|
CSI Programs
Climate Change Ocean Change Alternative Energy Environmental Education Urban Conservation Predator Conservation Primate Conservation Ethics Initiative
| |
|
|
|
Written By: Krista Fish
|
 |
|
Deforestation in the Congo
Basin Threatens Primates Habitat
Source www.bbc.co.uk |
According to the IUCN (International
Union for the Conservation of Nature and Natural Resources or the
World Conservation Union), over 1/3 of primate species are listed as
critically endangered, endangered, or vulnerable (IUCN, 1996). Although
primates are found in tropical and subtropical habitats such as woodlands
and savannas, over 90% of primate species occur in tropical forests (Cowlishaw
and Dunbar, 2000; Mittermeier and Cheney, 1987). Because primates are at
their highest diversity in tropical forests, the loss of these forests is
widely regarded as the process that most threatens primate species (Chapman
and Peres, 2001; Mittermeier and Cheney, 1987; Southwick and Siddiqi,
2001). Growing human populations which are expanding into forest habitats
and clearing forests for agriculture are the chief cause of forest loss (Cowlishaw
and Dunbar, 2000). Commercial logging, subsistence harvesting of timber,
mining, and dam construction are other human activities leading to forest
loss in the tropics (Cowlishaw and Dunbar, 2000; Mittermeier and Cheney,
1987). Throughout their history, humans have utilized timber and converted
forests to agricultural land.
However, the rate of forest loss has
increased in the last 50 years (Cowlishaw and Dunbar, 2000). During the
1990s, 15.2 million ha were lost annually in the tropics (FAO, 2001). Recent data suggests that deforestation continues at an alarming rate-
especially in primate habitats. From 2000-2005, South America lost 4.3
million ha of forest each year and Africa lost 4.0 million ha per year (FAO,
2005). These high rates of deforestation have resulted in the loss of more
than 50% of the ancestral forest cover around the world (WRI/WCMC/WWF,
1997).
The extinction risk faced by
primates is exacerbated by characteristics of their biology. Many of the
diurnal primates have a large body size (>5 kg). Large body size may
increase extinction risk for primates due to two factors.
|
 |
|
Orangutan's are
facing many threats in the wild, most recent being the increased
production of palm oil in Indonesia. Palm oil can be found in many
of the food products we consume. Vast tracts of forest have been
cleared to allow for the increases production of this product.
Photo: www.primates. |
First, large
primates are a more profitable target for human hunters compared to small
primates (Cowlishaw and Dunbar, 2000). Second, their large body size
imposes constraints on their life histories (Cowlishaw and Dunbar, 2000).
Large-bodied primates have slow life histories- they require more time to
reach sexual maturity and a longer period between births when compared to
smaller primates. As a result, many large primate species cannot quickly
replace members of their population who may be lost due to human activities
such as hunting (Purvis et al., 2000).
In addition to the threat created by
forest loss, there are other dynamics at work. Forest fragmentation, primate
crop raiding, and hunting of primates for use in medicines, as pets, and for
food also impact the ability of primates to survive into the future. These
threats to primates are found throughout the world, but their extent varies
based on local economic conditions, religions, and politics.
Back to the top |
|
Primate Conservation Concerns in
Africa
|
 |
|
De Brazza's Monkey
one of the many primate species affected by the bushmeat trade.
Photo: www.guenons.com |
In addition to habitat loss, hunting
negatively impacts many African primate species. Although subsistence
hunting of primates and other wild animals has occurred in Africa for
centuries, the recent expansion of the bushmeat trade in Africa may pose a
serious threat to primates. Estimates for some African cities suggest that
half of all protein consumed in urban areas comes from the bushmeat trade (Fa
et al., 1995). A survey of bushmeat available in markets in the Central
African markets revealed that hunters target prey such as primates because
their body size makes them easy to hunt, easy to transport to market, and
also brings in a good price (Fa et al., 1995). The results of the market
survey also suggest that endangered primates such as guenons (Cercopithecus
nictitans, C. preussi), and drills (Mandrillus leucophaeus)
are hunted at levels that far exceed sustainable harvests (Fa et al., 1995).
