app for Real-time Amazon Fire Monitoring has detected over 200 major fires in 2020.

The app specializes in filtering out thousands of the traditional heat-based fire alerts to prioritize only those burning large amounts of biomass (defined here as a major fire).*

Our key findings include:

  • We have detected 227 major Amazon fires (Brazil 220, Bolivia 6; Peru 1), as of August 10.
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  • The vast majority of major fires have been in the Brazilian Amazon, where a strikingly high number (85%) have burned recently deforested areas. Thus, the fires are actually a smoking indicator of the rampant deforestation now in Brazil.
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  • In Brazil, we have detected two forest fires, but this risk increases as we get deeper into the dry season. The rest of the fires have been on older fields.
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  • In Brazil, the vast majority (94%) of the major fires have been illegal, in violation of the state and national fire moratoriums established in July. In fact, despite the moratoriums, the number of major fires is accelerating: 143 so far in August following 77 in May through July.
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  • In Brazil, 14 of the fires have been in Protected Areas.
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  • In the Bolivian and Peruvian Amazon, we have recently started detecting fires in the drier ecosystems (savannahs and grasslands).

See below for a more detailed breakdown of the results.

 

Additional Results

The Base Map is a screen shot of the app’s “Major Amazon Fires 2020” layer.

The vast majority of the fires have been in the Brazilian AmazonPará (37%) and Amazonas (39%), followed by Mato Grosso (17%) and Rondônia (8%).

Importantly, the vast majority of the major fires in the Brazilian Amazon (85%) have burned recently deforested areas (cleared between 2018 and 2020) covering 280,000 acres (113,000 hectares). Thus, we argue that the central issue is actually deforestation and the fires are actually a smoking indicator of this forest loss.

We have detected the first two forest fires, burning 388 acres (1,447 hectares) in Mato Grosso and Para.

The rest of the major fires have been on older cattle or agricultural lands (deforested prior to 2018).

The most impacted protected areas are Jamanxim and Altamira National Forests in Pará. We emphasize, however, that these fires were burning recently deforested areas (not forest fires) and so, again, the primary issue is deforestation.

In Brazil, the vast majority of the major fires (94%) appear to be illegal as they violate the state and national government mandated fire moratoriums established in July. In fact, despite the moratoriums, the number of major fires is accelerating: 143 so far in August, following 64 in July, 12 in June, and the first one in May.

In the Bolivian Amazon, we have recently started detecting fires in the savannahs in the department of Beni. We also detected one fire in a recently deforested area in the Santa Cruz department.

In the Peruvian Amazon, we have recently started detecting fires in the upper elevation grasslands. The biggest one was actually within a protected area (Otishi National Park). There have also been smaller grassland fires near the buffer zone of upper Manu National Park.

 

Key Examples of 2020 Fires

Overall our key finding is that most major Brazilian Amazon fires are burning recently deforested areas, and not raging forest fires. Below is a series of satellite image time-lapse videos showing examples of recent deforestation followed by a major 2020 fire.

 

Brazilian Amazon Fire #54, July 2020

 

Brazilian Amazon Fire #59, July 2020

 

Brazilian Amazon Fire #76, July 2020

 

Brazilian Amazon Fire #110, August 2020

 

*Notes and Methodology

In a novel approach, the app combines data from the atmosphere (aerosol emissions in smoke) and the ground (heat anomaly alerts) to effectively detect and visualize major Amazon fires.

When fires burn, they emit gases and aerosols. A new satellite (Sentinel-5P from the European Space Agency) detects these aerosol emissions. Thus, the major feature of the app is detecting elevated aerosol emissions which in turn indicate the burning of large amounts of biomass. For example, the app distinguishes small fires clearing old fields (and burning little biomass) from larger fires burning recently deforested areas or standing forest (and burning lots of biomass).

We define “major fire” as one showing elevated aerosol emission levels on the app, thus indicating the burning of elevated levels of biomass. This typically translates to an aerosol index of >1 (or cyan-green to red on the app). To identify the exact source of the elevated emissions, we reduce the intensity of aerosol data in order to see the underlying terrestrial heat-based fire alerts. Typically for major fires, there is a large cluster of alerts. The major fires are then confirmed, and burn areas estimated, using high-resolution satellite imagery from Planet Explorer.

See MAAP #118 for additional details.

No fires permitted in the Brazilian state of Mato Grosso after July 1, 2020. No fires permitted in all of Brazilian Amazon after July 15, 2020. Thus, we defined “illegal” as any major fires detected after these respective dates.

There was no available Sentinel-5 aerosol data on July 4, 15, and 26.

 

Acknowledgements

This analysis was done by Amazon Conservation in collaboration with SERVIR Amazonia.

Citation

Finer M, Nicolau A, Villa L (2020) 200 Major Amazon Fires in 2020: Tracker Analysis. MAAP.

153,000 Acres Of Brazil Nut Forests Protected by Amazon Conservation and Google

 Brazil nut concessionaires walking in forestAmazon Conservation’s sister organization Conservación Amazónica – ACCA, with support from Google.org, just finished up a two-year initiative that trained community members to use cutting-edge satellite and field technologies to combat deforestation in the southern Peruvian Amazon, now protecting over 150,000 acres of lowland forests.

This initiative trained 75 Brazil nut harvesters and their families in forest monitoring technologies, which will help them safeguard forests to be used for sustainable purposes. Preventing deforestation of natural resources is not only environmentally important, but also economically, as the productive forests in and around the Madre de Dios area in Peru provide a sustainable and forest-friendly economic income to around 45,000 people, about 20% of the population.

