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An Investigation of Illegal Mahogany Logging in Peru's Alto Purús National Park and its Surroundings

Authors:
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An Investigation of Illegal Mahogany Logging in Peru’s
Alto Purús National Park and its Surroundings
January 2005
Chris Fagan and Diego Shoobridge
Correspondence
Chris Fagan: chrisfagan33@yahoo.com
Diego Shoobridge: dspwperu@amauta.rcp.net.pe
Table of Contents
1. SUMMARY ……………………………………………………………………………………….2
2. INTRODUCTION …………………………………………………………………………………3
3. OBJECTIVES ………………………………………………………………………………….…6
4. METHODS ……………………………………………………………………………………….6
5. RESULTS ………………………………………………………………………………………...8
5.1 Illegal Mahogany Logging ………………………………………………………...…….….9
5.1a Access to the Alto Purús ……………………………...….………….…………...…9
5.1b Mahogany logging in the Sepahua–Cujar River region of the park……………….......10
5.1c Mahogany logging in the titled indigenous communities …………………………….12
5.1d Mahogany and CITES ….………………………….……………………………...15
5.2 Uncontacted Indigenous Groups. ………………………………………………………….16
5.2a Encountering uncontacted people in the Alto Purús National Park …………………..16
5.2b A shrinking forest: the last stand for the uncontacted people …………………….…..18
5.2c How many groups of uncontacted people live in the Alto Purús?…………………….20
6. CONCLUSION AND RECOMMENDATIONS ……………………………………………………..21
7. ACKNOWLEDGEMENTS ………………………………………………………………………..24
8. LITERATURE CITED ……………………………………………………………………………25
1
1. Summary
Illegal logging of bigleaf mahogany trees (Swietenia macrophylla) in Peru’s Alto Purús National
Park and adjacent lands continues despite Peruvian laws and international regulations intended to
protect mahogany, indigenous people and conservation areas (see Map 1). This illegal logging is
detrimental to the ecosystem of the Alto Purús region, indigenous communities in the area,
uncontacted indigenous groups and global
biodiversity.
Area of
illegal
logging
Area o
f
illegal
logging
We recommend:
removing immediately loggers
operating in the park
constructing and staffing control
posts on the primary access routes
into the park
monitoring closely the logging
operations in the indigenous
communities northeast of the park
and the forestry concessions along
its western border
creating an independent research
team to investigate mahogany
logging in the region and the
legality of Peru’s mahogany
exports
pressuring importing countries to
reject shipments of illegal
mahogany from Peru
We were also prepared to recommend the
creation of the Alto Purús National Park in
what was formerly the Alto Purús
Reserved Zone, a move being considered
by the Peruvian government at the time of
our investigation. However, the
recommendation became immaterial in
November 2004, when the government
announced the creation of the Alto Purús
National Park, covering 2.5 million
hectares, 93% of the former reserved zone.
Our findings and recommendations are
based on an investigation conducted in
the fall of 2004 in the Alto Purús National Park (the Alto Purús Reserved Zone, at the time), as well
as forestry concessions and indigenous communal lands adjacent to it. The investigation involved
two overflights and four weeks of river travel. Data were collected through personal observations
and a combination of informal and structured interviews with indigenous leaders, government
officials, non-governmental organization (NGO) staff, loggers and local inhabitants.
Map 1: Illegal logging occurs inside the Alto Purús National
Park and the indigenous communal lands outside its borders.
2
2. Introduction
Located in Madre de Dios and Ucayali states, in one of the most remote and inaccessible parts of the
Peruvian Amazon, the Alto Purús region has long been recognized as a conservation priority
nationally and internationally. The region supports numerous endangered plants and animals, such
as the harpy eagle (Harpia harpyja), the short-eared dog (Atelocynus microtis) and the giant river
otter (Pteronura brasiliensis). In addition to being one of the most important and best-preserved
refuges for endemic and endangered species in Amazonia, this vast, pristine wilderness is home to
some of the last nomadic, indigenous people living in voluntary isolation on earth.
On November 20, 2004, after years of debate
among governmental agencies, non-governmental
groups, indigenous federations, the timber
industry and other stakeholders, the Peruvian
government took a great step forward in
preserving the region by creating the 2,510,694-
hectare Alto Purús National Park and the 2
hectare Purús Communal Reserve in what was
formerly the Alto Purús Reserved Zone
02,033-
the
nse
he
ps
————————————
1 2. The
new park becomes Peru’s largest and connects
1.7 million-hectare Manú National Park to the
south with Brazil’s 670,000-hectare Chandless
State Park to the east, forming the largest expa
of strictly protected land in the entire Amazon
basin—an area almost the size of Costa Rica
(Leite-Pitman et al. 2003) (see Map 1b). This
network of protected areas has a forest canopy
that stretches virtually unbroken from beyond t
Brazilian border all the way to the Andes, some
300 kilometers to the southwest, forming perha
the most important wilderness corridor in the
upper Amazon.
Despite this progress, the area—including its
flora, fauna and peoples—is still threatened by
illegal logging of mahogany, which occurs in two
primary places: along the western boundary of the
park and within the titled indigenous communities
northeast of the park (see Map 2).
1 Supreme Decree No. 040-2004-AG
M
ap 1b: The new park is the central link to a huge network
of protected areas on both sides of the Peru–Brazil border.
2 ParksWatch presented results described in this report to Peru’s park service, INRENA, in late October 2004.
ParksWatch was one of many organizations that had been advocating national park status for the Alto Purús. One of the
most significant contributions to these efforts was the book, Alto Purús: Biodiversidad, Conservación y Manejo
published in 2003 by Duke University’s Center for Tropical Conservation and edited by Renata Leite-Pitman, Nigel
Pitman and Patricia Alvarez. The book highlights the region’s remarkable biological and cultural diversity, as well as
human impacts, and provided the scientific justification for making the Alto Purús a national park.
3
Area o
f
illegal
logging
Area o
f
illegal
logging
Map 2: Illegal logging occurs inside the park’s western boundary
and within the indigenous communities northeast of the park.
Unsustainable logging has led to a precipitous decline in bigleaf mahogany (Swietenia macrophylla)
populations throughout Central and South America. In Peru, currently the world’s largest exporter of
mahogany, the range of mahogany has decreased by 50%, and experts estimate that within the next
decade it could shrink by an additional 28% (Kometter et al. 2004). The Alto Purús3 harbors one of
the last remaining stands of commercially-viable mahogany in Peru and Bolivia, and tree density for
mahogany in the Alto Purús is among the highest in Peru (Kometter et al. 2004) (Map 3). With
mahogany still being the highest-valued tropical timber species on the international market, the Alto
Purús has become a hotspot for illicit logging.
This illegal logging occurs despite Peru’s Forestry Law No. 27308 (July 16, 2000), which
established a 10-year ban on mahogany and cedar logging in several watersheds including the Alto
Purús. The trade of the illegal wood violates the Convention on International Trade in Endangered
Species of Wild Fauna and Flora (CITES), which in November 2002 was amended to include
mahogany in its Appendix II list of endangered species (the protections that come with the listing
took effect a year later).
The illegal logging occurs in the region both because its virtually-untapped supply of mahogany is
an attractive target and because weak monitoring of logging activities in titled lands and forestry
concessions adjacent to the park allow loggers to act with impunity.
————————————
3 Henceforth, the “Alto Purús” refers to the entire region—the Alto Purús National Park, Purús Communal Reserve and
adjacent lands.
4
Alto
Purús
region
Map 3: Density (trees/ha) and commercial viability of mahogany in Peru and Bolivia
(Kometter et al. 2004).
The illegal logging affects not only the mahogany population and ecosystem of the Alto Purús, but
also its indigenous peoples, who include nomadic, uncontacted groups4. Loggers have set up
exploitative trade relationships with small indigenous communities in the area just northeast of the
Alto Purús National Park, whereby the indigenous peoples give the loggers permission to cut down
mahogany trees in exchange for extremely-overpriced supplies. Loggers may also be encountering
uncontacted indigenous peoples in the park, leading to situations that often turn violent.
Concerned by reports of illegal logging of mahogany in the Alto Purús, in September 2004,
ParksWatch, in collaboration with the regional government of Ucayali, began a four-week
investigation of logging inside and adjacent to what was then the Alto Purús Reserved Zone. By
documenting this logging activity and its effects, then disseminating our findings, we hoped to spur
efforts to discourage illegal logging and better protect the people and ecology of the Alto Purús
National Park and surrounding lands.
————————————
4 “Uncontaced groups” or “uncontacteds” refers to indigenous people living in voluntary isolation.
5
3. Objectives
The primary objectives of the investigation were to:
document illegal logging activities in the western section of the Alto Purús Reserved
Zone (now the Alto Purús National Park);
gain insight into the legality of logging operations in the indigenous communities located
to the northeast of the park, as well as the forestry concessions on the Sepahua River
adjacent to the park’s western border;
better understand the effects of illegal logging on local indigenous communities,
uncontacted indigenous groups and the biological integrity of the park;
bring international attention to the problem of illegal logging in the Alto Purús in order to
spur actions to mitigate its detrimental effects;
gather information that would strengthen the proposal under consideration by the
Peruvian government to make the Alto Purús a national park; and
provide Peru’s park’s service, INRENA, with information needed to improve
management of the Alto Purús regardless of its eventual protected area category.
