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Why
is GAFI needed
Orangutan
The
Conservation Status of the Orangutan
Once widespread throughout the forests of Asia, orangutans are now confined
to two islands, where two genetically distinct species exist: the Sumatran
orangutan (Pongo abelii) and the Bornean orangutan (P. pygmaeus). A
recent assessment of the conservation status of the Bornean and Sumatran
orangutans, their rate of decline, and the extent of remaining habitat
paint a bleak picture. Population sizes and densities within habitat
patches are falling across the species’ ranges, and the prohibitive
rate of forest loss continues unabated. In the decade between
1992 and 2003, it is estimated that orangutan habitat declined by more
than 5.5 million hectares.
There are less than 8 million hectares of orangutan habitat
left standing in Kalimantan, and less than 900,000 hectares on Sumatra.
Across the orangutans’ entire range, conversion of forests to
oil palm plantations is occurring on a massive scale, logging continues
with no signs of being reduced, irrespective of the protection status
of the land, and infrastructure developments threaten to fragment the
habitat of the last viable populations. In order to be considered genetically
viable in the long term, populations must number 500 or more individuals.
On Sumatra, only 3 such populations exist. As their habitat is further
cleared, degraded and fragmented, it is likely that any populations
that continue to survive in protected areas may soon drop below this
critical threshold, at which point remaining individuals make no contribution
to the long-term survival of the species. Taking into account rates
of habitat loss and fragmentation, persecution as agricultural pests
and the illegal pet trade, and with less than 60,000 individuals remaining,
extinction of both the Sumatran and Bornean species within a few years
is a certainty if current trends continue.
Key
causes of decline
The lowland forests of Borneo and Sumatra are the only places in the
world where the orangutan can still be found in the wild. Population
numbers have fallen dramatically in the last 30 years as their forest
habitat has been decimated. An estimated 80% of orangutan habitat was
lost between 1975 - 1995, and several million more hectares have disappeared
in the last decade. This decline has been attributed to widespread logging,
devastating fires, and conversion for plantation agriculture.
The illegal pet trade is
strongly linked with the degradation and conversion of forests due to
increased accessibility for hunters and poachers. It has been estimated
that for every infant that survives the process of capture and transport,
at least 3 others will have been lost, and each of these infants also
represents the death of an adult female orangutan, the most demographically
important members of every wild population. The number of confiscated
infants resident at rehabilitation centres indicates that this trade
continues at unsustainable levels.
Habitat degradation through
logging activity occurs extensively across the two islands. Although
this reduces the capacity of the forests to support high population
densities, orangutans are able to survive in these disturbed habitats.
However, it is now common practise for expired logging concessions to
be clear-cut and converted to plantations. It is predicted that all
unprotected lowland forest will have disappeared on Sumatra and Borneo
by 2010. Current patterns of land conversion result in increased pressure
on protected forests to supply timber, and further encroachment will
reduce the viability of populations even within national parks.
Lethal conflict
is now a frequent occurrence in plantations and nearby private gardens,
as orangutans are forced out of degraded forest fragments in search
of enough food for survival. Perceived as a threat to the plantations’
profits, these endangered and protected species, a flagship for the
conservation of South-east Asian rainforests, are considered to be agricultural
pests and killed.
Orangutans:
A flagship species for the Indonesian and Malaysian Rainforests
An extremely significant species-habitat association
exists between orangutans and the rainforest ecosystem they inhabit.
The apes act as seed dispersers that help maintain species diversity,
so the presence of orangutans is a good indicator of the biological
diversity of Southeast Asian rainforests. If orangutans are present
at ‘normal’ densities, then the area is also likely
to contain at least 5 other species of primates, at least five
species of hornbills, at least 50 different fruit tree species,
and 15 liana species. Thus orangutans are an excellent “flagship
species” for rainforest conservation. The species’
requirements with regard to area and habitat are wide enough that
if orangutans were made a focus of protective management, the
biodiversity of species within its range would also automatically
be preserved.