In Peru, local families or associations can be granted a piece of public forests to be used for specific purposes – called a concession – such as harvesting nuts and berries, or for ecotourism. This system prevents acres of forests from falling victim to destructive activities, such as land squatting, illegal logging, or invasions by gold miners. Additionally, concessionaires are required by law to report on illicit activities in their concessions, which is a way the government gets community support to protect large swaths of forests.

Brazil nut concessionairesBefore this program, concessionaires and their communities lacked capacity to monitor these large, remote areas and a way to rapidly and safely report deforestation in their territories. Our innovative methodology of combining real-time satellite imagery analysis and drone field technology (which includes smartapps and other technologies developed by Google) with legal training, gave concessionaires the ability to detect and report deforestation as it happened in their territory. This is a stark contrast from before, when the only way to monitor thousands of acres of forests was through foot patrols that took days to complete. 

Now 75 Brazil nut harvesters and their families are using satellite imagery, early deforestation alerts, and GPS applications on mobile devices to monitor their forests. Among them, 23 individuals successfully obtained their licenses as drone pilots from the Ministry of Transport and Communications’ General Directorate of Civil Aeronautics. This means they can now their entire territory in minutes, without having to face potential risks of confronting dangerous individuals committing environmental crimes or even running into outsiders who might bring diseases like the novel coronavirus into their communities. 

Brazil nut appetizersThrough this program, over 153,000 acres (62,000 hectares) of forests are now monitored and protected with technology by the local people we empowered. Moreover, technological kits were donated to each individual or local association, each containing a drone, a maintenance kit, a laptop and a printer, giving them the knowledge and tools needed to safeguard forests..

These successes were celebrated with a closing ceremony in the Castaña Amazon Park earlier this year. Local authorities and representatives of local organizations attended, such as the director of the Research Institute of the Peruvian Amazon (IIAP) and members of local harvesting associations. During the ceremony, attendees enjoyed Brazil nut appetizers, while watching presentations about the project, the results achieved, and the collaborators and participants. The event ended with a guided tour of the Brazil Nut Harvesting Center in the Castaña Amazon Park, which is noted as the first living Brazil nut tree park in the world.

Presenter at Brazil Nut Google EventThe project, led by our director of our Southwest Amazon Drone Center, Carlos Castañeda, will continue to provide technical support to maintain the donated drones and training to reinforce what they learned, as well as be available to answer any questions that may arise during monitoring and surveillance of their concessions. Thus, the continuity of the project and its sustainability are ensured.

This Google.org-funded project was the first of its kind nationwide in Peru. After this success, Amazon Conservation continues its mission of conserving the Amazon basin using new technologies. Over the next three years, we hope to strengthen the real-time monitoring of the forests by empowering local people and employing science and technology as a proven way to fight deforestation in the Amazon and create a model for other tropical forests around the world.

Amazon Fire Tracker 2020 – July Update

Recall we recently launched an innovative new app for Real-time Amazon Fire Monitoring (see MAAP #118 for details).

In a novel approach, the app combines data from the atmosphere (aerosol emissions in smoke) and the ground (heat anomaly alerts) to effectively detect and visualize major Amazon fires.

The app specializes in filtering out thousands of the heat-based fire alerts to prioritize only those burning large amounts of biomass and thus emitting elevated levels of aerosol (defined here as a major fire).*

Example of a major fire in the Brazilian Amazon burning recently deforested area. Brazil major fire #54, July 30, Mato Grosso. Image: Planetscope (Planet).
Example of a major fire in the Brazilian Amazon burning recently deforested area. Brazil major fire #54, July 30, Mato Grosso. Image: Planetscope (Planet).

As of the end of July, we have detected 77 major Amazon fires thus far in 2020, all in Brazil.

In summary, 84% of the major fires are burned recently deforested areas and 83% were illegal (in violation of fire moratoriums). We detected the first forest fire on the last day of the month.

We have started detecting large and uncontrolled fires in the drier ecosystems of Bolivia, but outside the Amazon watershed.

See below for a more detailed overview of the 2020 Amazon fire season thru the end of July.

 

Key Results

The Base Map is a screen shot of the app’s “Major Amazon Fires 2020” layer.

Base Map. Screen shot of the app’s “Major Amazon Fires 2020” layer.
Base Map. Screen shot of the app’s “Major Amazon Fires 2020” layer.

As noted above, we have detected 77 major Amazon fires thus far in 2020, all in Brazil.

The first major fire was detected on May 28 in the state of Mato Grosso in southeastern Brazilian Amazon (see MAAP #118). This event was followed by 12 major fires in June, all in Mato Grosso (see Fire Tracker #12).

The number of major fires in Mato Grosso decreased in July, suggesting the state’s new fire moratorium (starting July 1) may be working.

Starting in mid-July, the major fire activity shifted to the surrounding Brazilian states of Amazonas, Rondônia and Pará. This shift coincided with national fire moratorium (starting July 15), indicating it has not been as effective.

Overall, most of the major fires (83%) appear to be illegal as they violate the state and national government mandated fire moratoriums established in July.

Importantly, most of the major fires (84%) have burned recently deforested areas (deforested 2018-20) covering 108,000 acres (44,000 hectares). See MAAP #113 for more on this important point in regards to the 2019 fires.

We detected the first forest fire on the last day of the month. It burned 388 acres (157 hectares).

The other major fires have been in older cattle or agricultural areas (deforested pre 2018).

We have started detecting large and uncontrolled fires in the drier ecosystems of Bolivia, but outside the Amazon watershed.

 

Key Examples of 2020 Fires

Overall our key finding is that most major Brazilian Amazon fires are burning recently deforested areas, and not raging forest fires. Below is a series of four satellite images time-lapse videos showing examples of recent deforestation (2019) followed by a major 2020 fire burning lots of biomass that was detected by the app.