4. Methods
The on-site investigation was carried out from September 16th to October 15th 2004. Data were
collected through personal observations and a combination of structured interviews and casual
conversations with local inhabitants, loggers, NGO staff and government employees as well as other
stakeholders. A video camera, print cameras and a Geographical Information System (GIS) were
used in gathering data (see Map 4 for expedition routes).
Data collection began in the city of Pucallpa, the logistical hub for loggers working in the Alto
Purús. In Pucallpa, we chartered a plane to take us to Puerto Esperanza, flying over our planned on-
the-ground expedition route through the park.
Our intention was to traverse the indigenous communities, communal reserve and park by boat and
on foot, beginning in Puerto Esperanza, located within the indigenous communities northeast of the
park, and ending in the town of Sepahua outside the park’s western border. In order to be successful,
we would need to locate a logging road connecting the park with forestry concessions on the
Sepahua River.
The expedition departed Puerto Esperanza in two boats, carrying food, supplies, gasoline and oil for
the entire trip. We hired seven local Sharanahua men as assistants and guides. The first four days
were spent traveling and gathering data on logging activity in the indigenous communities. On the
fifth day we crossed through the communal reserve and entered the park. Five days later on the
Cujar River, a tributary stream of the Alto Purús, and approximately two days from the logging road
where we would begin walking, we unexpectedly came across camps made by uncontacted
6
indigenous people. To avoid any possibility of transmitting diseases to them or a violent encounter,
we turned around immediately and began the long journey back to Puerto Esperanza. The following
day, on our descent, two of our assistants saw two uncontacted men watching us leave from the
river’s edge.
Unable to traverse the entire park and logging road as intended, we decided to return to Puerto
Esperanza and fly to Sepahua with the intention of traveling the logging road from the other side,
stopping short of the area where we encountered the uncontacted people. During the flight to
Sepahua, we took photos and video from the air and recorded GIS data on illegal logging activities.
In doing this, we were able to document illegal logging activity in the park in close proximity to the
area where we found the uncontacted camps. In light of this discovery, we became particularly
interested in gauging the effect, both current and potential, of illegal logging on the uncontacted
people.
In Sepahua, we hired two assistants and one boat and traveled five days up the Sepahua River to the
Quebrada la Unión, the stream where the logging road begins. We spent three days walking the
logging road and interviewing loggers working in the park’s border region before returning to
Sepahua.
Map 4: The routes of the two overflights and two river trips.
7
5. Results
The results of our investigation are summarized here, then explored in more detail in this section.
1. The government ban on mahogany logging is ignored. Peru’s Forestry Law No. 27308
(July 16, 2000) established a 10-year ban on mahogany and cedar logging in several
watersheds including the Purús River, but logging occurs wherever there are mahogany trees
regardless of permits or management plans.
2. Timber from within the Alto Purús National Park is laundered through forestry
concessions on the park’s western side. Management plans for the logging concessions
lack complete inventories of mahogany reserves, so the number of legally harvestable trees
in each concession is not known. As a result, illegal logs from the park are easily mixed with
logs from the concessions, and there is no way to confirm whether the wood was cut in the
concession or the park. While the logs are painted with the name of the concession, without
complete inventories of the concession, or monitoring of logging activities in the
concessions, there is no way to know if the wood is actually from where the logger claims it
is.
3. Alto Purús National Park boundaries are not monitored. We confirmed that there is no
enforcement of park boundaries or monitoring of logging activities in the adjacent forestry
concessions on the Sepahua River to ensure that loggers respect park boundaries.
4. Shipments of timber down the Sepahua River are not effectively monitored. INRENA
monitors the Sepahua River only during the rainy season when, according to one local man,
“the river is so full of logs that you can’t even travel downriver.” However, as we found, in
the dry season loggers are able to transport illegal boards from the park to the city of
Pucallpa without any concern of being asked to show permits or prove that the wood was
legally harvested.
5. There is very little mahogany left in the forestry concessions on the Sepahua River,
according to INRENA and WWF-Peru forestry engineers; therefore, at least some, if not all,
of the mahogany that is transported down the Sepahua River is cut inside the park and not in
the concessions as loggers claim.
6. There is no “ground-truthing” of logging activities in the indigenous communities
northeast of the park. There is no on-the-ground monitoring of logging activities in the
communities. Loggers ignore forestry management plans—if they exist—as well as
community boundaries and any other regulations. And, they often set up exploitative trade
relationships with the indigenous communities when bartering for permission to log their
lands.
7. Air cargos of mahogany from Puerto Esperanza are not effectively monitored. There is
no effective monitoring system to ensure wood leaving Puerto Esperanza by plane has been
legally harvested. Before being loaded onto a plane, each board or log should be checked by
INRENA to ensure that it came from an indigenous community with a proper permit. We
found that wood is not always checked before being transported by plane to Pucallpa.
Furthermore, without any on-site monitoring of the logging camps inside the communities, it
is impossible to verify the origin of the wood.
8
8. Chainsaws are commonly used to cut mahogany logs into boards, a practice illegal in
Peru because it is wasteful.5 According to an official with the Ucayali state government, an
estimated 80% of the mahogany felled in the indigenous communities is cut into boards with
chainsaws.
9. Uncontacted peoples are being harmed by intrusions into the park. We found evidence
that encounters between the uncontacted groups and visitors to the park are occurring more
frequently. These encounters can have tragic consequences for the uncontacteds when the
situations turn violent or the uncontacteds are exposed to foreign diseases.
5.1 Illegal Mahogany Logging
We found evidence of illegal logging inside the Alto Purús National Park’s remote western border
and in the titled indigenous communities outside its northeastern border. The two areas are separated
by over 150 kilometers and involve different logging teams and entirely different circumstances.
The loggers accessing the park’s western section come from adjoining forestry concessions on the
Sepahua and Inuya Rivers. Following small tributary streams, they walk across the hills that divide
the watersheds of these two rivers from those of the Cujar and Curiuja Rivers, tributaries of the Alto
Purús River located in the park. We found that wood stolen from the park’s Cujar River is easily
transported past a logging control post on the Sepahua River. Somewhere along its journey from the
park to Pucallpa, and eventually Lima, it is mixed in with wood legally harvested from the
concessions.
The situation in the titled indigenous communities on the northeastern side of the park is more
complicated. Logging is legal in these communities, but only under certain regulations that ensure it
is done in a sustainable manner. Unfortunately, these regulations are not being implemented. The
logging is done without sound management plans or under the guise of plans developed haphazardly
by the loggers, not the communities. In addition, the system for monitoring the permits and source
of the wood before it is loaded onto planes in Puerto Esperanza is ineffective and, according to local
people, marred by corruption. The illicit logging activity in the communities threatens not only the
mahogany species, but it has fostered a system of egregious exploitation of the indigenous people.
The communal lands provide the loggers with a virtually untapped supply of mahogany, so, at least
for now, there is no reason for the loggers to venture further upstream into the Purús Communal
Reserve or the park.
5.1a Access to the Alto Purús
The only direct access to the Alto Purús is by air to Puerto Esperanza, a modest town of
approximately 600 people located on the Alto Purús River. The town is the capital of the Purús
province within the state of Ucayali. There are no roads nor is it possible to access the Alto Purús by
river from other parts of Peru. The Brazilian border is a one- or two-day trip down the Alto Purús
River from Puerto Esperanza; however, this route is used infrequently for travel or trade. Puerto
Esperanza has a paved airstrip, which is used by small and mid-sized planes from the city of
Pucallpa, located approximately 400 kilometers to the northwest. All flights are chartered, the
majority by loggers, who monopolize travel to and from the region and use these planes to fly
————————————
5 According to Article No. 311 of Supreme Decree No. 014-2001-AG. April 9, 2001, ruling of Peru’s Forestry and
Wildlife Law No. 27308.
9
mahogany out and supplies in. There is an active army base in Puerto Esperanza, and various small
shops sell food and supplies flown in from Pucallpa to town residents, indigenous peoples and now
the burgeoning logging community.
From Puerto Esperanza, the park is accessed by traveling upstream on either the Alto Purús or
Curanja Rivers, through the indigenous communal lands and then the communal reserve (Map 2).
Going up either river, it is a four- to five-day journey to the (eastern) park boundary in a motorboat
with a nine horsepower “peque-peque” engine. Both rivers begin in the hills on the opposite
(western) side of the park.
It is possible, but extremely difficult, to access the park from other directions. For example, loggers
are accessing the park by traveling up the Inuya and Sepahua Rivers and then walking over the hills
that serve as the park’s western boundary. The interior of the park is virtually unexplored, a vast and
untamed wilderness used only occasionally by narcotic traffickers on their way to Brazil and the
uncontacted groups living nomadically there.
5.1b Mahogany logging in the Sepahua–Cujar River region of the park
The Sepahua River and its tributaries form part of the western border of the Alto Purús National
Park. There are twelve forestry concessions along the Sepahua with various levels of activity, four
of which border the park. In most cases, the loggers operating in these concessions are
subcontractors with agreements with the concession owners to extract wood. The concession of
primary interest to us borders the park and has a camp on the Sepahua River at the mouth of the
Quebrada la Unión stream. The camp is the beginning of a logging road that enters the park near the
Cujar River. In previous years, the road has been used by tractors to pull mahogany logs from the
park to the Sepahua River.