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ORANGUTANS
IN SUMATRA
Orangutans were historically found in forests across Sumatra but are
now restricted to North Sumatra and Aceh provinces. The Sumatran orangutan
(Pongo pygmaeus abelii) has been classified as "Critically Endangered"
by the IUCN (World Conservation Union). Populations have declined from
over 12,000 in 1994, to around 7,300 at the last comprehensive survey
carried out in 2003. The species is threatened by habitat loss and poaching,
and a proposed network of roads through the Gunung Leuser National Park,
containing most of the remaining viable populations, further threatens
their survival.
With their jungle
environment burnt and logged and their food sources lost, the Sumatran
orangutan population is declining by as many as 1,000 per year. Current
estimates suggest that they could become extinct in the wild in less
than 10 years. Illegal logging and the deliberate starting of forest
fires in order to convert virgin forest to timber and palm oil plantations
are the main factors responsible for the loss of over 80% of orangutan
habitat over the last 20 years.
The
Sumatran orangutan has suffered a high degree of habitat fragmentation;
the most up-to-date surveys indicate that less than 900,000 hectares
of suitable habitat remain on the island, in 13 distinct forest fragments.
The largest population of Sumatran orangutans exists in the province
of Aceh, but data indicate that 1,000 individuals were being lost per
year during 1998-1999 in this area alone, and populations plummeted
across the island by 50% in just 8 years prior to 2000.
Only 3 of the remaining
population units are considered to be demographically and genetically
viable, with more than 500 individuals. All three are located within
the Leuser Ecosystem, a 2.6 million hectare expanse of forest spanning
the borders of Aceh and North Sumatra, which has been acknowledged as
one of the world’s most important biodiversity hotspots. The ecosystem
incorporates the Gunung Leuser National Park, but the majority of orangutans
are resident outside the park boundaries, and the forests are experiencing
a 10-15% rate of habitat loss per year due to logging. This astounding
rate of forest decline implies that even the most recent estimate of
remaining habitat, made at the beginning of 2004, will now be out of
date and forest patches will have shrunk even further.
There are four
separate habitat units within the Leuser ecosystem, which were connected
until around a decade ago. Efforts to reconnect them in the future would
produce a large and viable population, but work has already begun on
the construction of the Ladia Galaska road system, which cuts through
the ecosystem in at least nine places. This development promises extensive
fragmentation and destruction of the forest, easier access for illegal
loggers and poachers, and inevitable significant population reductions
for many endangered species including the Sumatran orangutan, tiger,
rhinoceros and elephant.
There
is great pressure for the conversion of forests to agricultural uses
across Indonesia, and this has been occurring at an alarming rate on
Sumatra, which now has over 4 million hectares of oil palm plantations
– more than four times the area of remaining orangutan habitat
on the island. It is clear that the small amount of remaining habitat
will soon disappear if forest loss continues, and although a handful
of orangutans may continue to survive in isolated forest fragments,
these populations will not be genetically or demographically viable
and will make no contribution to the long-term survival of the species.
This implies that the effective extinction of the Sumatran orangutan
is imminent, and the call for a halt to habitat loss is more urgent
than ever.
(photos by Nicholas
Tignonsini)
ORANGUTANS
IN BORNEO
The Bornean orangutan is found in the Indonesian provinces of West,
Central and East Kalimantan, and the Malaysian states of Sabah and Sarawak.
Intense field surveys over the last ten years have revealed higher estimated
population numbers of orangutans on Borneo than previously thought,
but during this time the rate of habitat decline has escalated, resulting
in a high degree of fragmentation of remnant forest patches across the
island. Experts believe this to be a key factor in the continuous reduction
in population numbers in all three subspecies, and it is thought that
even low rates of hunting could destabilize and threaten the survival
of Bornean orangutan populations, even within good quality habitat.
If individuals are
unable to disperse safely between forest fragments, and if habitat destruction
continues, it is predicted that all populations will decline steadily
to extinction. Recent habitat analyses revealed that in 2002 the total
area of orangutan habitat remaining in Kalimantan was approximately
8.5 million hectares, divided into 306 distinct habitat units. Almost
half of these habitat units were less than 10,000 hectares in size,
together accounting for just 5.5% of the total area, highlighting the
severity of the fragmentation of the remaining lowland forests. To compound
the problem, the majority of the forest is now classified as degraded,
and is therefore likely to be able to support lower densities of orangutans
than primary forest, as well as being vulnerable to re-classification
as conversion forest – destined to be clear-cut and converted
to oil palm plantations. Taking into account an estimated rate of deforestation
on Borneo of 1.3 million hectares per year, the outlook for the Bornean
orangutan is not much more favourable than that of the Sumatran species.
Remaining habitat is already likely to have been reduced to less than
5 million hectares in the last 3 years, and predictions have been made
that all unprotected lowland forests, excluding peat swamps, will have
disappeared from Kalimantan by 2010.
KEY
CAUSES OF ORANGUTAN DECLINE
The decline of the orangutan on Borneo and Sumatra in recent years symbolises
the devastation of one of the world’s biodiversity hotspots –
the lowland rainforests of Southeast Asia. The major threats to the
survival of orangutans have been identified as habitat loss, degradation
and fragmentation, with a secondary, associated threat being live capture
for the pet trade.
HABITAT
LOSS
Indonesia has one of the highest tropical forest loss rates in the world,
with 64 million hectares of forest cover having been cleared in the
last 50 years. Despite the increasing scarcity of remnant patches of
forest on Borneo and Sumatra, the rate of deforestation is showing no
sign of slowing down: around 15 years ago an average 1.7 million hectares
was cleared annually in Indonesia, increasing to 2 million hectares
by the turn of the millennium. A World Bank report has blamed commercial
developments, especially oil palm plantations, for this acceleration,
and if this rate continues, there will be no lowland forest (excluding
peat swamp forests) left outside protected areas in Kalimantan by 2010,
and in Sumatra by 2006. The remaining swamp forests will disappear over
the 5 years following the removal of dipterocarp forests, as peat swamps
sustain a lower density of commercially valuable tree species, and are
therefore prone to lower rates of exploitation.
The
Mega-Rice Project, described as “the largest and most destructive
agricultural conversion project in the world in recent times”,
demonstrates the vulnerability of large areas of orangutan habitat to
rapid conversion. Forest clearance and peat drainage took place on a
massive scale between 1996-1998 to reclaim one million hectares of swamp-forest
floodplains in Central Kalimantan, in an attempt to increase Indonesia’s
rice production capacity. This development faced considerable opposition
because such activity causes the development of acidic soils, hydrological
disturbance, and results in the die-off of surrounding forest cover,
whilst sustaining very low agricultural productivity. The project was
an unmitigated failure, and after the area had been abandoned, massive
drainage canals continued to siphon off water from the surrounding peatland
forests. The vast forest clearance had already claimed an important
area of orangutan habitat and displaced thousands of animals, and when
the dry peat and dead wood gave rise to 6 months of uncontrollable fires
during 1997-1998, a further 400,000 hectares of forest burnt. The fragmentation
of the remnant forest patches, coupled with the inhospitable matrix
of farmland, rivers and canals, prevented around 8,000 orangutans from
escaping, and these died in the fire. Despite the area being classified
as “estate crops” on official government maps, not a single
blade of rice was ever planted, and the land remains barren and unproductive.
Yet lessons remain un-learned
and the conversion of forest to agriculture continues on a massive scale.
The rapid expansion of oil palm plantations across Borneo and Sumatra
has already involved the clear-felling of millions of hectares of forests,
and all unprotected lowland forests are vulnerable to eventual future
conversion.
Between
1989 and 2000, the area of oil palm harvested in Indonesia more than
tripled. By the beginning of 2004, there were 6.5 million hectares of
oil-palm plantations across Sumatra and Borneo. Of this, almost 4 million
hectares had previously been forested. However, the palm-oil industry
is associated with deforestation beyond establishing oil-palm estates
on previously forested land. Orangutan inhabit lowland dipterocarp,
freshwater and peat swamp forests, but unfortunately this habitat is
located precisely in those areas that are preferentially converted to
oil-palm plantations.
Aceh, probably the last stronghold
of the Sumatran orangutan, is losing its forests at a rate of 270,000
hectares per year. Research has shown that 20,000 hectares of the Tripa
and Truman-Singkil swamp forests, known to support one of the highest
densities of orangutans in Sumatra, were converted to oil palm plantations
between 1990 and 2000, with half of this area being lost in the space
of only 2 years. In 2003, the area cultivated with oil palms in Sabah
and Sarawak reached over 1.6 million hectares, with an estimated 80,000
hectares of forest being converted to plantations every year. Conversion
to oil palm plantations is now recognized as a primary threat to the
lowland forests on Borneo and Sumatra, and hence the continued survival
of countless species, including the orangutan.
HABITAT
DEGRADATION AND FRAGMENTATION
Orangutans have a slow life history, characterised by extended periods
of parental care and long inter-birth intervals of around 8 years. This
pattern confers low population growth rates and slow recovery from habitat
and population disturbance events such as logging and hunting. Population
densities tend to remain low, even in suitable habitat, and are even
lower in logged and secondary-growth forests. A long-term census of
orangutans in the Sebangau forests recorded a 49 per cent decline in
numbers within 8 years. This has been attributed to a decline in the
carrying capacity of the habitat patch due to the removal of large fruiting
trees during logging operations. These reductions persist after the
initial disturbance - old secondary growth forests contain only 30-50%
of the orangutan density found in primary forest.
Illegal logging
accounts for 70%t of the timber supplied to the processing sector, and
occurs across the orangutans’ range, including within the boundaries
of supposedly protected areas. Since 1999, local governments in Indonesia
have held the power to designate new protected areas within their provinces,
but are also responsible for generating their own revenues. Natural
resource extraction and exploitation is often the simplest way of raising
local income, so land-use plans seldom take into account the long-term
conservation value of the forests. The current state of Kutai National
Park is a clear indication of the failure of the protected area system
in Indonesia and serves as a cautionary tale for conservationists working
to ensure the safety of remaining orangutan populations from further
habitat destruction. Since the late 1960s, Kutai has been overrun by
logging concessions, industrial complexes, open-pit coalmines and human
settlements. Two intense fires in 1983 and 1998 were responsible for
the loss of 95% of the lowland forest, and the degraded state of the
ecosystem prior to the fires has been implicated in the extent of the
damage. Now, only around 10% of the park remains forested, decimating
the orangutan population, from an estimated 4,000 in 1970, to just 500
today.
Logging,
whether illegal, or legal but unsustainable, leaves a lasting legacy
in the forest long after the sound of chainsaws has died away. The Sebangau
Ecosystem in Central Kalimantan was granted protected status at the
end of 2004, but the integrity of the Sebangau National Park is threatened
by old and extensive illegal logging canals which are causing drainage
and degradation of the peat soils. Although the expansion of the protected
area network to encompass habitats supporting rich biodiversity is critical,
past experience warns against complacency. No extant population, irrespective
of size and the protection status of the habitat, should be judged to
be beyond threats to its stability and continued survival. Extension
of protected areas should be followed by appropriate strategies to mitigate
the threats specific to each vulnerable area.
Orangutans are
particularly vulnerable to population declines following fragmentation
due to their large home ranges, low population densities and reproductive
rates, and demand for the pet trade. Infrastructure developments lead
to inevitable increases in habitat degradation as the forest is opened
up, facilitating access to previously undisturbed areas. Research has
estimated that 64% of orangutan habitat has already been negatively
affected by infrastructure developments, and the construction of new
roads will mean increased access to forests for hunters and poachers,
and an inevitable further decline in population numbers .
HUNTING
AND POACHING
Despite the orangutans’ position on Appendix I of the Convention
on International Trade in Endangered Species (CITES), prohibiting unlicensed
trade due to the conservation status of the species in the wild, there
is a huge local, national, and international demand for infant orangutans
to be kept as pets. Young orangutans are highly dependent on their mothers
for survival and development, and in order to obtain an infant for the
pet trade it is necessary to kill the mother. It has been estimated
that for every infant that survives the process of capture and transport,
at least 3 others will have been lost, and each of these infants also
represents the death of an adult female orangutan, the most demographically
important members of every wild population.
It is not known precisely how many orangutans are currently kept as
pets, but over 500 individuals have been confiscated and are currently
being cared for at just two rehabilitation centres in Central Kalimantan,
representing at least 2,000 infants, and 2,000 adult females that have
been removed from wild populations in one province. Additionally, orangutans
are still hunted for food in some areas, an activity which is thought
to be responsible for historical local extinctions across Borneo. Experts
have calculated that a hunting or poaching rate of greater than 1% is
sufficient to destabilise even a large population in good quality habitat,
accelerating the rate of decline beyond the impacts of habitat degradation.
It is clear that the removal of 4,000 individuals from the wild in one
province is entirely unsustainable and a significant threat to the viability
of the remaining populations.
FOREST FIRES
Around 40% of Indonesia’s legal timber supply results from land
clearance for conversion to industrial plantations. If the remaining
timber stands are not commercially valuable, burning has been a widely-used
method of land clearance. The infamous forest fires of 1997/98 were
responsible for the devastation of over 5 million hectares of forest,
and created the single largest anthropogenic CO2 event recorded.
Although undoubtedly
aggravated by years of exploitative logging and exacerbated by an El
Niño effect, the majority of these fires were triggered primarily
by palm-oil companies using uncontrolled burning to clear land, as implicated
by satellite imagery. It is believed that some palm-oil companies also
light fires in order to degrade forest land and speed up the permit-allocation
process. It has been estimated that the fires of 1997/98 alone were
responsible for the loss of one-third of Borneo’s orangutan population
– a massive step back in the conservation effort to save this
species from extinction.
SUMMARY
Orangutans are able to survive in disturbed secondary forests, albeit
at reduced densities, but logging concessions become reclassified as
“nonproductive production forest” when less than 20m3 of
commercially valuable timber species remain per hectare. Although these
severely degraded habitats would still be able to support low levels
of biodiversity, once this exploitation threshold is reached, the land
becomes available to be completely clear-cut and undergo cultivation
with plantation crops such as oil palm. Illegal and legal but unsustainable
logging in managed production forest concessions will lead to a shortage
of timber in the future, and conversion to oil palm plantations will
inevitably follow in these degraded areas, leading to greater pressure
on protected areas to supply timber.
Despite lower densities of
commercially valuable timber species relative to dry forests, the lowland
peat swamp forests of Borneo and Sumatra have undergone high rates of
commercial logging, with two particularly serious implications. Firstly,
the removal of trees causes drainage and degradation of the peat, leaving
root systems exposed and incapable of supporting the trees, leading
to the literal collapse of the forest. Additionally, alterations to
the canopy structure allow more sunlight to reach the ground, reducing
humidity. Dry peat is incredibly flammable, and uncontrollable fires
during the dry season lead to the large-scale degradation of vast expanses
of forest, leaving the area vulnerable to conversion to oil palm plantations
or other agricultural uses.
Observations carried
out by WWF and TRAFFIC indicate an increase in the trade in infant orangutans
over the last ten years. This is thought to be linked to other criminal
activities such as the illegal timber trade, and is also associated
with forest conversion, as poaching and trade is particularly common
in areas where there has been a recent increase in forest accessibility
due to infrastructure developments surrounding plantations. It was estimated
that 1,000 Bornean orangutans are lost from the wild every year to supply
markets in Bali and Java alone.
It is clear that current
rates of forest degradation and conversion are entirely unsustainable,
and these activities are inflicting irrevocable damage to forest ecosystems,
endemic species, and local communities who rely on the forest for their
livelihoods and survival.
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