The problem of the bushmeat trade in
Africa illustrates the often intertwined nature of threats to animals. For
example, timber companies move into forests in order to commercially log the
forest. Not only does this result in loss of forest, but it also
contributes to the bushmeat trade. Logging company employees often kill
wild animals for their own consumption or to sell for profit in nearby
cities. Many loggers depend upon cash generated from bushmeat in order to
pay for basic needs such as food, clothing, healthcare, and education for
themselves and their families (Wilkie et al., 1992).
Primates also impact African
economies through their crop-raiding activities. In Africa, shifting
agriculture has been practiced for centuries (Naughton-Treves et al.,
1998). The resulting landscape is a mosaic of fields/orchards planted near
forests or forest fragments. Primates utilize this mixed landscape to their
advantage and feed in both fields and the forest (Naughton-Treves et al.,
1998). Although primates have likely been crop-raiding since the advent of
agriculture, the degree of conflict between farmers and wildlife has
recently escalated as humans move closer to the remaining forests (Hill,
1997). Farmers report large economic losses due to crop-raiding (Hill,
1997). In order to prevent these losses, farmers set traps for crop raiders
or lobby governments to undertake eradication programs. Baboons (Papio
anubis) and vervet monkeys (Cercopithecus aethiops) are
frequently targeted because they are perceived to be the animals which most
threaten crops (Hill, 1997). Even for widespread species such as baboons,
hunting to control crop-raiding may be done at unsustainable levels
(Fitzgibbon et al., 1995). Primate crop-raiding also harms conservation
efforts. Farmers whose land is nearest to forests report the majority of
losses to crop-raiding animals (Hill, 1997). Losses to crop-raiding and the
resulting negative perception of primates affect the views of local people
regarding primates and the usefulness of protected forest habitats (Hill,
2002).
Back to the top |
|
Primate Conservation Concerns in
Madagascar
|
 |
|
Encroachment is a
problem throughout the world here ring-tailed lemurs forage on the
forest floor next to ox and cart
Photo -
Krista Fish |
Madagascar is a large island located
off the east coast of Africa and is home to a unique array of bird, mammal,
and reptile life. In Madagascar, 100% of the primate fauna is endemic. The prosimian primates in Madagascar evolved in isolation from monkeys, apes,
and many of the potential competitors and predators found in mainland Africa
and Asia (Richard, 1987). The recent arrival of humans who began settling
Madagascar from Indonesia and Africa between 1500-2000 years ago altered the
ecology of the island (Richard, 1987). Not long after humans colonized
Madagascar, 15 species of primates became extinct (Cowlishaw and Dunbar,
2000). The extinct primate fauna in Madagascar were all larger in body size
than living lemurs. One species even grew to 200 kg- approximately the size
of a male gorilla (Cowlishaw and Dunbar, 2000). The exact cause of the
extinction of the Malagasy primates is unknown; however, several factors
have been suggested. The first people to settle in Madagascar burned forests
to clear the land for agriculture and the resulting habitat loss may have
led to the extinction of the large lemurs (Chapman and Peres, 2001; Burney
et al., 1997). Humans also brought new species of plants and animals to the
island. The introduced species may have been destroyed the native plant
community or been competitors for food (Cowlishaw and Dunbar, 2000). Additionally, the large, terrestrial lemurs would have been attractive
targets for human hunting (Cowlishaw and Dunbar, 2000). Today the primates
on Madagascar face the same challenges that doomed their large relatives. Deforestation continues in Madagascar as land is cleared for agriculture
uses and timber is used as a fuel source (Cowlishaw and Dunbar, 2000). Lemurs are also hunted for subsistence (Cowlishaw and Dunbar, 2000). However, hunting practices are not uniform throughout the country. Hunting
of certain lemur species is forbidden by taboos which vary from region to
region (Cowlishaw and Dunbar, 2000).
Back to the top |
|
Primate Conservation Concerns in
Asia
|
 |
|
Traditional medicine
in Asia pose great threats to many species including primates. On
the left of the photo there are dried Slow Loris - a small nocturnal
primate often found in traditional medicine remedies.
photo: Matt Jeffery |
There are more critically endangered
primate species in Asia than anywhere else in the world (IUCN, 1996).