 

Brazilian Amazon Fire #1, May 2020

Brazilian Amazon Fire #4, June 2020

 

Brazilian Amazon Fire #12, June 2020

Brazilian Amazon Fire #18, July 2020

Brazilian Amazon Fire #54, July 2020

*Notes and Methodology

When fires burn, they emit gases and aerosols. A new satellite (Sentinel-5P from the European Space Agency) detects these aerosol emissions. Thus, the major feature of the app is detecting elevated aerosol emissions which in turn indicate the burning of large amounts of biomass. For example, the app distinguishes small fires clearing old fields (and burning little biomass) from larger fires burning recently deforested areas or standing forest (and burning lots of biomass).

We define “major fire” as one showing elevated aerosol emission levels on the app, thus indicating the burning of elevated levels of biomass. This typically translates to an aerosol index of >1 (or cyan-green to red on the app). To identify the exact source of the elevated emissions, we reduce the intensity of aerosol data in order to see the underlying terrestrial heat-based fire alerts. Typically for major fires, there is a large cluster of alerts. The major fires are then confirmed, and burn areas estimated, using high-resolution satellite imagery from Planet Explorer.

No fires permitted in the Brazilian state of Mato Grosso after July 1, 2020. No fires permitted in all of Brazilian Amazon after July 15, 2020. Thus, we defined “illegal” as any major fires detected after these respective dates.

There was no available Sentinel-5 aerosol data on July 4, 15, and 26.

Acknowledgements

This analysis was done by Amazon Conservation in collaboration with SERVIR Amazonia.

Citation

Finer M, Nicolau A, Villa L (2020) Amazon Fire Tracker 2020 – July Update. MAAP.

Bringing Climate Resilience to Local Communities

For the past year our team in Bolivia and Peru have been working with EUROCLIMA+, an initiative of the European Commission focused on combating climate change in Latin America. We are working with local communities to pilot climate change resilience in their sustainable use of forest resources.

Promoting sustainable forest resources is important for keeping forests standing, and an initiative that we have been expanding for many years now. The Amazon rainforest is full of economically valuable products, such as the Brazil nuts and açaí berries, which are important sources of income for local communities. These fruits can only grow in standing forests, and cannot survive in a monoculture or farmed operation setting. 

 

 

An Economic Essential

Luis Arteaga, our Technical Director in Bolivia, coordinates this project. His team works in the northern part of Bolivia, where local communities heavily depend on these forest goods to make a living. “Almost all the families dedicate themselves to harvesting forest fruits, mainly the Brazil nut, which is their main economic activity.” 

Noting the ecological makeup of the area, one can see why: the northern municipality of the Santa Rosa del Ábuna conservation area has the highest concentration of Brazil nut trees in the department of Pando, Bolivia. These nuts generate up to 90% of local families’ overall income, and although harvesting is a job that requires a lot of dedication and back-breaking work, it generates important opportunities for commercialization and sustainable forest management. Luis puts it simply, “If Brazil nuts didn’t exist or didn’t grow in these forests, they would have already been cut down for another economic activity.” 

bags of brazil nutsTying the importance of conservation of these forests not only to climate change but also to economic sustainability of local and global economies is vital for countries and communities to see the value of forests. In fact, our area of work in Bolivia holds 85% of the Brazil nut production in the world, and keeping those forests standing through sustainable activities will have a significant impact in the fight against deforestation and carbon emissions.

 

 

Confronting Climate Change

A key aspect of our work with EUROCLIMA+ is recognizing how these sustainable forest economies help mitigate the effects of climate change on communities and on the planet, which hadn’t previously been as much on peoples’ minds. This pilot work is also helping local communities become aware of how climate is changing the forests on which they depend, so they can plan for their long-term, sustainable use, without needing to turn to destructive practices like timber extraction and cattle ranching if a harvesting season is affected by global warming. This involves not only making sure we have healthy forests, but also helping communities diversify their source of income sustainably, such as harvesting other complementary forest products like açaí berries and sustainably farming paiche fish. 

“In my opinion,” Luis notes, “one important advancement is that we are learning how climate change has impacted, is impacting, and will impact this vital bi-national region of the Amazon in Peru and Bolivia. Working with EUROCLIMA+ has taught us to use the climate lens to think about all of our future conservation work as well, and this is a good step forward.”

The Escazú Agreement: Internationalizing the Amazon?

Populism and nationalism in politics are two sides of the same coin.

By: Enrique Ortiz, Amazon Conservation Board Member. (Original article published in El Comercio. See here.)

Photo of Enrique Ortiz, author of the articleThe Escazú Agreement, a regional agreement on access to information, public participation and access to justice in environmental matters in Latin America and the Caribbean whose ratification is soon to be debated in Congress, has generated an intense reaction and discussion. There is a sector that affirms that this agreement would attempt against our sovereignty in the Amazon. Considering that if this agreement is ratified, the important decisions for the economic development of the country would remain in the hands of international spheres. On the other hand, others consider that such an agreement leads to improved information flow and citizen participation. Both are necessary for the development of the country, particularly in Peru where social and environmental conflicts have paralyzed many important works for the economy. Understanding the scope of the agreement and its true implications is crucial for the future of Peru.

The Escazú Agreement stipulates that the signatory countries undertake to comply with a series of mechanisms for transparency of information, consultation, decision making processes, protection of environmental defenders and conflict resolution related to projects that may affect the environment.

How can the Escazú Agreement threaten national sovereignty, and in particular, with our Amazon? To begin with, this is a Latin American regional agreement, which has been signed by 22 democratic nations (including those Amazonian), and so far, has been ratified by 9 of them. The agreement clearly states that decisions are the affairs of each country, within their own regulatory frameworks.  It also stipulates that in cases where the conflict is between States, these – and only under a bilateral agreement – can be submitted to arbitration by the International Court of The Hague, as an international instance. That court does not have jurisdiction for internal affairs of a country, such as those between private, communities and the State. The resolution of controversies within a country is another matter, and only after exhausting the national justice mechanisms, they can be resolved by resorting to international bodies, which have nothing to do with the Escazú agreement.