The Quebrada la Unión camp was not occupied when we arrived and the tractors had been removed.
The condition of the logging road indicated that the tractors had not been used there since last year’s
cutting season. However, the presence of supplies, including cables used to pull logs, indicated that
the camp is being used as a supply depot for loggers working in the area, and a cleared footpath
along the logging road indicated that loggers are using the road to access the boundary area of the
concession and the park.
The logging road used in the past by tractors to
pull logs from the park to the Sepahua River. An abandoned logging camp on the logging
road near the border of the park.
10
According to local people living on the Sepahua River, the concession owner used the tractors to
extract approximately one million board-feet of mahogany from the area during the previous three
logging seasons. We do not know how much of the wood came from the concession and how much
from the park. However, we do know that in September 2002 there were approximately 300
mahogany logs stacked in the Quebrada la Unión camp awaiting transport. We did not find any logs
at the camp or, for that matter, any live mahogany trees in the concession. There is not enough
mahogany left in the concession to make a large-scale operation possible or the use of the tractors
economically viable.
We interviewed an indigenous Amahuaca woman who had recently returned from a logging camp
located inside the park where she worked as a cook. The camp belongs to the owner of the Quebrada
la Unión concession mentioned above. Several informants that we interviewed on the Sepahua River
told us that with mahogany trees now scarce within the concessions, loggers have begun cutting
inside the park where mahogany is still abundant and its extraction economically viable despite high
transportation costs.
We also interviewed two loggers who were part of a team based at Quebrada la Unión cutting
mahogany in the park. Two weeks before our arrival, twelve of their colleagues traveled down the
Sepahua on five rafts of mahogany boards cut with chainsaws from trees in the park. The mahogany
rafts passed through the town of Sepahua and were loaded onto boats bound for Pucallpa. The
passing of these rafts was confirmed by local people living on the river, as well as the caretaker for
the otherwise abandoned INRENA logging control post.
The forestry control post and logs on the Sepahua River.
This forestry control post along the Sepahua River was one of two in the area that were built in
November 2003 as a joint project among WWF-Peru, the non-governmental organization
Conservation of the Cutivireni Patrimony (ACPC) and INRENA. The other, which was located on
the Inuya River, was burned down by loggers in May 2004. The post on the Sepahua River is
supposed to be staffed by INRENA personnel who check permits and verify the sources of wood
floating downstream from the forestry concessions located upstream near the park. However, no one
from INRENA was at the post during our investigation, and according to the caretaker, they had not
visited the post for over four months. INRENA personnel in the town of Sepahua, located several
days travel downstream from the control post, confirmed that they would not occupy the control
post until the rainy season begins and the river becomes high enough for the loggers to transport
whole logs. They were not aware that rafts made out of mahogany planks cut in the park had passed
by the post two weeks earlier or of an illegal logging camp in the park near the headwaters of the
Sepahua River.
11
During an overflight of the border area between the Sepahua River and the park, we located a
logging camp on a small tributary of the Cujar River well within the boundaries of the park (S 10 °
57.266’ – W 072° 21.854’). The camp included a cleared area of several hectares, which we assume
was to become a garden for the loggers and a center of operations. There appeared to be a shelter
and several stacks of boards on the side of the clearing. The camp proves that logging is occurring
inside the park, and anecdotal evidence we collected from local people and the loggers indicates the
likelihood of other similar camps inside the park. According to local people, some logging camps
are also used as production centers for narcotics, which are transported through the park to Brazil.
An illegal logging camp in the western section of the park.
Loggers are also extracting wood from other rivers inside the park’s western border, according to
our informants. A pilot for a local mission informed us that he has seen a significant amount of
logging activity in the Inuya-Curiuja River region. Future investigation of this section of the park is
necessary.
5.1c Mahogany logging in the titled indigenous communities
The cultural diversity of the Alto Purús is staggering. Approximately 80% of the population of 3000
belongs to eight distinct indigenous groups (Cashinahua, Sharanahua, Culina, Mastanahua,
Amahuaca, Chaninahua, Asháninka and Yine) living in 31 communities within the titled communal
lands located northeast of the Alto Purús National Park. The communities vary in size from
approximately five to 30 families. The Cashinahua are the largest group followed by the Sharanahua
and the Culina. The remaining 20% of the population is primarily mestizos, and to a lesser degree
Brazilians, living in Puerto Esperanza.
Logging activity in the indigenous communities has increased dramatically since ParksWatch last
evaluated the Alto Purús in July 2002 (Fagan and Salisbury 2003). At that time, mestizo loggers
with chainsaws were new arrivals to the region, and only a handful of communities had begun to sell
their trees to the loggers. Since then, several communities have allowed mestizo loggers financed by
large international timber companies to set up operations in their lands. The town of Puerto
Esperanza has been transformed into the hub of logging operations occurring upstream. The only
species logged other than mahogany is cedar (Cedrela spp.); however, according to local officials,
close to 100% of the wood that is transported from Puerto Esperanza to Pucallpa is mahogany
because air transport of cedar or any other species is not economically viable.
12
Logging is legal in the communal lands with proper permits from INRENA’s forestry sector.
Permits ensure that the logging is done in a sustainable manner, with proper management plans and
participation on behalf of the communities.6 However, the question of whether the loggers have
valid permits, or if they are working under legitimate management plans, is actually quite irrelevant
because the loggers do not abide by any regulations once they are upstream in the communities.
Much of the logging activity three years ago had been in the Sharanahua indigenous communities on
the Alto Purús River—communities such as Gastabala and San Marcos. However, according to the
Sharanahua community leaders, they grew tired of being exploited by the loggers and instead have
decided to work with WWF–Peru to develop legitimate management plans for their land. They will
begin logging again once the management plans are finished and the permits issued.
Three of the 31 communities in the region have legal permits. They are the Cashinahua communities
of Miguel Grau, Curanjillo and Colombiana located on the Curanja River. However, according to
local officials, once upstream, the loggers work wherever there are mahogany trees regardless of
permits or community boundaries. The loggers use the existing permits to launder wood extracted
from communities without permits. In the three communities with permits, the management plans
are not being followed. Furthermore, even if they were followed they do not ensure sustainability. In
a rush to obtain permits and extract the wood, the loggers develop the management plans on behalf
of the communities in a haphazard manner in a matter of days. In comparison, management plans
being developed for other communities working with WWF–Peru take upwards of two to three
months to develop.
A felled mahogany tree in the community of
Colombiana (left) and cut mahogany boards (above)
(photos from 2002).
The logging companies no longer hire men from the communities to cut the trees as they did in
2002. Now they bring their own teams of loggers to do the work. The loggers arrive at the
communities offering advanced payments of various goods in exchange for the wood. The loggers
————————————
6 According to Title V, Chapter VI, Subchapter VII of Supreme Decree No. 014-2001-AG. April 9, 2001, ruling of
Peru’s Forestry and Wildlife Law No. 27308.
13
then travel to the town of Atalaya to buy logging permits on behalf of the communities because
community leaders cannot afford the cost of air travel. The cost of the permits are inflated and added
to the communities’ debt. The community leaders reach agreements with the loggers to cut a certain
number of mahogany trees over a given period of time. However, once the camps are established,
the loggers do not leave the communities until all the mahogany trees have been cut, continuously
making new agreements with the community leaders to harvest more trees. The agreements are
based on the exchange of mahogany for food and other supplies, such as sugar, salt, shotgun
cartridges and plastics. The loggers inflate prices of supplies, and usually the community members
are given the supplies before the cutting begins, perpetuating their debt. Trees are cut until the
communities have paid for the supplies based on the inflated prices.
The prices that the loggers pay the community leaders for the wood are a fraction of market price.
Loggers offer between 10 and 50 Peruvian centavos (6 – 15 U.S. cents) per board-foot of mahogany
in the communities. The sawmills in Puerto Esperanza pay significantly more (4.00 soles or 1.33
U.S. dollars) per board foot; however, not all the communities possess the chainsaws or motorized
boats to transport the wood from their communal lands to Puerto Esperanza, so they are forced to
accept the logger’s offer. Money rarely changes hands; the loggers simply deduct the cost of the
mahogany from the debt the communities owe for the permits or the food and supplies they were
given in advance—at outrageously inflated prices. As of October 2004, the price of mahogany per
board foot was 9.00 soles (3.00 U.S. dollars) in Pucallpa, 12 soles (4.00 U.S. dollars) in Lima, and
18.00 – 20.00 soles (6.00 – 6.66 U.S. dollars) in the United States. In the end, the communities
receive between 100 and 200 Peruvian soles, or 30 – 60 U.S. dollars, for one mature mahogany tree
worth several thousand dollars on the international market.
The difficult access to and from Puerto Esperanza would seem to facilitate the monitoring and
control of wood leaving the region. However, the large majority of planes are chartered from the
military by loggers and ultimately the loggers control the transport of people, supplies—and wood—
between Puerto Esperanza and the rest of Peru. Illegal mahogany leaves Puerto Esperanza without
proper monitoring by authorities whose offices are just a stone’s throw from the landing strip.