Primates in Asia are losing their forest habitat. However, during the
period from 2000-2005, Asia reported net forest gains (FAO, 2005). The
discrepancy is largely due to the types of forests that are being planted in
China. Both diverse tropical forests and land previously used for
agriculture are now being converted to monoculture plantations that supply
hardwood and pulp for paper production (Choudhury, 2001; FAO, 2005; Kumara
and Singh, 2004). Because plantations seldom contain species of trees that
provide food for primates, these habitats are unsuitable for primates and
other forest animals.
|
 |
|
The pet trade
is a problem for many primate species - this young gibbon was a pet
for a young girl in Phnom Penh Cambodia.
Photo: Matt Jeffery |
Hunting of primates is a serious
threat to primates in Asia. Although consuming primate meat is forbidden by
Hinduism, Buddhism, and Islam, the reality is that primates are hunted in
areas where these religions are practiced (Cowlishaw and Dunbar, 2000). Many traditional religions in Asia do not forbid primate consumption, so
primates may be hunted to supply meat to these populations (Choudhury, 2001;
Kumara and Singh, 2004). In urban areas, meat from primates and other wild
animals is a prized food item as it is associated with elite classes
(Workman, pers. comm.). Primates are also hunted to be sold as pets and
for use in traditional medicine (Nijman, 2004; O’Brien et al., 2004;
Workman, 2004). The demand for primate pets has increased in recent years
due to the growing middle class in China and its desire for exotic pets
(Workman, 2004).
Although many primates in Asia are
critically endangered, others suffer from a problem of overabundance. In
particular, the case of rhesus macaques in India highlights how trade bans
helped a population to recover, only to have created new concerns. During
the 1960s, researchers documented a large decline in rhesus macaque
populations in India as the macaques were being overtrapped to support
biomedical research, vaccine production, and pharmaceutical testing in
western laboratories (Southwick and Siddiqi, 2001). Bans on rhesus exports
helped the population to stabilize and then expand. Now, rhesus macaques
are considered a pest species throughout their range (Southwick and Siddiqi,
2001). Rhesus macaque populations have expanded to nearby urban areas where
they steal food from homes, gardens, and occasionally attack people
(Southwick and Siddiqi, 2001). Although both laws and religious traditions
prohibit harming these animals, many people living near the macaques have
negative attitudes towards the macaques and relocation programs for problem
monkey groups have been undertaken (Choudhury, 2001; Southwick and Siddiqi,
2001).
Back to the top |
|
Primate Conservation Concerns in
the Neotropics
 |
Mantled howler monkey feeding in a Panamanian
forest fragment.
Photo - Krista Fish |
In the New World tropics, two
dominant conservation concerns have emerged: forest fragmentation and
hunting. Throughout Central America, there are few remaining large tracts
of tropical forest (Chapman and Peres, 2001; Estrada et al., 1994). Instead, the landscape is one where forest fragments appear as islands in a
sea of urban and agricultural land use. These fragments are not simply
small versions of large forests. Instead, a greater percentage of the
forest fragment area is subject to edge effects such as lower levels of
humidity, increase in wind, and drier soils near the edge (Marsh, 2003;
Turner, 1996). These edge effects alter the type of vegetation that remains
in the forest which in turn affects the ability of primates to survive in
forest fragments. Fragmentation problems are further compounded as some
primates may be unable to travel between fragments (Marsh, 2003; Turner,
1996). As a result, the deleterious effects of inbreeding may impact
primates living in fragments (Chiarello, 2003; Pope, 1996).
Fragmentation is also a concern in
parts of South America. The fragmentation of the Atlantic coastal forests in
Brazil has been occurring for the last 500 years, beginning with the arrival
of Europeans (Chiarello, 2003). The majority of the Atlantic coastal forest
now exists as fragments (Chiarello, 2003). This region of Brazil is of
concern to primatologists as two genera of primates are endemic to these
forests: Brachyteles and Leontopithecus (Chiarello, 2003). In
order to conserve these genera, the threats of fragmentation, inbreeding,
and hunting need to be addressed.