There is a fear that said agreement will hinder important development projects for the country, or for a specific interest group. And it is argued that this is particularly important in times when we urgently need an economic revival. And it is true, we need development plans, but those that are economically, socially and environmentally sustainable. Otherwise, we will have more Tía Marías, Congas and other extractive projects stranded in the midst of conflicts with no solution in sight. What is expected, instead, is that the Escazú Agreement has the key to resolve these situations throughout the country, on the coast, the Andes and the Amazon.

Peru has played a very important role in the gestation of this agreement since the Rio+20 United Nations conference in 2012. Our chancellery -for three governments- has promoted the vision and structure of this agreement, as expressed in the Lima Declaration. Furthermore, Peru held the vice-presidency of the negotiating executive committee’s and signed the agreement in September 2018, at the United Nations headquarters. In August 2019, President Martín Vizcarra and his chancellor sent the draft legislative resolution to the then President of Congress, for approval. How can it be that, suddenly, the referred agreement is branded by some as a surrogate that cedes 53% of the country to foreign environmental NGOs, and as a national newspaper denounces on the front page, “do they want to rob us of the Amazon”? Very strange.

Populism and nationalism in politics are two sides of the same coin. Painful examples of this are part of our recent history, and today we are seeing it in Brazil. We want development projects that can advance, that are profitable and that have mechanisms for participation, defense of citizens’ rights, and with a long-term vision, as recommended by the OCDE studies, to which our country wants to access. Vision is a keyword for the bicentennial. Let us keep our eyes open to the opportunities that this agreement can give us.

 

Behind the Camera: A Look at Camera Trap Impacts

The past few months we’ve featured “Camera Trap Tuesday” on our social media pages, posting glimpses of Amazon animals living their daily lives, freely interacting with each other and their environment when there’s no human presence. But what is the real impact of camera traps? Our camera traps and wildlife conservation expert Nelly Guerra talks about this important initiative; and what it’s like working on our camera trap program in Bolivia with our sister organization Conservación Amazónica – ACEAA. She also recently presented a webinar on the camera trap program in Bolivia, which you can view here.

 

Benefits of Camera Trap Technology

To begin, Nelly notes that placing camera traps in the forests is the most effective way to record wild species. Images and videos of medium and large-sized mammals commonly elusive to the human eye are recorded in their natural habitats throughout the day and night. Cameras are able to stay out in the field for much longer than a person, be less disruptive, and observe more hours of authentic animal activity. The camera traps are a useful tool to obtain accurate information on the distribution of many species, their abundance, activity patterns, and habitat use. Camera trap management is a key technology that we use to understand the state of biodiversity in an area, which allows us to evaluate key regions to protect and adjust our conservation efforts.

 

A Snapshot of Our Current Implementation

Our camera trap program has been implemented in our areas of work in Bolivia since 2015. We have camera traps placed in:

  1. TCO Tacana II, an indigenous territory we’ve worked with for decades in the North of the Department of La Paz,
  2. Santa Rosa del Abuná Integral Model Area, a conservation area we helped create in the department of Pando,
  3. Manuripi National Wildlife Reserve National Protected Area, an area for conservation we’ve been supporting also in the Department of Pando.

These places have successfully managed to register a wide variety of wild species, several of which had previously been declared as no longer living in the area.

We have recorded many animals in the area that have been categorized as endangered, near-threatened, or vulnerable by the internationally-recognized IUCN Red List of threatened species. This includes the endangered giant otter (Pteronura brasiliensis), near-threatened jaguar (Pantera onca), bush dog (Speothos venaticus), and harpy eagle (Harpia harpyja), as well as the vulnerable white-lipped peccary (Tayassu pecari) and South American tapir (Tapirus terrestris).

 

Successes of Camera Traps

One highlight of this project has been getting to know an incomparable variety of wildlife. Camera traps have given us data that helps us understand which forests are healthy, because the healthy ones host a great amount of biodiversity.

Another very important accomplishment of working with the camera traps is they have encouraged the inclusion and interest of Indigenous peoples and communities in working with this technology. They provide a way for these communities to monitor the wildlife that exists in their forests and evaluate their conservation status, while at the same time committing to conserving and caring for the Amazon’s wild fauna. For Nelly, “The greatest achievement has been an interest in documenting wildlife through videos and photographs, as well as the interest to develop new camera trap techniques without altering the natural habitat of the species that hide inside our forests.” Getting communities up and close to the animals with whom they share their forest home helps them become more active in their conservation.

 

Zooming in on the Future

Camera trap photo of deerTo wrap up, we ask Nelly what she wants others to know about this technology. She replies that, “Working with camera traps is a methodology of gaining conservation information. They are a very useful tool to measure indicators of abundance and distribution of wildlife populations, and obtain data economically without disturbing the natural habitat of wild species. They allow us to analyze the state of conservation of the forests, because the more fauna records collected with the camera traps, the healthier our forests are. Conversely, if you have fewer fauna records that means that our forests are being disturbed by humans and that it makes the fauna migrate to other less disturbed places.”

If all goes well after the pandemic that we are experiencing, Nelly hopes that this beneficial forest monitoring program can be expanded, and more camera traps could be installed in other key areas. She finishes with a message for young conservationists saying, “I would like to encourage students to work and do wildlife research with camera traps, and learn to perform research on the state of our biodiversity in our Amazon forests.”