During the four days we spent in Puerto Esperanza, the office of INRENA’s Forestry Division
remained closed. Freshly cut mahogany boards were transported from the sawmills to the airstrip
without any discernible monitoring by local officials. It is a commonly held belief that INRENA’s
Forestry Division’s monitoring efforts are marred by corruption. Local people do not believe that
INRENA is enforcing the laws intended to protect mahogany and ensure the sustainable use of the
resources within the indigenous communities. At risk is not only the future of mahogany, but also
the future of the indigenous inhabitants and their children, who become poorer with each extracted
mahogany tree. Unfortunately, logging is one of the only ways for local people to earn money or
supplies, which they desperately need, so they are forced to accept the prices and conditions set by
the loggers.
14
Mahogany boards being transported to the airstrip in Puerto
Esperanza (left). A Naval plane chartered by loggers to
transport wood from Puerto Esperanza to Pucallpa (above).
5.1d Mahogany and CITES
A large portion of the mahogany logged in the Alto Purús region is most likely exported to the
United States and Europe, and thus protected under CITES regulations meant to protect endangered
species from international trade forces.
In 2001, 30 – 40% of Peru’s mahogany exports were illegal (Traffic 2001). This figure is
undoubtedly much greater today as most commercially-viable trees are in protected areas (Kometter
et al. 2004). The logging giant Bozovich, the largest exporter of Peruvian mahogany to the United
States, is operating in both the Sepahua River basin and in the indigenous communities northeast of
the park. According to WWF–Peru staff in Sepahua, Bozovich is the largest timber company active
in the Sepahua River concessions, and “almost all the mahogany from the Sepahua River goes to the
United States.” A local sawmill operator in Puerto Esperanza, and an official with the Ucayali state
government and former logger, estimate that 70 – 90% of all mahogany from the titled indigenous
lands is exported to the United States.
According to Manúel Sobrol Filho, Executive Director of the International Tropical Timber
Organization (ITTO), “The inclusion of S. macrophylla in Appendix II of CITES imposes exporting,
importing and monitoring requirements on the species, which should be linked to its sustainable
management in natural forest habitats” (ITTO 2004). The listing is intended to protect the species
from overexploitation as a result of international trade and to ensure that the trade is sustainable. As
such, exporting countries, like Peru, must verify that mahogany shipments are not detrimental to the
survival of the species (CITES 2002). Mahogany can be exported legally only if it receives a “non–
detrimental” finding from the Peruvian Scientific Authority. However, in April 2004, the Peruvian
Scientific Authority and the Peruvian government acknowledged that non-detriment findings have
not been made for mahogany, and furthermore that the government lacks the capacity to do so
(Hershowitz and Muffett 2004). Yet, despite this admission, the government continues to enable the
exportation of mahogany by issuing CITES permits for mahogany, an obvious contravention of this
international accord. Additional research is needed to determine where along the chain-of-custody,
from stump to market, the exporters are obtaining export permits for wood so obviously out of
compliance with CITES criteria.
15
Based on the evidence that we have provided, Peruvian mahogany is not being managed in a
sustainable manner, and is not in compliance with the non-detriment finding as mandated by
Appendix II of CITES. However, it continues to be exported, primarily to the United States and
Europe where it is received by importers and furniture makers. In 2002, 85% of the mahogany sawn
wood exported by Peru went to the United States (ITTO 2004). Undoubtedly, the United States
government and importers, and less so those of the European Union, deserve part of the blame for
ignoring CITES trade regulations meant to protect endangered species. If mahogany is to be
conserved, importing countries must uphold their responsibilities to enforce CITES regulations.
5.2 Uncontacted Indigenous Groups
There are two uncontacted indigenous groups known to use the Alto Purús as part of their seasonal
migratory routes. The smaller group is locally referred to as the Curanjeños because they live in the
headwaters of the Curanja River with a migratory route to the north towards the headwaters of the
Embira River in Brazil. After many years of infrequent sightings by the native Cashinahua
communities on the upper Curanja River, a small group of Curanjeños is now in sporadic contact
with members of the Pioneer Mission, a Protestant evangelical group headquartered in the United
States. The Pioneers are also interested in contacting and Christianizing the Mashco-Piro, the larger
and more mysterious of the two uncontacted groups.
The Mashco–Piro, or simply the “Mashco” are believed to be in constant movement between the
upper stretches of the Alto Purús River and the Las Piedras and Manú Rivers to the south. The
evidence suggests that they visit the Alto Purús during the driest parts of the year (primarily in June
and July) to collect the Izana plant (Gynerium sagitatum) to make arrows. Another possibility is that
they visit to collect the eggs of the Taricaya turtle (Podocnemis unifilis), which are laid on the
exposed beaches when water levels are low during the dry season.
Not much is known about the effect of illegal logging on the lives of these uncontacted people. One
reason may be that loggers are reluctant to report encounters with uncontacteds that occur in
protected areas. However, we do know that the immune systems of the uncontacted groups are
susceptible to the unfamiliar viruses brought by outsiders, with many such encounters leading to
viral outbreaks and, subsequently, death of indigenous peoples (Schulte-Herbruggen and Rossiter
2003). Another threat is that loggers deplete local game populations, which are the primary protein
sources for the uncontacted people. Most distressing, however, are violent encounters between the
uncontacteds and loggers or other travelers. Our findings indicate that the majority of recent
encounters in the Alto Purús have resulted in the death of uncontacted people.
5.2a Encountering uncontacted people in the Alto Purús National Park
While encounters with the Mashco are very rare, we were acutely mindful of the possibility, albeit
small, of encountering them in the park. However, the unanimous opinion among our assistants and
other local people was that it was already too late in the dry season for the Mashco to still be in the
area. That said, we were aware that their migratory routes often change from year to year, and there
was no guarantee that they were not still in the area. Thus it was with the utmost caution that we
proceeded through the titled indigenous lands and the Purús Communal Reserve and into the park
towards the logging road and area of reported logging activity.
Nine days after leaving Puerto Esperanza and approximately three days from the logging road, we
found a camp used by the Mashco. The condition of the brown, desiccated palm leaves used to make
the shelters indicated that it had been used two or three months earlier. The camp consisted of 30
16
separate shelters grouped together on either side of the river. There were individual shelters slightly
upstream and downstream from the main camp, presumably used as lookouts. We assumed that two
adults shared each shelter and therefore estimated that the group numbered approximately 60 adults.
Each shelter had the remains of a campfire. Scattered around the fires were bones of capybara
(Hydrochaeris hidrochaeris) and tapir (Tapirua terrestris) and shells of motelo turtles (Geochelone
denticulata), among other unidentified animal remains. Also found were three manufactured items: a
plastic plate, an old, burned tuna can and a small piece of red fabric tied to one of the several, old
leaf-woven baskets. Marks on bones and bamboo indicated that the inhabitants had at least one
machete.
Evidence of the two- to three-month-old
Mashco camp.
The presence of the camp confirmed that the Mashco used the area during the peak of the dry
season. With the rainy season already underway, we assumed that they had left the area and we
continued traveling upstream towards the logging road. Later that same day, by chance, we observed
a muddy trail of human footprints leading up the riverbank and into the forest. On the top of the
riverbank, barely discernable among the dense vegetation, was a group of six shelters. Each had a
campfire and bedding made out of leaves. They were similar to the shelters we had found earlier that
morning, however the condition of the shelters and the presence of raw meat on a cracked turtle
shell implied that the camp had been used within the past few days. We stayed for only a few
minutes and then began floating downstream (the direction from which we had come), without
starting the motors.
Within minutes, we heard distinct sounds coming from the forest, which our assistants identified as
the Mashco calling to one another by mimicking the call of the spider monkey. We started the
motors and headed downstream as fast as possible. The following morning, approximately eight
hours of travel from where we heard the calls of the Mashco the day before, we began hearing
similar sounds in the forest. As we traveled a bend in the river, two members of our group saw two
men emerge from the dense riverbank and watch us leave. The assistants identified the two men as
Mascho. Given our location, we surmise that the two men were members of a separate and friendly
sub-group of the group we heard the day before and traveling at a different pace.
17
Evidence of the recently made Mashco camp.
While we were disappointed to abandon our plan to traverse the entire park and travel by foot over
the logging road to the Sepahua River, the decision to change plans was relatively easy. We were
not going to risk a face-to-face encounter, which could have led to violence or the transmission of an
infectious disease to the Mashco. Our Sharanahua assistants, several of whom had encountered the
Mashco in recent years, believed that, instead of avoiding contact, as was the norm in the past, the
Mashco had begun reacting aggressively to intrusions. The opinion among our assistants was that
the Mashco were avenging deaths from skirmishes with illegal loggers. This belief had fostered a
feeling of intense anxiety towards the Mashco on behalf of the Sharanahua men. Rather than risk an
aggressive reaction to a face-to-face encounter, from either the Mashco or our Sharanahua assistants,
we decided to turn around and leave the area.
5.2b A shrinking forest: the last stand for uncontacted people
Any explanation for why we encountered the Mashco so late in the dry season is purely speculative.