Even in the remaining large tracts
of forests such as those found in the Amazon basin, primate populations are
declining. Large-bodied primate species such as howler monkeys (Alouatta
sp.), woolly monkeys (Lagothrix sp.), and spider monkeys (Ateles
sp.) are favorite prey items of humans (Peres and Dolman, 2000). Subsistence
hunters may take hundreds of primates in a year and in many locations,
long-term hunting has resulted in the local extinction of large-bodied
primates (Chapman and Peres, 2001; Peres and Dolman, 2000).
Back to the top |
|
Primate Conservation Concerns in
Europe and North America People in countries outside of the
tropics play a role in primate conservation. The exotic pet trade in the
United States is lucrative and primates are part of this trade with prices
ranging from $3000 for monkeys to $30,000 for apes (IPPL, 2003). Although
the importation of primates for the pet trade was banned in 1975,
wild-captured primates are smuggled into the US for the pet trade-
especially along the US-Mexico border (IPPL, 2003). The demand for bushmeat
also extends beyond the tropics as African expatriates fly bushmeat into
European countries (Chapman and Peres, 2001).
|
|
Why does primate conservation
matter?
Forests around the world serve
important roles as they prevent soil degradation and erosion, protect
watersheds, limit the greenhouse gas effect, provide subsistence resources,
commercial timber, and recreational opportunities (Mittermeier and Cheney,
1987). Primates are part of healthy forests in the tropics as they
contribute to forest regeneration. Since many species of primates eat a
diet high in fruits, they are important seed dispersers (Chapman and Onderdonk, 1998). As primates feed on fruit, they spit out or defecate
seeds away from the parent tree which gives the seed a higher chance of
germination and survival (Chapman and Onderdonk, 1998; Chapman and Peres,
2001). Trees with large seeds may be particularly impacted by the loss of
primates as other frugivorous animals such as birds may be unable to
disperse their seeds (Chapman and Onderdonk, 1998). In addition to
seed-dispersal, primates play other roles in their habitats as predators,
prey, and competitors for resources. The loss of primates from their
habitats will have serious implications for other species of plants and
animals.
For more information about the
Conservation Science Institute Primate Initiative (CSIPI) or if you
would like to get involved with the program please contact Krista Fish,
CSIPI coordinator, Department of Anthropology, Hale Science Building Campus
Box 233, University of Colorado,
Boulder, CO. 80309
e-mail: Krista.Fish@Colorado.edu.
Back to the
top |
|
Useful Links:
http://sciencebulletins.amnh.org/bio/f/lemurs.20060401/index.php
|
|
References
Burney DA, James HF, Grady FV,
Rafamantanantsoa JG, Ramilisonina, Wright HT, Cowart JB.1997. Environmental
change, extinction and human activity: evidence from caves in NW Madagascar.
Journal of Biogeography 24(6):755-767.
Chapman CA and Onderdonk DA. 1998.
Forests without primates: primate/plant codependency. American Journal of
Primatology 45:127-141.
Chapman CA and Peres CA. 2001.
Primate conservation in the new millennium: the role of scientists.
Evolutionary Anthropology 10:16-33.
Chiarello AG. 2003. Primates of the
Brazilian Atlantic forest: the influence of forest fragmentation on
survival. In: Primates in Fragments: Ecology and Conservation. Marsh LK
(editor). New York: Kluwer Academic/Plenum Publishers, p. 99-121.
Choudhury A. 2001. Primates in
Northeast India: an overview of their distribution and conservation status.
Envis Bulletin: Wildlife and Protected Areas 1(1):92-101.
Cowlishaw G, Dunbar R. 2000. Primate
Conservation Biology. Chicago: University of Chicago Press.Estrada A,
Coates-Estrada R, and Meritt D. 1994. Non-flying mammals and landscape
changes in the tropical forest region of Los Tuxtlas, Mexico. Ecography
17:229-241.
Fa JE, Juste J, Perez de Val J,
Castroviejo J. 1995. Impact of market hunting on
mammal species in Equatorial Guinea. Conservation Biology 9(5):1107-1115.
FAO. 2001. Global Forest Resources
Assessment 2000. Food and Agriculture Organization of the United Nations,
Rome, 2001. http://www.fao.org/forestry/fo/fra/index.jsp
FAO. 2005. Global Forest Resources
Assessment 2005: Progress towards sustainable forest management. Food and
Agriculture Organization of the United Nations, Rome, 2005. http://www.fao.org/forestry/fra2005
Fitzgibbon CD, Magoka H, Fanshawe JH.
1995. Subsistence hunting in Arabuko-Sokoke Forest, Kenya, and its effects
on mammal populations. Conservation Biology 9: 1116-1126.
Hill CM. 1997. Crop-raiding by wild
vertebrates: the farmer’s perspective in an agricultural community in
western Uganda. International Journal of Pest Management 43(1):77-84.
Hill CM. 2002. Primate conservation
and local communities-ethical issues and debates. American Anthropologist
104(4): 1184-1194.
IPPL (International Primate
Protection League) (2003). The US pet monkey trade. IPPL News. www.aesop-project.org/US_Pet_Monkey_Trade.htm
IUCN (International Union for the
Conservation of Nature and Natural Resources) (1996). IUCN List of
Threatened Species, IUCN Gland, Switzerland.
Kumara HN and Singh M. 2004.
Distribution and abundance of primates in rainforests of the Western Ghats,
Karnataka, India and the conservation of Macaca silenus.
International Journal of Primatology 25(5):1001-1018.
Marsh LK. 2003. The nature of
fragmentation. In: Primates in Fragments: Ecology and Conservation. Marsh LK
(editor). New York: Kluwer Academic/Plenum Publishers, p. 1-10.
Mittermeier RA, Cheney DL. 1987.
Conservation of primates and their habitats. In: Primate Societies. Smuts
BB, Cheney DL, Seyfarth RM, Wrangham RW, and Struhsaker TT (editors).
Chicago: University of Chicago Press, p. 477-490.
Naughton-Treves L, Treves A, Chapman
C, Wrangham R. 1998. Temporal patterns of crop-raiding by primates: linking
food availability in croplands and adjacent forest. Journal of Applied
Ecology 35: 596-606.
Nijman V. 2004. Conservation of the
Javan gibbon Hylobates moloch: population estimates, local
extinction, and conservation priorities. The Raffles Bulletin of Zoology
52(1):271-280.
O’Brien TG, Kinnaird MF, Nurcahyo A,
Iqbal M, Rusmanto M. 2004. Abundance and distribution of sympatric gibbons
in a threatened Sumatran rain forest. International Journal of Primatology
25(2):267-284.
Peres CA, Dolman PM. 2000. Density
compensation in neotropical primate communities: evidence from 56 hunted and
nonhunted Amazonian forests of varying productivity. Oecologia 122:175-189.
Pope TR. 1996. Socioecology,
population fragmentation, and patterns of genetic loss in
endangered primates. In:
Conservation Genetics: Case Histories from Nature, Avise J, Hamrick J
(editors). Norwell: Kluwer Academic Publishers, p. 119-159.
Purvis A, Gittleman JL, Cowlishaw G,
Mace GM. 2000. Predicting extinction risk in declining species. Proceedings
of the Royal Society of London 267: 1947-1952.
Richard AF. 1987. Malagasy
prosimians: female dominance. In: Primate Societies. Smuts BB, Cheney DL,
Seyfarth RM, Wrangham RW, and Struhsaker TT (editors). Chicago: University
of Chicago Press, p. 25-33.
Southwick CH, Siddiqi MF. 2001.
Status, conservation and management of primates in India. Envis Bulletin:
Wildlife and Protected Areas 1(1): 81-91.
Turner IM. 1996. Species loss in
fragments of tropical rain forest: a review of the evidence. Journal of
Applied Ecology 33:200-209.
Wilkie DS, Sidle JG, and Boundzanga
GC. 1992. Mechanized logging, market hunting, and a bank loan in Congo.
Conservation Biology 6:570-580.
Workman C. Primate conservation in
Vietnam: toward a holistic environmental narrative. American Anthropologist
106(2):346-352.
WRI/WCMC/WWF. 1997. Bryant D, Nelson
D, Tangley L. The last frontier forests: ecosystems and economies on the
edge. World Resources Institute, Forest Frontiers Initiative, World
Conservation Monitoring Center, and the World Wildlife Fund for Nature.
http://www.wri.org/wri |
|