 

 

 

Restoring Degraded Forests with Rosewood

Team member planting rosewood seedling

Rosewood (Aniba rosaeodora) is a unique type of tropical hardwood, noted for the dark red color that stains its inner trunk and a sweet smell that gets processed into Rosewood essential oil, which is a major ingredient of high quality perfumes and cosmetic products. The oil is obtained from tree trunks through steam distillation from chipped wood and bark, methods that require the destruction of the tree. Because of this economic value, rosewood trees have been cut in such large proportions in the Amazon that natural populations are significantly depleted. It is internationally recognized by the IUCN Red List as an endangered plant species. Thus, with support from the National Fish and Wildlife Foundation, Amazon Conservation began a project to recover a population of rosewood and explore the use of this species for reforestation and restoration of degraded forests damaged by slash-and-burn agriculture and artisanal, illegal gold mining. 

The lowland Amazonian forests at our Los Amigos Conservation Hub in Peru offer the perfect conditions for re-establishing rosewood trees. The areas at Los Amigos selected for planting had previously been disturbed by slash-and-burn agriculture and artisanal gold mining, but surrounded by primary forest. The project demonstrates that rosewood is a species that can be used in projects to restore degraded lands, which can be applied to thousands of hectares of degraded lands across the region impacted by extractive activities. Moreover, the trees planted in this project can serve as a seed bank for others who may wish to reforest and conduct ecological restoration that includes rosewood, either for strict conservation or for managed, nondestructive leaf harvest, which could generate additional income for local communities.

 

Just arrived rosewood (Aniba roseadora) seedlings being prepared to plant in temporary bags.Getting Started: A Quest to Find Rosewood Seedlings

 

We planned to purchase rosewood seedlings from a local provider in the region of Madre de Dios, Peru, but this proved to be a challenge due to the scarcity of rosewood seeds. After contacting a number of providers throughout Peru, we obtained 2,500 seedlings from our friends at the nonprofit Camino Verde, located in northern Peru. 

The long trip from northern Peru took its toll on the seedlings. Upon arrival to Los Amigos, the project’s agroforestry technician placed and cared for them in the nursery, where he closely monitored their development and nursed them back to health. After a couple of weeks of care, the seedlings were ready to be transplanted to the degraded areas identified for restoration! 

 

Rosewood seedling with biocharPlant TLC: Adding Soil-Enriching Biochar to Help Seedlings Survival 

 

To increase the chance of the seedlings’ survival once transplanted to the affected areas – since much of the soil was dry and damaged – we added biochar when planting them.

Biochar is a soil-enhancing charcoal made from sustainable sources that helps retain water and nutrients in the soil for plants to take up as they grow. Biochar has also been known to clean mercury contamination from the soil, which would also improve the soils previously contaminated activities.

A total of two tons of biochar were acquired from the nonprofit consortium CINCIA (Centro de Innovación Científica Amazónica), half of which were kindly donated. 

 

Our team preparing the Rosewood restoration areaPreparing the Restoration area

Preparation of the restoration area was originally planned for March and April of this year, but the delay of the rainy season last year allowed us to get a head-start in prepping the area for the seedlings in mid-September 2019 (which was great timing, as our original timeline would have been affected by the COVID-19 global pandemic).

Our agroforestry experts prepared the land through clearing weeds and shrubs from the area. The standing Guayaba trees (Psidium guajava) already present in the forest were left, serving as a complementary tree species to the rosewood seedlings, providing shade and protecting them from intense sun and rain.

 

Rosewood seedlings being transported by riverGiving the seedlings a new home

From October-December 2019, our agroforestry technicians planted the rosewood Team member planting rosewood seedlingseedlings mixed with biochar. The first 1,250 seedlings were transplanted to a target area of 2.1 hectares (5.2 acres), which had been verified as an ideal area for restoration through reforestation using this species. A tractor and a short boat trip down the river helped bring the seedlings to their new home, where they were planted throughout the end of 2019.

The remaining 1,250 unplanted rosewood seedlings continued to grow in the nursery through the rainy season, along with other local seedlings to support a healthy forest ecosystem and the steady growth of rosewood, including 500 moriche palms (Mauritia flexuosa or “aguajes” in Spanish), 150 bolaina blancas (Guazuma crinita) and 650 Amazon grapes (Pourouma cecropiifolia) seedlings. By April 2020 the rainy season had ended, and our team had just finished planting the remaining trees. As of April, a total of 5,000 trees have been planted: 2,500 rosewood seedlings and 2,500 complementary tree species. We look forward to studying how this reforestation effort improves degraded forest, and based on the survival rate of the seedlings, whether it can be expanded to other areas of the Amazon disturbed by slash-and-burn agriculture and illegal gold mining.

 

We thank the National Fish and Wildlife Foundation for their generous contribution to carry out this important project, which will support the planting of almost 5,000 essential trees to restore damaged lands in the Amazon.  

——

 

MAAP #122: Amazon Deforestation 2019

Newly released data for 2019 reveals the loss of over 1.7 million hectares (4.3 million acres) of primary Amazon forest in our 5 country study area (Bolivia, Brazil, Colombia, Ecuador, and Peru).* That is twice the size of Yellowstone National Park.

Table 1 shows 2019 deforestation (red) in relation to 2018 (orange).

Table 1. Amazon 2019 primary forest loss for 2019 (red) compared to 2018 (orange). Data: Hansen/UMD/Google/USGS/NASA, MAAP.
Table 1. Amazon 2019 primary forest loss for 2019 (red) compared to 2018 (orange). Data: Hansen/UMD/Google/USGS/NASA, MAAP.

Primary forest loss in the Brazilian Amazon (1.29 million hectares) was over 3.5 times higher than the other four countries combined, with a slight increase in 2019 relative to 2018. Many of these areas were cleared in the first half of the year and then burned in August, generating international attention.