As our guides suggested, it is possible that because the rainy season had been late in developing, the
Mashco were waiting for the heavy rains to begin before continuing on their migration. While that
may very well be true, it is also possible that they have been forced to change their migratory
movements to spend more time in the park because of encroachment by loggers in the lands
surrounding the park. Clearly, the area of undisturbed forest is shrinking. The area northeast of the
park contains the titled indigenous communities; inside the park’s western border there is localized
logging on the Cujar and Curiuja Rivers, with widespread logging occurring further to the west in
the forestry concessions on the Sepahua, Inuya and Mapuya Rivers; and to the southeast there is
extensive logging activity in the Las Piedras River basin.
In the only study done on the impact of illegal logging on uncontacted groups in the Alto Purús
region, Schulte-Herbruggen and Rossiter (2003) documented 176 illegal logging camps along the
Las Piedras River in the southeastern portion of the Alto Purús National Park and the adjacent State
Reserve for Indigenous in Voluntary Isolation. These loggers reported 18 separate encounters with
uncontacted people in 2001 and 2002. Overall, 17.3% of all the loggers interviewed had encountered
uncontacted people, and the number of encounters increased by 600% from 2001 to 2002.
During our investigation we collected testimony from local people regarding encounters with
uncontacted groups in the headwaters of the Alto Purús and Sepahua Rivers in or near the park. All
of the encounters occurred in 2001 and 2002, and all but one resulted in violence. The following are
excerpts from the testimonies.
18
In February 2001, Sharanahua and Mashco men fought at the mouth of the Santa Cruz
stream on the Alto Purús River. A group of local loggers arrived at a tree they had cut
several days earlier on the Santa Cruz stream to find numerous human footprints, so the
loggers left the area. Later that day, a group of approximately 100 Mashco men and women
arrived at a small settlement at the mouth of the stream and began killing domesticated
animals and destroying a house. After watching the events for several hours from the other
side of the river, two Sharanahau men poled their canoe to the middle of the river and fired
their shotguns at the Mashco. Two Mashco were killed and their bodies carried into the
forest by other members of the group. According to the man who shot them, the Mashco
visited the area each dry season to take peanuts from his garden and there had never been
any violence. He suggested that they acted aggressively this time because they were angry
about the mahogany logging taking place in the forest along the Santa Cruz stream. For a
detailed account of this encounter see Shoobridge (2001).
In July 2002, the catholic priest from Puerto Esperanza and a local guide attempted to travel
from the Alto Purús to the Sepahua River to investigate the route for a potential road to
connect the Alto Purús with the rest of Peru. They turned around because of the presence of a
group of Mashco. According to his guide, the Mashco saw the two men but did not react
aggressively.
In July 2002, a few days after the encounter described above involving the catholic priest,
four narcotic traffickers encountered what is believed to be the same group of Mashco on the
upper Alto Purús River. A fight ensued in which two of the drug traffickers were killed and
the other two escaped into the forest. The bodies of the dead traffickers were never found,
and it is not known if any of the Mashco were killed.
In May 2002, on the upper Sepahua River near the logging road, three native Amahuaca men
fought with a group of uncontacted people. According to one of the Amahuaca men, he was
attacked while fishing with his wife. They escaped unharmed, and he returned with two other
men and followed the uncontacted group into the forest where they were camped. The
Amahuaca men killed four of the uncontacteds in the subsequent fight. It is likely that this
group if uncontacteds were not Mashco but a different group (see discussion below).
The Sharanahua and Amahúaca men living close to the park believe that there has been a marked
change in posture of the Mashco in recent years, from one of avoidance to one of aggression. As one
of our assistants explained:
“When we worked on the Alto Purús and Cujar Rivers in the 1970’s and 80’s collecting animal
skins, occasionally we would see the Mashco and they would always avoid us and run away. There
were never any problems. Now it is different. They shoot arrows at us and want to kill us to take our
things.”
Local people blame the supposed change in the Mashco’s behavior on the arrival of the loggers
working in the park and surrounding lands. Several local men who have encountered the Mashco in
the past, believe that the Mashco have become more aggressive in order to protect their shrinking
territory and avenge murders by loggers. In a 2003 study of encounters in the Alto Purús, Michael
and Beier found that in at least 10 encounters before 2001, the Mashco showed no signs of
19
aggression but instead retreated in every instance. The evidence indicates that the increase in violent
encounters involving the Mashco coincides with the arrival of loggers to the region.
The testimonies we collected about the four encounters seem to support the belief among local
people living near the park that the Mashco have a new willingness to fight instead of flee, as was
the norm in the past. However, it is not entirely clear who initiated the violence; in fact, the notion of
a more violent Mashco is contradicted by our own encounter with them. Despite hearing our motors
and having ample opportunity to react aggressively to our presence, the Mashco chose not to
confront us and instead let us leave peacefully. We believe that the increased number of violent
encounters involving the Mashco can be at least partly attributed to the anxiety that local people and
loggers feel towards the Mashco. Their deep fear of the Mashco has fostered a propensity to react
quickly—and violently—to any signs of aggression from the Mashco.
Regardless of why more violence is occurring, any willingness by the uncontacted groups to fight
will ultimately prove disastrous. Although they are skilled hunters, their bow and arrows are simply
no defense against shotguns. As illegal loggers continue to view the Alto Purús National Park as a
lawless frontier ripe for the taking, the survival of the Mashco and other uncontacted groups in the
Alto Purús is in jeopardy.
5.2c How many groups of uncontacted people live in the Alto Purús?
The evidence suggests that there were two different groups of uncontacted people involved in the
encounters described above. The participants in the first three accounts describe the uncontacteds as
Mashco. The men had long hair hanging down their backs tied in a headband; they wore red paint
and ornaments on their arms and legs and penis straps. The two men our assistants saw during our
trip match this description.
However, the Amahuaca men involved in the fourth encounter on the Sepahua River near the
logging road and the boundary of the park, inspected the bodies of the four men they killed, and
their descriptions do not match those given for the Mashco. The men they killed were very tall, with
long beards and substantial body hair. In addition, their skin had a yellowish color that was not
paint. The Amahuaca men believe that the uncontacted group they fought with was not Mashco but
an entirely different group, given their very aggressive nature and unusual appearance. Among the
possessions left by the uncontacted group, the Amahuaca men found a heavy metal pot that is
typical of those made in Brazil. The Amahuaca reasoned that the group was from Brazil, possibly
from the Embira River region.
A third group, the Curanjeños, live in the park in the headwaters of the Curanja River. A small
group of them have some contact with the evangelical Pioneer Mission. It is not known whether they
will choose to leave the forest for settled life in the near future.7
————————————
7 According to the Sharanahua man who is working as a translator for the Pioneer missionaries (the Sharanahua speak a
similar dialect to the Mastanahua language that the Curanjeños speak), he has conversed with a group of three
Curanjeños six times over the past year. From these conversations, he has learned that the Curanjeños are a small group
that lives in fear of the larger Mashco group. The missionaries are now learning Mastanahua in order to communicate
directly with the Curanjeños. It is possible that they intend to learn as much as possible from the Curanjeños with the
ultimate goal of contacting the more mysterious and “uncivilized” Mashco.
20
6. Conclusion and Recommendations
The Alto Purús National Park will not be consolidated overnight. The logging industry is fueled by a
powerful demand for mahogany in the world’s richest countries, primarily the United States and in
Europe. As local populations of mahogany are depleted throughout other parts of Amazonia, the
amount of pressure that loggers put on the Alto Purús and nearby protected areas in the region will
increase. The future of the Alto Purús as a viable protected area—and the future of the uncontacted
people that regard it as their home—depends on strict enforcement of the park’s boundaries and
thorough monitoring of logging operations on adjacent lands. In addition, importing countries need
to do their part to reduce the demand for illegal mahogany from Peru. We offer the following
recommendations for consolidating the Alto Purús National Park and preventing the continued
illegal logging of mahogany in the region.
1. Remove the loggers currently operating inside the park
Illegal logging is occurring inside the western border of the park in close proximity to uncontacted
indigenous groups. We call for the immediate removal of loggers operating in the Sepahua–Cujar
River region. Unsubstantiated reports of logging in the Inuya–Curiuja River region and the Mapuya
River should be investigated immediately. According to our information, the extent of illegal
logging on the Las Piedras River has decreased since 2003 when new control posts were
constructed; however this area should also be investigated. In addition, there is evidence of Peruvian
loggers working along the Brazilian border that may be approaching the park from the Yurúa and
Breu Rivers. This, too, needs to be investigated.
2. Restrict access to areas of the park used by uncontacted indigenous groups
Our investigation proves that at least one uncontacted group, the Mashco, still uses the Alto Purús as
part of their migratory route. In addition, the testimony we collected on the Sepahua River indicates
that an additional group, quite possibly from Brazil, used the region as part of its migratory route in
2002 and could do so again in the future. Evidence of logging activity inside the park and on
adjacent lands indicates that the territory available to these nomadic tribes is shrinking. Furthermore,
an increase in the frequency of violent encounters involving the uncontacteds coincides with the
arrival of loggers in the region, and many of these encounters have had tragic consequences for the
uncontacted people.
We recommend that the park’s Cujar and Curiuja Rivers be declared an area of strict protection in
order to reduce the likelihood of encounters with the Mashco. Only local indigenous people, who
occasionally travel through the park to the Sepahua River basin, should be allowed to access these
areas. In addition, missionary work should not be allowed inside the park or communal reserve.
3. Build control posts on the five rivers that serve as the primary access routes to the park
The limited number of access routes to the park will facilitate the control of its borders. Our
recommendations regarding control posts are similar to those described by Leite-Pitman and Pitman
(2003). The priority use for park funds should be spent on building and staffing control posts on the
park’s boundary on the five rivers that serve as the primary access routes to the park—the Alto
Purús and Curanja in the northeast, the Las Piedras in the southeast and the Sepahua and Inuya in
the west. In addition, the effectiveness of the control post in the town of Puerto Esperanza—where
all the wood from the communities leaves via plane—needs to be improved significantly. Additional
21
posts within the forestry concessions on the Sepahua, Inuya and Las Piedras Rivers are needed to
ensure the legality of logging activities in the concessions; however, these posts are of secondary
importance to the five posts to be located on the park’s border.
Alto Purús River:
A new control post should be built on the border of the communal reserve and the park in order to
monitor all access to the park from the Alto Purús River. Once this post is operational, and if
funding allows, a second post should be built to monitor use of the communal reserve. The best
located for this second post is at the abandoned INRENA camp called Caobal. The camp was used
by INRENA’s forestry sector to collect mahogany seeds for reforestation projects but has been
abandoned for several years. It is strategically located inside the communal reserve between the
boundary of the park and the community of Monterrey, an excellent location for monitoring use of
the communal reserve by local people and other visitors.
Curanja River:
As with the Alto Purús River, the ideal scenario is to build two posts on the Curanja River to
monitor both the park and communal reserve. However, the priority should be to construct a post on
the border of the communal reserve and the park in order to monitor all access to the park from this
river. If funding is available, a second post should be built to monitor use of the communal reserve.
The best location for this second post is the border of the communal reserve and titled communal
lands near Puerto Paz, a small settlement being used by the Pioneer Mission to contact the
Curanjeños indigenous group.
Sepahua River:
The existing control post on the Sepahua River should be staffed year-round in order to prevent the
transport of illegal wood during the dry season. However, it is more important to build a new control
post upstream near the Quebrada la Union logging camp in order to control access to the park and to
monitor logging activity in the four forestry concessions in the vicinity that border the park.
Inuya River:
A post needs to be built near the border of the park in order to control access to the park and monitor
logging activity along its border. In addition, the post that was burned down in May 2004 should be
rebuilt and re-staffed. As with the Sepahua River, this post is needed to monitor the legality of wood
being transported from the forestry concessions located upstream.
Las Piedras River:
The existing control post should be staffed year-round. The current status of logging activity in this
region should be investigated to determine if a second post is needed on the border of the park and
the forestry concessions.
Puerto Esperanza:
A stronger presence in Puerto Esperanza is necessary to control the flow if illegal wood from the
indigenous communities to Pucallpa via plane. The existing INRENA office there needs to be
staffed full-time by senior level personnel.
4. Implement frequent and thorough monitoring of the forestry concessions on the Sepahua
River
22
Management plans need to be developed and implemented in the forestry concessions along the
Sepahua River as a first step towards ensuring that mahogany trees are being managed in a
sustainable manner and in accordance to Peruvian and international laws. Frequent and thorough on-
site inspections of the concessions will encourage concessionaires to implement the management
plans. The plans must include complete inventories of mahogany trees in order to stop the mixing of
wood from the park with that from the concessions. Of particular importance are the four
concessions that border the park.
5. Develop a new committee under the Indigenous Federation of the Alto Purús
(FECONAPU) to oversee and monitor logging activities in the indigenous communities along
the Curanja and Alto Purús Rivers
The committee should be coordinated by FECONAPU, which has a vested interest in the
sustainability of mahogany reserves in the communal lands. The committee will work to ensure that
logging in the communities is being done in a sustainable manner, with proper management plans
and legal permits and in compliance with Peruvian and international laws. In addition, it will report
any exploitative business transactions between the loggers and the indigenous people. The on-site
inspections should be conducted in collaboration with INRENA.
6. Assist PIMA in the development of a FECONAPU committee to monitor use of the new
communal reserve and park
The park and communal reserve are managed by PIMA (the Participation of Native Communities in
the Management of Natural Protected Areas), an INRENA project with funding from the Global
Environmental Facility. PIMA’s success at enforcing new boundaries and regulations will depend a
great deal on their ability to involve the local communities in the process. PIMA’s monitoring team
should include representatives from the local indigenous communities located near the communal
reserve and park. These “park guards” should be placed at the control posts on the Curanja and Alto
Purús Rivers as well as in Puerto Esperanza.
7. Create an independent research team to work in collaboration with Peru’s CITES
Scientific Authority to investigate the management of logging concessions in the region and the
legality of Peru’s mahogany exports
Peru’s 2000 forestry law mandated an independent forest control and supervision agency for
auditing forest concessions and for the chain-of-custody tracking of mahogany logs. However, the
agency has not been developed. An independent agency will help remove any corruption from the
monitoring activities. The group should begin by focusing on the logging concessions bordering the
Alto Purús National Park to the south and west.
8. Develop publicity campaigns to raise awareness of the environmental and social impacts of
illegal logging of mahogany in Peru and to pressure importing countries to reject shipments of
mahogany from Peru
Timber importers, furniture makers and consumers need to be made aware of the harmful impacts
associated with illegal mahogany logging in Peru. Importing countries, primarily the United States
and the European Union, should be pressured to reject imports of mahogany from Peru until the
Peruvian government can ensure that its wood is in compliance with international trade laws as
mandated by CITES.
23
7. Acknowledgements
We would like to thank the Intendencia de Áreas Naturales Protegidas del Insituto Nacional de
Recursos Naturales (INRENA) and Jhonny Aysanoa Lopez and Ricardo Jon Llap; Javier Balbin
Durand of Fondo Mundial para la Naturaleza – Peru (WWF – Peru); Jorge L. Herrera Sarmiento and
Reynaldo Tuesta Cerron of Proyecto de Participacion Indigena en el Manejo de Areas Protegidas
(PIMA); Josefina Takahashi of Sustenta; Lelis Rivera of the Centro para el Desarrollo del Indígena
Amazónico (CEDIA); Jaime Del Aguila of the Federacion de Comunidades Nativas del Rio Purús
(FECONAPU); Sydney Hoyle de Vega and the Government of Ucayali Province; Roy Hoyle de
Vega; María Del Carmen Alvarez, Edgar Alzamora and Orializ Olivera of the Asociación Navarra
Nuevo Futuro; Don Pancho; field assistants and guides Jorge Del Aguila, Raul Silvano, Moises
Fernandez, Alfredo Melendez, Mario Melendez del Aguila, Sebastian Olivera Montes, Manuel
Olivera Bardales, Alberto Olivera Olivera, Pasqual and Mateo; Nicolas Salcedo, mayor of Sepahua;
Aeroandino and Alas de Esperanza airlines; reviewers Sara Ashenberg, Ted Gullison, Martha
Martinez, Harold Beck and James Todd; and cartographer David Salisbury.
24
8. Literature Cited
CITES (Convention on International Trade in Endangered Species of Wild Fauna and Flora). 2002.
Amendments to Appendices I and II of the Convention adopted by the Conference of the Parties in
Santiago, Chile, from 3 to 15 November 2002. CITES, Geneva, Switzerland. Available online at:
http://www.cites.org.common.cop/12/appendix_notice.PDF.
Fagan, C., and D. Salisbury. 2003. Uso de la Tierra y Actividades Economicas en Cinco
Comunidades Indigenas de la Provincia de Purús. Pages 177 – 189 in R. Leite-Pitman, N. Pitman,
and P. Alvarez, editors. Alto Purús: Biodiversidad, Conservation y Manejo. Center for Tropical
Conservation. Durham, North Carolina.
Hershowitz, A., and C. Muffet. 2004. NRDC and Defenders of Wildlife write to European
Commission detailing concerns about the continued importation of mahogany from Peru in violation
of CITES. Available online at:
https://www.peruforests.org/news/NRDC_Defenders_EU_mahogany12_04.pdf
ITTO (International Tropical Timber Organization). 2004. Making the mahogany trade work.
Report of the workshop on capacity-building for the implementation of the CITES Appendix-II
listing of mahogany. ITTO Technical Series 2004.
Kometter, R. F., M. Martinez, A. G. Blundell, R. E. Gullison, M. K. Steininger, and R. E. Rice.
2004. Impacts of unsustainable mahogany logging in Bolivia and Peru. Ecology and Society 9(1):
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Biodiversidad, Conservation y Manejo. Center for Tropical Conservation. Durham, North Carolina.
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del Alto Purús. Pages 149 – 162 in R. Leite-Pitman, N. Pitman, and P. Alvarez, editors. Alto Purús:
Biodiversidad, Conservation y Manejo. Center for Tropical Conservation. Durham, North Carolina.
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investigation into the impacts of illegal logging activity in Las Piedras, Madre de Dios, Peru.
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macrophylla in Bolivia, Brazil and Peru. Available online at:
http://www.traffic.org/mahogany/legis.html.
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... While the socio-environmental impacts of selective logging upon an indigenous community and indigenous responses have been documented for the Alto Tamaya (Salisbury 2007;Salisbury et al. 2011), the lack of peer-reviewed literature concerning the local social and environmental impacts of mahogany logging upon Peruvian indigenous communities is striking. Chris Fagan and Diego Shoobridge (2005; highlighted the problems of mahogany extraction in the Alto Purús region through reports of ParksWatch 1 and Round River Conservation Studies 2 , but no peer-reviewed study has documented the extraction of mahogany from the indigenous perspective for the region. ...
... While mahogany serves as a premier wood for boat building within local communities and may be used as a local construction material, it is one of the most coveted and expensive woods on the international market. Depletion of mahogany stocks throughout Latin America led to a boom in extraction of the resource in Purús (Fagan and Shoobridge 2005;. The commercial value of the species depends upon available supply, costs of cutting, labor, transport, export, and finally, processing as a value-added product. ...
... From 2000-2008, there was a marked increase in mahogany extraction in southeastern Peru, which might be characterized as a "boom." The indigenous communities of the Purús and Curanja rivers were active, if unequal, participants in this boom (Fagan and Shoobridge 2005;. 3) Produce maps made by inhabitants of the region's indigenous communities. ...
... Previous contacts with encroaching Europeans have all been devastating for indigenous populations [3][4][5][6]. Disease, displacement, deforestation, mining, narcotrafficking and hydrocarbon extraction are currently some of the major threats to indigenous societies [1][2][3][4][5][6][7][8][9][10][11][12]. Limited information is available as to the demographic health of populations that remain isolated, but most are likely to be critically endangered and facing many of the same external threats that have plagued indigenous populations in the region for the past 500 years [1,2]. ...
... Photographs and videos of villagers shooting bows-and-arrows at planes or fleeing for cover have proven important for documenting their locations and gaining international interest in their conservation. It has been surmised that some isolated people in this region have been recently forced to flee into the state of Acre, Brazil because of invading drug and timber smugglers in Peru who have pushed into indigenous lands [7][8][9][10][11][12]. Many watersheds have been impacted by logging in both Peruvian protected areas and territorial reserves that have been set aside for isolated indigenous populations. ...
... Many watersheds have been impacted by logging in both Peruvian protected areas and territorial reserves that have been set aside for isolated indigenous populations. Logging is not permitted in protected areas, but loggers continue to operate with impunity inside park boundaries [8][9][10], and logging activities are purportedly financed by narcotrafficking [10][11][12]. ...
Article
Full-text available
The vast forests on the border between Brazil and Peru harbour a number of indigenous groups that have limited contact with the outside world. Accurate estimates of population sizes and village areas are essential to begin assessing the immediate conservation needs of such isolated groups. In contrast to overflights and encounters on the ground, remote sensing with satellite imagery offers a safe, inexpensive, non-invasive and systematic approach to provide demographic and land-use information for isolated peoples. Satellite imagery can also be used to understand the growth of isolated villages over time. There are five isolated villages in the headwaters of the Envira River confirmed by overflights that are visible with recent satellite imagery further confirming their locations and allowing measurement of their cleared gardens, village areas and thatch roofed houses. These isolated villages appear to have population densities that are an order of magnitude higher than averages for other Brazilian indigenous villages. Here, we report on initial results of a remote surveillance programme designed to monitor movements and assess the demographic health of isolated peoples as a means to better mitigate against external threats to their long-term survival. 2. Introduction Brazil's indigenous agency, Fundação Nacional do Índio (FUNAI), periodically releases information concerning locations of isolated peoples, also known as 'uncontacted Indians' or 'indigenous people in voluntary isolation' [1,2]. The long-term survival of isolated peoples hangs in a delicate balance. Previous contacts with encroaching Europeans have all been devastating for indigenous populations [3–6]. Disease, displacement, deforestation, 2014 The Authors. Published by the Royal Society under the terms of the Creative Commons Attribution License http://creativecommons.org/licenses/by/4.0/, which permits unrestricted use, provided the original author and source are credited.
... As these easily accessible populations were depleted, and as technology and overland transportation infrastructures improved, low-density terra firme populations came under increasing pressure during the 1970s and 1980s (White 1978;Grogan et al. 2002;Kometter et al. 2004). Today, intact commercial populations survive only in the most remote regions of south-west Amazonia such as in west Acre and southwest Amazonas (Brazil) and in the Alto Purús region of Peru (Grogan et al. 2002(Grogan et al. , 2008Fagan & Shoobridge 2005. ...
... Scientific Authorities take two general approaches to NDF for timber species: (1) sustainability may be evaluated at the level of the production or management unit, based on knowledge of local population parameters such as density, population structure, growth and mortality rates, or (2) sustainability may be verified by setting annual export quotas based on empirical knowledge of national stocks, density patterns, population dynamics and long-term impacts of quota-driven exploitation rates (CITES 2003 Fagan & Shoobridge 2005Cerdan 2007;CITES 2007a). Finally, quantitative assumptions underlying export quotas have been questioned, especially that the 'average' commercial-sized mahogany tree from the Peruvian Amazon yields 8.4 m 3 of sawn timber for export (INRENA 2006b). ...
... Most published studies of roundwood conversion efficiency in the tropics report wastage rates exceeding 50% (Table 2). While roundwood-tosawnwood conversion efficiency in the Amazon is commonly Grogan, personal observation 2003), and that significant quantities of sawn mahogany from Peru are processed in situ by the highly wasteful cuartoneo (quartering) technique using single or paired chainsaws (Fagan & Shoobridge 2005, we believe this conversion rate to be optimistic. No data are available to indicate what percentage of processed mahogany sawnwood meets export (primeira) standards. ...
Article
Full-text available
Big-leaf mahogany's listing on CITES Appendix II requires producer nations to certify that exported supplies were obtained in a manner non-detrimental to the species' survival in its role in the ecosystem. Non-detriment findings based on annual export quotas should verify that current harvest rates are sustainable with respect to total commercial stocks. In order to assess this impact, a method for converting export-quality sawnwood volumes to numbers of standing trees is used to estimate the number of mahogany trees and forest area required to produce the original and revised 2007 export quotas set by Peru, correcting for systematic measurement error caused by buttresses and for stem defects caused by heart-rot (hollow bole). Based on large-scale inventory data from three forest sites in nearby south-west Brazil, the average commercial-sized (> 75 cm diameter in Peru) mahogany tree in this region would yield 6.4–8.5 m3 of roundwood (standing volume), which in turn would be processed or milled into 1.7–2.2 m3 of export-grade sawnwood. From this estimate, 6120–8070 commercial-sized trees would have been harvested to supply the original 2007 export quota of 13 477 m3, from a forest area of 407 300–536 750 ha at landscape-scale densities reported by the Peruvian CITES Scientific Authority. To supply the revised export quota of 4983 m3, an estimated 2260–2980 commercial-sized trees will be harvested from a forest area of 150 600–198 450 ha. Both estimates exceed the number of trees the Peruvian Scientific Authority estimates can be sustainably harvested annually (961 ± 144 trees > 75 cm diameter) based on preliminary inventory data. The method estimates that, since 1996, 154 000–203 000 mahogany trees have been logged in Peru from a forest area of 10.2–13.5 million ha to supply the total reported export volume during this period (including the revised 2007 export quota) of 339 114 m3. This area corresponds to 18–25% of mahogany's total natural range in Peru, or 37–49% of mahogany's estimated remaining range in 2001. Without empirical knowledge of density patterns, surviving commercial stocks, and biological and technical issues linking processed lumber (sawnwood) to standing trees (roundwood), it will remain difficult to evaluate the sustainability of export quotas issued at the national level for mahogany or other tropical timber species.
... Consumer demand for high-value luxury timbers has been a principal driver of predatory logging in the tropics for several centuries (Lamb 1966). The pursuit of bigleaf mahogany (Swietenia macrophylla, Meliaceae) across southern Amazonia since the early 1970s has opened roads hundreds of kilometers into previously inaccessible primary forests, in turn opening those forests to cattle ranching, small-holder agriculture, and agribusiness and provoking conflict with Indigenous Amerindians that has frequently been disruptive and violent (Watson 1996;Fagan & Shoobridge 2005). Commercial mahogany stocks have been eliminated at local and regional scales through overharvesting, forest degradation, and deforestation (White 1978;Veríssimo et al. 1995;Gullison et al. 1996;Calvo & Rivera 2000;Grogan et al. 2002;Kometter et al. 2004). ...
... Forest cover maps confirm that deforestation affects much lower percentages of protected areas compared to the overall range (4.8% vs. 21%; see Bruner et al. 2001), while Indigenous Lands are also highly effective at curbing deforestation (10% vs. 21%; see Schwartzman & Zimmerman 2005). In Ecuador, Peru, and Bolivia, 14-16% of mahogany's (Veríssimo et al. 1995;Greenpeace 2001;Grogan et al. 2002;Fagan & Shoobridge 2005, 2007). ...
Article
Full-text available
Consumer demand for the premier neotropical luxury timber, big-leaf mahogany (Swietenia macrophylla), has driven boom-and-bust logging cycles for centuries, depleting local and regional supplies from Mexico to Bolivia. We revise the standard historic range map for mahogany in South America and estimate the extent to which commercial stocks have been depleted using satellite data, expert surveys, and sawmill processing center data from Brazil. We estimate an historic range of 278 million hectares spanning Venezuela to Bolivia, 57% of this in Brazil. Approximately 58 million hectares (21%) of mahogany's historic range had been lost to forest conversion by 2001. Commercial populations had been logged from at least 125 million more hectares, reducing the commercial range to 94 million hectares (34% of historic). Surviving stocks are extremely low-density populations in remote regions representing a smaller fraction of historic stocks than expected based on estimated current commercial range. Our method could advance international policy debates such as listing proposals for CITES Appendices by clarifying the commercial and conservation status of high-value timber species similar to mahogany about which little information is available. The fate of remaining mahogany stocks in South America will depend on transforming current forest management practices into sustainable production systems.
... The opportunistic hunting and trading of species is also connected to (formal and informal) logging and mining. Loggers and miners depend on wild fauna for sustenance in the areas where they operate (Castro et al. 1976;Robinson et al. 1999;Hill 2002;Ortiz von Halle 2002;Fagan and Shoobridge 2005; Boekhout van Solinge 2008). The opening of roads due to these operations also facilitates the wildlife commerce (Traffic 2008; Robinson et al. 1999;Boekhout van Solinge 2007). ...
Article
Full-text available
There is only scant empirical field research that explores the structures of the wildlife trade throughout the world. This study describes the processes that take place before, during and after wildlife is traded illegally in Peru through the words and experiences of the actors involved. This analysis utilizes formal interviews (N = 47), observations and thick descriptions in order to contextualize the processes of catching, selling, buying and rescuing wild fauna. Wildlife trade across Peru is found to be opportunistic and informal. The actors involved in this commerce are best described as ordinary citizens looking to supplement their low incomes.
... Most of the world's last isolated tribes with limited contact to the outside world reside in greater Amazonia [1]. Their prospects for long-term isolation and survival are precarious at best, given the tragic history of previous contacts with encroaching outsiders [2][3][4][5][6][7] and the continuing onslaught of external threats that plague their existence, namely disease, displacement, and deforestation [1,2,[4][5][6][7][8][9][10][11][12]. Government programs have been structured to protect lands for indigenous peoples in Brazil, known as indigenous territories [13]. ...
Article
Full-text available
The headwaters of the Amazon Basin harbor most of the world's last indigenous peoples who have limited contact with encroaching colonists. Knowledge of the geographic distribution of these isolated groups is essential to assist with the development of immediate protec-tions for vulnerable indigenous settlements. We used remote sensing to document the locations of 28 isolated villages within the four Brazilian states of Acre, Amazonas, Roraima, and Rondônia. The sites were confirmed during previous over-flights and by image evidence of thatched-roof houses; they are estimated to host over 1,700 individuals. Locational data were used to train maximum entropy models that identified landscape and anthropo-genic features associated with the occurrence of isolated indigenous villages, including elevation , proximity to streams of five different orders, proximity to roads and settlements, proximity to recent deforestation, and vegetation cover type. Isolated villages were identified at mid elevations, within 20 km of the tops of watersheds and at greater distances from existing roads and trails. We further used model results, combined with boundaries of the existing indigenous territory system that is designed to protect indigenous lands, to assess the efficacy of the existing protected area network for isolated peoples. Results indicate that existing indigenous territories encompass all of the villages we identified, and 50% of the areas with high predicted probabilities of isolated village occurrence. Our results are intended to help inform policies that can mitigate against future external threats to isolated peoples.
... International attention has become even greater since 2003, when mahogany listing in CITES Appendix II came into effect. In recent years several reports have documented rife illegal logging of mahogany in Peru, showing that it is taking place inside protected areas and indigenous territories, even threatening the very survival of indigenous tribes (Schulte-Herbrüggen, 2003;Fagan and Shoobridge, 2005;AIDESEP, 2007). ...
... While anthropologists have argued that members of the Isconahua tribe near the Ucayali study area were able to avoid the trafficking trails crisscrossing their homelands (Arbaiza Guzmán et al. 1995), our fieldwork found the amount of coca and logging trails too numerous to not have an impact on Isconahua annual migration patterns, hunting, and extractivism (Fig. 3). On the Purús River, the number of conflicts between uncontacted tribes and both coca workers and loggers has increased in recent years resulting in deaths on both sides (Fagan and Shoobridge 2005). Whereas in the past the uncontacteds in the Purús would run from potential conflicts, local people believe the tribes have become more aggressive due to the exponential increase of logging activity in the Alto Purús National Park and adjacent lands. ...
Article
The cultivation and traffic of coca, Erythrolxylum coca, and coca derivatives remain understudied threats to the conservation of the Amazon rainforest. Currently the crop is transforming land use and livelihoods in the ecologically and culturally rich borderlands of Amazonian Peru. The isolated nature of this region characterized by indigenous populations (both settled and uncontacted), conservation units, resource concessions, and a lack of state presence provides fertile ground for the boom and bust cycle of coca production and facilitates the international transport of the product to neighboring Brazil. This paper explores the social and environmental impacts of coca production, eradication, and transport through an analysis of both spatial and ethnographic data on land use and livelihood strategies along the Ucayali and Purús Rivers. Results map out the regional distribution and recent history of commercial coca fields and transboundary transportation routes and identify threats to the conservation of indigenous landscapes and borderland forests. KeywordsCoca–Conservation–Amazonia–Border–Peru–Brazil
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Background. The world’s last uncontacted indigenous societies in Amazonia have only intermittent and often hostile interactions with the outside world. Knowledge of their locations is essential for urgent protection efforts, but their extreme isolation, small populations, and semi-nomadic lifestyles make this a challenging task. Methods. Remote sensing technology with Landsat satellite sensors is a non-invasive methodology to track isolated indigenous populations through time. However, the small-scale nature of the deforestation signature left by uncontacted populations clearing villages and gardens has similarities to those made by contacted indigenous villages. Both contacted and uncontacted indigenous populations often live in proximity to one another making it difficult to distinguish the two in satellite imagery. Here we use machine learning techniques applied to remote sensing data with a training dataset of 500 contacted and 25 uncontacted villages. Results. Uncontacted villages generally have smaller cleared areas, reside at higher elevations, and are farther from populated places and satellite-detected lights at night. A random forest algorithm with an optimally-tuned detection cutoff has a leave-one-out cross-validated sensitivity and specificity of over 98%. A grid search around known uncontacted villages led us to identify 3 previously-unknown villages using predictions from the random forest model. Our efforts can improve policies toward isolated populations by providing better near real-time knowledge of their locations and movements in relation to encroaching loggers, settlers, and other external threats to their survival.
Article
The geopolitical initiative of creating military settlement projects, fronteras vivas (living borders), along isolated stretches of the Amazon borderlands transforms land use and livelihoods in unexpected ways. A case study in the Peruvian Amazon explores the natural resource management, household economics, and political geography of a borderland military base and associated settlement. Results find the military settlement project's transboundary impacts create opportunities for international conflict in an age of South American integration. La geopolítica de crear fronteras vivas, proyectos de asentamiento rural, en las fronteras amazónicas cambia el uso de la tierra y modo de vivir en estas fronteras aisladas en maneras inesperadas. Un estudio de caso en la Amazonía peruana investiga el manejo de recursos naturales, la economía, y la geografía política de un proyecto de asentamiento rural militar. Los resultados indican que los impactos transfronterizos del proyecto de asentamiento crean oportunidades para conflicto internacional en una época de la integración regional sudamericana. A geopolítica de criar fronteiras vivas, projetos de assentamento rural, nas fronteiras amazónicas muda o uso de terra e modo de viver em estas fronteiras isoladas em maneiras inesperadas. Um estudo de caso na Amazônia peruana pesquisa a utilização de recursos naturais, a economía familiar, e a geografía política de um projeto de assentamento rural militar. Os resultados indicam que os impactos transfronteiriços do projeto de assentamento criam oportunidades para conflito internacional numa época da integração regional sudamericana.
Article
Full-text available
Although bigleaf mahogany [Swietenia macrophylla King (Meliaceae)] is the premier timber species of Latin America, its exploitation is unsustainable because of a pattern of local depletion and shifting supply. We surveyed experts on the status of mahogany in Bolivia and Peru, the world's past and present largest exporters. Bolivia no longer has commercially viable mahogany (trees > 60 cm diameter at breast height) across 79% of its range. In Peru, mahogany's range has shrunk by 50%, and, within a decade, a further 28% will be logged out. Approximately 15% of the mahogany range in these two countries is protected, but low densities and illegal logging mean that this overestimates the extent of mahogany under protection. The international community can support mahogany conservation by funding park management and by encouraging independent verification of the legality of mahogany in trade. Our findings demonstrate that a systematic expert survey can generate reliable and cost-effective information on the status of widespread species of concern and help to inform appropriate management policy. Copyright © 2004 by the author(s). Published here under licence by The Resilience Alliance.
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