Primary forest loss rose sharply in the Bolivian Amazon (222,834 hectares), largely due to uncontrolled fires escaping into the dry forests of the southern Amazon.

Primary forest loss rose slightly in the Peruvian Amazon (161,625 hectares) despite a relatively successful crackdown on illegal gold mining, pointing to small-scale agriculture (and cattle) as the main driver.

On the positive side, primary forest loss decreased in the Colombian Amazon (91,400 hectares) following a major spike following the 2016 peace accords (between the government and FARC). It is worth noting, however, that we have now documented the loss of 444,000 hectares (over a million acres) of primary forest in the Colombian Amazon in the past four years since the peace agreement (see Annex).

*Two important points about the data. First, we use annual forest loss from the University of Maryland to have a consistent source across all five countries. Second, we applied a filter to only include loss of primary forest (see Methodology).

 

2019 Deforestation Hotspots Map

The Base Map below shows the major 2019 deforestation hotspots across the Amazon.

2019 deforestation hotspots across the Amazon. Data: Hansen/UMD/Google/USGS/NASA, MAAP.
2019 deforestation hotspots across the Amazon. Data: Hansen/UMD/Google/USGS/NASA, MAAP.

Many of the major deforestation hotspots were in Brazil. Early in the year, in March, there were uncontrolled fires up north in the state of Roraima. Further south, along the Trans-Amazonian Highway, much of the deforestation occurred in the first half of the year, followed by the high profile fires starting in late July. Note that many of these fires were burning recently deforested areas, and were not uncontrolled forest fires (MAAP #113).

The Brazilian Amazon also experienced escalating gold mining deforestation in indigenous territories (MAAP #116).

Bolivia also had an intense 2019 fire season. Unlike Brazil, many were uncontrolled fires, particularly in the Beni grasslands and Chiquitano dry forests of the southern Bolivian Amazon (MAAP #108).

In Peru, although illegal gold mining deforestation decreased (MAAP #121), small-scale agriculture (including cattle) continues to be a major driver in the central Amazon (MAAP #112) and an emerging driver in the south.

In Colombia, there is an “arc of deforestation” in the northwestern Amazon. This arc includes four protected areas (Tinigua, Chiribiquete and Macarena National Parks, and Nukak National Reserve) and two Indigenous Reserves (Resguardos Indígenas Nukak-Maku and Llanos del Yari-Yaguara II) experiencing substantial deforestation (MAAP #120). One of the main deforestation drivers in the region is conversion to pasture for land grabbing or cattle ranching.

Annex – Colombia peace accord trend

Table 1. Deforestation of primary forest in the Colombian Amazon, 2015-20. Data: Hansen/UMD/Google/USGS/NASA, UMD/GLAD. *Until May 2020
Table 1. Deforestation of primary forest in the Colombian Amazon, 2015-20. Data: Hansen/UMD/Google/USGS/NASA, UMD/GLAD. *Until May 2020

Methodology

The baseline forest loss data presented in this report were generated by the Global Land Analysis and Discovery (GLAD) laboratory at the University of Maryland (Hansen et al 2013) and presented by Global Forest Watch. Our study area is strictly what is highlighted in the Base Map.

For our estimate of primary forest loss, we used the annual “forest cover loss” data with density >30% of the “tree cover” from the year 2001. Then we intersected the forest cover loss data with the additional dataset “primary humid tropical forests” as of 2001 (Turubanova et al 2018). For more details on this part of the methodology, see the Technical Blog from Global Forest Watch (Goldman and Weisse 2019).

For boundaries, we used the biogeographical limit (as defined by RAISG) for all countries except Bolivia, where we used the Amazon watershed limit (see Base Map).

All data were processed under the geographical coordinate system WGS 1984. To calculate the areas in metric units, the projection was: Peru and Ecuador UTM 18 South, Bolivia UTM 20 South, Colombia MAGNA-Bogotá, and Brazil Eckert IV.

Lastly, to identify the deforestation hotspots, we conducted a kernel density estimate. This type of analysis calculates the magnitude per unit area of a particular phenomenon, in this case forest cover loss. We conducted this analysis using the Kernel Density tool from Spatial Analyst Tool Box of ArcGIS. We used the following parameters:

Search Radius: 15000 layer units (meters)
Kernel Density Function: Quartic kernel function
Cell Size in the map: 200 x 200 meters (4 hectares)
Everything else was left to the default setting.

For the Base Map, we used the following concentration percentages: Medium: 7%-10%; High: 11%-20%; Very High: >20%.

References

Goldman L, Weisse M (2019) Explicación de la Actualización de Datos de 2018 de Global Forest Watch. https://blog.globalforestwatch.org/data-and-research/blog-tecnico-explicacion-de-la-actualizacion-de-datos-de-2018-de-global-forest-watch

Hansen, M. C., P. V. Potapov, R. Moore, M. Hancher, S. A. Turubanova, A. Tyukavina, D. Thau, S. V. Stehman, S. J. Goetz, T. R. Loveland, A. Kommareddy, A. Egorov, L. Chini, C. O. Justice, and J. R. G. Townshend. 2013. “High-Resolution Global Maps of 21st-Century Forest Cover Change.” Science 342 (15 November): 850–53. Data available on-line from: http://earthenginepartners.appspot.com/science-2013-global-forest.

Turubanova S., Potapov P., Tyukavina, A., and Hansen M. (2018) Ongoing primary forest loss in Brazil, Democratic Republic of the Congo, and Indonesia. Environmental Research Letters  https://doi.org/10.1088/1748-9326/aacd1c 

Acknowledgements

We thank G. Palacios for helpful comments to earlier versions of this report.

This work was supported by the following major funders: Norwegian Agency for Development Cooperation (NORAD), Gordon and Betty Moore Foundation, International Conservation Fund of Canada (ICFC), Metabolic Studio, Erol Foundation, MacArthur Foundation, and Global Forest Watch Small Grants Fund (WRI).

Citation

Finer M, Mamani N (2020) 2019 Amazon Deforestation. MAAP: 122.

Amazon Fire Tracker 2020: Brazil Fire #12 (June 29)

As presented in MAAP #118, Amazon Conservation launched a real-time fire monitoring app that specializes in the rapid and user-friendly detection and visualization of major Amazon fires.

In a novel approach, the app combines data from the atmosphere (aerosol emissions in smoke) and the ground (heat anomalies) to effectively monitor large Amazon fires.

2020 Amazon major fire #12, in Mato Grosso Brazil, on June 29. Data: Planet. Analysis: MAAP/Amazon Conservation.
2020 Amazon major fire #12, in Mato Grosso Brazil, on June 29. Data: Planet. Analysis: MAAP/Amazon Conservation.

As detailed below, the app just detected the 12th major Amazon fire of the year on June 29, 2020 (see the high-resolution image to the right).

It burned 587 hectares (1,451 acres) of land deforested in 2019.

Thus far, all 12 major Amazon fires of 2020 have:

  • Occured in the state of Mato Grosso, in the southeastern Brazilian Amazon.
  • Burned recently deforested areas (that is, areas deforested in 2018, 2019, or 2020). In other words, these are not forest fires. See MAAP #113 for background on this important point.

Below, we describe the process of using the app to detect and confirm the fire on June 29.

 

Step 1.

Detection of elevated emissions in the southeastern Brazilian Amazon (Mato Grosso).

Step 1. Detection of elevated emissions in the southeastern Brazilian Amazon (Mato Grosso).

Step 2.

Zoom in to confirm the elevated aerosol emissions, indicating the burning of abundant biomass.

Step 2. Zoom in to confirm the elevated aerosol emissions, indicating the burning of abundant biomass.

 

Step 3.

Adjust the transparency to see the underlying fire alerts that indicate the exact location of the fires. Obtain coordinates of the source of the fires.

Step 3. Adjust the transparency to see the underlying fire alerts that indicate the exact location of the fires. Obtain coordinates of the source of the fires.

Step 4.

Confirm fire with satellite imagery. For example, here is a high resolution image from Planet Explorer showing the fire burning on June 29.

Step 4. Confirm fire with satellite imagery. For example, here is a high resolution image from Planet Explorer showing the fire burning on June 29.

Step 5.

Using Planet’s extensive imagery archive, we were able to determine that the fires were burning an area deforested in 2019 (and not a forest fire). In the timelapse below, see that the deforestation occurred between September and October 2019, and then burned on June 29, 2020. The final image shows the day after the fires, June 30, to see the full extent of the burn.

Coordinates

-10.99, -55.13

References

Gorelick, N., Hancher, M., Dixon, M., Ilyushchenko, S., Thau, D., & Moore, R. (2017). Google Earth Engine: Planetary-scale geospatial analysis for everyone. Remote Sensing of Environment.
Planet Team (2017). Planet Application Program Interface: In Space for Life on Earth. San Francisco, CA. https://api.planet.com

Acknowledgements

This work was supported by the following major funders: USAID/NASA (SERVIR), Global Forest Watch Small Grants Fund (WRI), Norwegian Agency for Development Cooperation (NORAD),  International Conservation Fund of Canada (ICFC), Metabolic Studio, and Erol Foundation.

 

Citation

Finer M, Villa L (2020) Amazon Fire Tracker 2020: Brazil #12 (June 29). MAAP.

MAAP#121: Reduction Of Illegal Gold Mining In The Peruvian Amazon

Thanks to the support of the USAID, via the Prevent Project, dedicated to the prevention and combat of environmental crimes in the Amazon, we conducted a detailed analysis of recent illegal gold mining deforestation in the southern Peruvian Amazon.

The objective is to understand the trends from early 2017 to June 2020 (which includes the first part of the mandatory quarantine issued by the Peruvian government as of March 16, 2020 due to the coronavirus pandemic).

Base Map. Illegal gold mining deforestacion in the protected area buffer zones of the southern Peruvian Amazon, 2017-2019. Data: MAAP. Click to enlarge image.
Base Map. Illegal gold mining deforestacion in the protected area buffer zones of the southern Peruvian Amazon, 2017-2019. Data: MAAP. Click to enlarge image.

We focus on the buffer zones of two protected areas in the Madre de Dios region: Tambopata National Reserve and Bahuaja Sonene National Park (see Base Map).*

This area includes La Pampa, the current highest intensity illegal mining zone in the country. In February 2019, the Peruvian government launched Operation Mercury  to confront the illegality in La Pampa and surrounding areas.

The Base Map shows that gold mining deforestation in La Pampa decreased over 90% following Operation Mercury.

However, illegal gold mining does continue after Operation Mercury (including during the coronavirus state of emergency), but at lower rates. Thus, current snapshots may be misleading and recent context is important.

On the Base Map, the red arrows indicate the areas with the most recent illegal activity (click the image to enlarge). See below for more details.

 

Main Results

Table 1. Illegal gold mining deforestation before (yellow) and after (red) Operation Mercury in the buffer zones of Madre de Dios. Data: MAAP.
Table 1. Illegal gold mining deforestation before (yellow) and after (red) Operation Mercury in the buffer zones of Madre de Dios. Data: MAAP.

The Base Map and Table 1 illustrate the following key results:

  • In La Pampa, we documented mining deforestation of 173 hectares (428 acres) per month before Operation Mercury (January 2018 – February 2019). After the intervention, deforestation was reduced to 14 hectares (36 acres) per month (March 2019 – May 2020), a decrease of 92%.
    .
  • Upstream, in the Alto Malinowski, we documented the mining deforestation of 61 hectares (150 acres) per month before Operation Mercury. After the intervention, deforestation was reduced to 28 hectares (69 acres) per month, a decrease of 53%.
    .
  • Downstream, in the Apaylon area, we documented the mining deforestation of 2.9 hectares (7 acres) per month, before Operation Mercury. After the intervention, deforestation increased to 4 hectares (10 acres) per month, an increase of 41%. Apaylon is main area in the buffer zone where deforestation has increased.
    .
  • Within Tambopata National Reserve, we documented the mining deforestation of 6.5 hectares (16 acres) per month, before Operation Mercury. After the intervention, deforestation was reduced to 0.5 hectares (1.2 acres) per month, a decrease of 93%.
    .
  • Overall, illegal gold mining does continue in the buffer zones of Madre de Dios, but at lower rates than the previous two years. We documented the gold mining deforestation of 797 hectares (1,670 acres) after Operation Mercury.
    .
  • Regarding the speculation that illegal activity would increase during the coronavirus pandemic, we have not documented any major increase or surge in the buffer zones of Madre de Dios.* Illegal mining does continue, however, we documented the deforestation of 80 hectares (198 acres) during the quarantine.

 

Reduction of 90% in La Pampa

The following images show the major decrease in gold mining deforestation in La Pampa after Operation Mercury. Image 1 shows the rapid deforestation before Operation Mercury, between January 2017 (left panel) and February 2019 (right panel). Image 2 shows how the deforestation decreased after Operation Mercury, between February 2019 (left panel) and May 2020 (right panel). The red dot represents a reference point between the images.

Image 1. Rapid gold mining deforestation in La Pampa before Operation Mercury, between January 2017 (left panel) and February 2019 (right panel). Data: Planet.
Image 1. Rapid gold mining deforestation in La Pampa before Operation Mercury, between January 2017 (left panel) and February 2019 (right panel). Data: Planet.
Image 2. Mining deforestation decreased in La Pampa after Operation Mercury, between February 2019 (left panel) and May 2020 (right panel). Data: Planet.
Image 2. Mining deforestation decreased in La Pampa after Operation Mercury, between February 2019 (left panel) and May 2020 (right panel). Data: Planet.

 

Displaced Miners?

There has also been speculation that the focus of Operation Mercury in La Pampa would lead to illegal miners moving to other areas.* Base Map 2 shows two of the most threatened areas: Camanti and Pariamanu.

Table 2. Deforestation by illegal gold mining before (yellow) and after (red) Operation Mercury in two other threatened areas. Data: MAAP.
Table 2. Deforestation by illegal gold mining before (yellow) and after (red) Operation Mercury in two other threatened areas. Data: MAAP.

These are the main results for these two areas:

  • In Camanti (located in the buffer zone of Amarakaeri Communal Reserve), we documented the gold mining deforestation of 13.3 hectares (33 acres) per month before Operation Mercury. After the intervention, deforestation was reduced to 6.1 hectares (15 acres) per month, a decrease of 54%.
    .
  • In Pariamanu, we documented  the mining deforestation of 2.5 hectares (6 acres) per month before Operation Mercury. After the intervention, it increased to 4.2 hectares (10 acres) per month, an increase of 70%.
  • In summary, illegal gold mining continues in these two areas outside La Pampa. We documented the mining deforestation of 175 hectares (432 acres) after Operation Mercury (including 22 hectares during the pandemic). There is some evidence that miners are being displaced to Pariamanu, but there has not been a surge in Camanti.
Base Map 2. Main mining areas in the south of the Peruvian Amazon. Click to enlarge image.
Base Map 2. Main mining areas in the south of the Peruvian Amazon. Click to enlarge image.

Statement of the Peruvian Protected Area Agency (SERNANP)

El Servicio Nacional de Áreas Naturales Protegidas por el Estado (SERNANP) nos ha comunicado lo siguiente:

  • La actividad de control y vigilancia en la Reserva Nacional Tambopata es permanente y las autoridades (SERNANP, Policía Nacional del Perú, Fiscalías Especializadas en Materia Ambiental, y Marina de Guerra del Perú) continúan interviniendo a todas las actividades de minería ilegal, manteniendo el 100%.
  • Las zonas de amortiguamiento son espacios que están sujetos a la intervención de las autoridades de la Operación Mercurio (no del SERNANP). Se han realizado intervenciones continuas e interdicciones tanto en  las zonas indicadas en el reporte, como en Apaylon y Camanti.
    ,
  • Cabe mencionar que la Operación Mercurio, durante el 2019 y sobre todo en el 2020 (Incluyendo el período de cuarentena) ha ampliado sus operativos mas allá de la Pampa, lo cual explica porque en Camanti las cifras también se ha reducido.  En el segundo semestre de 2020 y en el 2021, se espera que los operativos es amplíen a otras zonas de Madre de Dios.

 

*Notes

 

Acknowledgments

We thank R. Segura, M. Castro, E. Ortiz, M. Silman, M. E. Gutierrez, S. Novoa, H. Balbuena, M. Allemant, and G. Palacios for their helpful comments on this report.

This report was conducted with technical assistance from USAID, via the Prevent project. Prevent is an initiative that, over the next 5 years, will work with the Government of Peru, civil society, and the private sector to prevent and combat environmental crimes in Loreto, Ucayali and Madre de Dios, in order to conserve the Peruvian Amazon.

This publication is made possible with the support of the American people through USAID. Its content is the sole responsibility of the authors and does not necessarily reflect the views of USAID or the US government.

USAID logo

Citation

Finer M, Mamani N (2020) Reduction of Illegal Gold Mining in the Peruvian Amazon. MAAP: