| Draft Revision 2
SALONGA NATIONAL PARK,
DEMOCRATIC REPUBLIC OF CONGO
Brief description: Salonga is the world’s second
largest tropical rainforest national park and the largest in Africa. It
is isolated in the centre of the Congo river basin, accessible chiefly by
water or air and is the habitat of many endemic endangered species, notably
the bonobo (pygmy chimpanzee), the Zaire peafowl, the forest elephant and
the African slender-snouted crocodile.
Threats to the Site: Heavy poaching for bushmeat and encroachment
by militias. Salonga, with the four other World Heritage sites in the D.RC.,
now benefits from a UNESCO project financed largely by the United Nations
Foundation, to provide funding of 4.1 million dollars for the training and
equipment of conservation staff as well as for protection of the country’s
bio-diversity. The U.S. State Department has also pledged massive funding.
COUNTRY Democratic Republic
Of Congo
NAME Salonga National Park (Parc Nationale
de la Salonga, PNS)
IUCN MANAGEMENT CATEGORY
II (National Park)
Natural World Heritage Site, inscribed in 1984.
Natural Criteria ii, iii.
Listed as World Heritage in Danger in 1999
because of incursion by militias and poaching of wildlife.
BIOGEOGRAPHICAL PROVINCE Congo Rain Forest (3.02.01)
GEOGRAPHICAL LOCATION Lies in the central Congo
River basin, 100km south of Boende, midway between Kinshasa and Kisingani,
in a very isolated region accessible mainly by water or air: 1°00'-3°20'S,
20°-22°30'E .
DATE AND HISTORY OF ESTABLISHMENT
| 1970: |
Designated
a National Park by Ordinance 70-318. It is defined in law as une
réserve naturelle intégrale in the sense of the
1933 London Convention. |
AREA 3,656,000ha in two blocks separated by
a 40-45km-wide corridor. The north block, in Equateur province, is more
than 1,700,000ha, the south block in Equateur, Bandudu and Kasaï
Occidental provinces is over 1,900,000ha.
LAND TENURE Government. Administered directly
by the Institut Congolais pour la Conservation de la Nature (ICCN).
ALTITUDE 350m to 700m rising from west to east.
PHYSICAL FEATURES The Park‘s two sectors
run along a series of parallel southeast-northwest trending river watersheds,
covering three types of landscape: low swamp-forested plateaux, river
terraces and high dry-forest plateaux, each with its distinct vegetation.
In the northern block, between the Lomela and Loile rivers, valleys in
the west are large and meandering with marshy banks. In the higher land
in the east, the valleys are deeper and rivers may run below cliffs up
to 80m high. The southern block lies between the Luilaka and Lula rivers.
Soils are a thin humus layer over clayey sands with several lateritic
flushes. In the lower western valleys up to half the soil cover is hydromorphic.
CLIMATE Typically continental equatorial: hot
and humid with a mean annual precipitation of 2000mm over most of the
reserve, falling to 1700m in the south, and with a slightly drier season
from June to August. Rains are mostly downpours and on only 30 days in
the year is precipitation less than 20mm. The average relative humidity
is 86%, regularly reaching saturation at night, but maintaining an average
of 77% during the day. Temperatures are stable with daily mean variations
between 20°C at night and 30°C during the day. The mean annual
temperature is 24.5°C. Cloud cover is often complete until 10 a.m.
and is associated with fog and storms from midday to 3 p.m., but skies
are often clear at night to 4 a.m.
VEGETATION The National Park covers over a third
of the immense Salonga-Lukenie-Sankuru forest and is the second largest
almost intact tropical rainforest reserve in the world. Its high (to 45m)
equatorial forest trees cover most of the area, varying in composition
according to the geomorphology. The principal forest types are swamp,
riverine, and dry-land forests. Lowland evergreen ombrophile forest is
dominated by well-developed stands of Gilbertiodendron dewevrei
with G. ogoouense and Brachystegia laurentii. Semi-deciduous
forest covers almost all the areas between the rivers, most frequently
comprising Staudtia stipitata, Polyalthia suavaeolens,
Scorodophloeus zenkeri, Anonidium mannii and Parinari
glaberrimum. Pioneer or transitory communities are found along river
banks, including Macaranga lancifolia, Harungana madagascariensis,
Uapaca heudelotii and Parinari congensis. Flood-liable forest
species are Oubanguia africana, Scytopetalum pierrianum and Guibourtia
demeusei. Swamp forest species are Entandophragma palustre, Coelocaryon
botryoides and Symphonia globulifera. Grassland covers less
than 0.5% of the park’s area; in the northern block it is known
locally as botoka-djoku or elephant's bath. Poaceae and Cyperaceae
occur in wet soils. In the south there are natural but man-maintained
savanna-like clearings termed esobe. There is some secondary forest on
disturbed land. Species composition is yet little studied.
FAUNA Systematic faunal surveys have begun,
and most Congo forest animals seem to be present. The most important of
these is the bonobo or pygmy chimpanzee Pan paniscus (VU) which
is endemic to the Democratic Republic of Congo where fewer than 10,000
may remain. However, it has been seen in the northwest, northeast and
southeast margins of the Park (Van Krunkelsven et al.,2000). Other primates
include Angolan black and white colobus Colobus polykomos angolensis,
western red colobus C. badius (VU), Thollon's red colobus, Procolobus
badius tholloni, the endemic black mangabey Lophocebus aterrimus,
and numerous Cercopithecus species: including redtailed guenon
Cercopithecus ascanius, Salonga guenon C. dryas, golden-bellied
mangabey C. galeritus chrysogaster, Wolf's mona C. mona wolfi,
Allen's swamp monkey Allenopithecus nigroviridis, Bosman's potto
Peridicticus potto and dwarf galago Galagoides demidovi.
In savanna-like areas in the south there are several grassland-dependent
species including side-striped jackal Canis adustus, serval Felis
serval,, Grimm's duiker Sylvicapra grimmia and black-bellied
bustard Eupodotis melanogaster.
Both subspecies of elephant Loxodonta africana cyclotis (VU)
and L. a. africana (VU) used to be very common in the Park. A
few still survive years of savage poaching. Other animals include long-tailed
pangolin Manis tetradactyla, giant ground pangolin M. gigantea,
tree pangolin Manis tricuspis tricuspis, Congo clawless otter
Aonyx congica, spotted-necked otter Lutra maculicollis,
leopard Panthera pardus iturensis, African golden cat Felis
aurata (K), Angolan mongoose Crossarchus ansorgei, Congo
water civet Osbornictis piscivora, red river hog Potamochoerus
porcus ubangensis, hippopotamus Hippopotamus amphibius,
blue duiker Cephalophus monticola, yellow-backed duiker C.
sylvicultor, bay duiker C. dorsalis, water chevrotain Hyemoschus
aquaticus, sitatunga Tragelaphus spekei, bushbuck T.scriptus,
bongo T. euryceros, and pygmy Cape buffalo Syncerus caffer
nanus. Reptiles include African slender-snouted crocodile Crocodylus
cataphractus.
101 species of birds have been recorded and 153 may be confirmed. Birds
include cattle egret Bubulcus ibis, black stork Ciconia nigra
(migrant), yellow-billed stork Mycteria ibis, the African grey
parrot Psittacus erythacus, a popular species for sale, and the
endemic Congo peafowl Afropavo congensis (VU). A list of birds
from the Park has recently been compiled by Van Krunkelsven (2000).
CULTURAL HERITAGE The native Iyalima are gradually
losing their young to out-migration and their ancient independent culture
with its low-impact on the forest may decline (Thompson,in litt,
2003).
LOCAL HUMAN POPULATION A group of about 800
Iyalima inhabit the western Dekese zone in the southeast of the park in
eight villages, living in harmony with the forest. Since the Park’s
designation, their occupation of their own lands has been officially illegal.
In 2003, the Lukuru Wildlife Research Project (LWRP) initiated a move
to formalise their status under newly revised conservation laws (Thompson,in
litt, 2003). In recent decades, Bantu groups from independent African
Christian movements, some seeking refuge from state pressures, have moved
into the Park: the Kimbanguistes in the south and Kitawalistes in the
north near Lomela. Both are in contact with poachers and it has been proposed
to relocate them outside the central zone. The Bianga community in the
south survives by poaching and farming within the Park. Local farming
is based on manioc, maize and banana, with coffee, rice, oil palms and
rubber trees and, with traditional fishing, hunting and gathering, continues
in the buffer zone.
VISITORS AND VISITOR FACILITIES There is potential
for virgin forest tourism, but there have been very few visitors in the
past because of the lack of infrastructure and access, and more recently,
civil war. However, the post at Mundja is accessible by air. In 2002 the
LWRP funded clearance and maintenance of the airstrip at Anga and in 2003,
the airstrip at Monkoto, with the Wildlife Conservation Society (WCS)
and MIKE-IUCN (elephant-monitoring program). All are in the south block
(Thompson,in litt, 2003).
SCIENTIFIC RESEARCH AND FACILITIES Much of the
Park is unexplored but as early as 1973-1977 an inventory of the flora
and fauna was compiled by the Canadian International Development Agency.
In 1987 a University of Freiburg expedition (Germany) observed bonobos
on the northeastern edge of the Park. In 1989 the Wildlife Conservation
Society led the first large mammal survey in the north block, focussing
on elephants. In 1987 Salonga was selected for a forest ecosystem conservation
project for Central Africa (Écosystèmes Forestiers d'Afrique Centrale,
ECOFAC) funded by the European Commission. For this, M.Colyn (University
of Rennes, France) established a research station at Botsima at the eastern
edge of the north block where university teams worked during 1990-1. In
1994, collaboration began between the Lukuru Project and ICCN in the Dekese
zone in the southeast of the south block to study the flora and fauna,
focussing on bonobos, community relations and conservation education (Thompson,in
litt, 2003). However, during the late 1990s all research was seriously
impeded by armed poachers and civil war.
Since 1988 the Zoological Society of Milwaukee County (ZSM) has been the
headquarters of the Bonobo Species Survival Plan. In 1995 it published
an Action Plan for Pan paniscus (ZSM,1995) and since 1996 when
not interrupted by war, ZSM under its field program the Bonobo and Congo
Biodiversity Initiative, has assisted ICCN with training of Congolese
field researchers and wildlife population assessment and monitoring. In
1997-8 it part funded a two-month reconnaissance survey from Watshi-Kengo
on the northern margin of the north block run by E. Van Krunkelsven (Société
Salonga, and Royal Zoological Society of Antwerp) to begin to determine
the status and distribution of the bonobo and other large mammals in that
area (Van Krunkelsven et al., 2000). Subsequent wildlife surveys
were conducted by B. Inogwabini (ICCN/ZSM) from Watshi-Kengo between December
2000 and May 2002 to evaluate the impacts of war on large animal populations.
During March-April 1998 an LWRP-ICCN team led the first reconnaissance
and bonobo/large mammal distribution survey in the south block and collected
data on human activities. In 1999 the WCS with the IUCN-MIKE program contracted
under a UNESCO World Heritage Site/United Nations project to coordinate
a long-term large-scale survey of and bio-monitoring program for the National
Park. In 2000 the Max-Planck-Institut (MPI, Jena, Germany) with the ICCN
Mundja Post, established a long-term bonobo study site outside the western
boundary of the south block at Ipope. From 2001 the Institut and the LWRP
have collaborated with the MIKE-IUCN program, and with the WCS, have conducted
surveys along 948 km of transects between June and December 2003 to provide
a systematic and replicable assessment of data on wildlife and threats
to conservation in the National Park and surrounding areas. These data
are used to evaluate the distribution and abundance of identified species
in relation to human access by roads and rivers, human settlements, the
impacts of forestry, mining and agriculture, anti-poaching and hunting
activity, microhabitats, and areas of past species distribution and abundance.
In 2003 the Lukuru Project travelled overland to map the east and south
limits of the south block frontier in the first attempt to cross this
region and demarcate the limits of rebel occupation. This information
was integrated into the ICCN database, including habitat description,
animal signs, human activity, geography, and photographs. In 2003 MPI
and GTZ (Germany) took satellite imagery, checked in the field and by
aerial photography, of the entire Park. This will be repeated every two
years for monitoring and the map is available through ICCN to its partner
organizations (Thompson,in litt, 2003). In the past, scientific
study has been limited by lack of facilities but in the north block, ZSM
has now set up a research station in an old poachers' camp, called Etaté.
There is rudimentary accommodation for scientists at Monkoto in the northern
south block
CONSERVATION VALUE The Park is the largest nearly
intact tropical rainforest national park in Africa and the second largest
in the world. It is the habitat of a very diverse flora and fauna and
many endemic endangered species, such as the bonobo (pygmy chimpanzee),
for which it was partly founded to protect, the Congo peacock, the forest
elephant and the African slender-snouted crocodile.
CONSERVATION MANAGEMENT The Park is the only
part of the Congo basin where the bonobo is nominally protected. In 1985
IUCN and WWF representatives visited and made several recommendations.
They suggested that increased effort should go towards improving knowledge
of the region: making the area's people more aware of the value of the
park, and if possible involving them in management activities; improving
the information on the relationship between the local people and the park's
ecosystems, such as studies in ethno-botany; improvement of the park's
infrastructure and building a research station (IUCN/WWF,1985). Civil
wars in 1996 and from 1998 paralysed conservation, but as they subside,
effective ICCN activity and help from outside the country have been restored.
ZSM's field program has assisted ICCN in the north block, as the Lukuru
Project has done in the south block, with emergency relief aid of materials,
funding for guards' salaries, guard training, equipment and medicines,
training of Congolese field researchers, wildlife population assessment
and monitoring; also by working with grassroots conservation education
groups. Both ZSM and LWRP have distributed the grants from UNESCO and
supplies funded by USAID to ICCN guardposts. ZSM created an anti-poaching
program in which river patrols and cable barriers across the Yenge river
have proved very effective; and the LWRP with the long established NGO
Nouvelles Approches founded and administered the DRC Parks Emergency
Relief Mission from 1997 and has assisted UNESCO, UNF and ICCN in the
field since 2001. By mid 2002 the Relief Mission, had delivered through
several projects, household supplies, medicines, equipment, salaries,
and educational resources and helped to restore the morale and effectiveness
of the guards by securing uniforms. The Park headquarters at Anga which
collapsed in 1999, is being reconstructed by the Project and airstrips
cleared at Anga and Monkoto posts. ZSM and LWRP are actively engaged in
fieldwork with the Wildlife Conservation Society, the Max-Planck-Institut
at Lui-Kotal and GTZ in biodiversity surveys and inventorying wildlife
abundance, distribution and threats, in capacity building and contribution
to the ICCN management plan, in increasing ICCN's capacity for surveillance
and security, in building relations between the people and ICCN throughout
the region, and in continued exploration of the Park (Thompson,in
litt, 2003).
A management plan for each guard post was developed in 2002 and for the
whole Park in 2003 when the IUCN-MIKE program and collaborators undertook
training for bio-monitoring inventory and survey work for park guards
at the Lokofa camp. To date, a policy of non-management has been followed
to avoid unexpected disturbance to the ecological balance and to allow
natural evolution of the ecosystems. Exploitation of the natural forest
occurs, but there is no plan for its reforestation or management. A scientific
management strategy has been adopted to provide technical and scientific
assistance to the management and monitoring of the Park and promote the
integrated development of peripheral areas.
MANAGEMENT CONSTRAINTS Though the Park was originally
far from the conflict in the east, it has many navigable rivers, and has
long been open to uncontrolled poaching, especially for ivory, but also
more recently for bushmeat including bonobos, eating which was tabu in
the Salonga region until the war. Civil conflict in 1996 and from 1998
paralysed transport, leading to increased reliance on bushmeat, especially
by the militia, However, war caused major economic collapse throughout
the D.R.C. In Salonga, no river patrols were run between 1990 and 1997
and infrastructure was destroyed. Guards were killed by armed poachers
seeking ivory and bushmeat and went unpaid for years. They were undertrained,
under-equipped, understaffed and stripped of their arms and uniforms by
the militia. Heavily armed soldiery have reinforced native poachers using
both traditional and modern methods to considerably reduce the numbers
of elephant and grey parrot, though recent investigations have found that
elephants and many primate species still exist (Van Krunkelsven et al.,
2000; Thompson,2002). There are also impacts from invading Bantu groups,
local population pressures, from shifting cultivation, tree cutting and
honey gathering and, in the south, habitat destruction by fire. More serious
still is the lack of sufficient management infrastructure, professional
trained staff and management planning; and patrol and communications equipment
are still lacking.
From 2001, the Rwandan RCD-Goma militia (Rassemblement Congolais pour
la Democratie), based in Goma) has controlled Zone Dekese, the southeastern
sector of the Park. This is within the area of the Lukuru Project which
negotiated authorisation to work in this sector from both the government
and from the rebel authorities (Thompson, in litt, 2003). In
the north, only government soldiers ensured the safety of expeditions
(Draulens & Van Krunkelsven, 2002). The partner NGOs, ZSM in the northwest,
LWRP in the southeast, hired local staff who braved long distances and
insecure conditions to pay guards, labourers and other staff from funds
made available by the UNESCO/DRC/UNF Project. Poaching in the site continues;
the number of staff working in the Park is totally inadequate for the
huge area where access is extremely difficult. The ability of ICCN, Kinshasa,
to manage this and other protected areas under its authority may improve
after a GTZ project re-started in 2002. This GTZ project recommenced payments
to several ICCN-Kinshasa staff and provided other basic needs such as
vehicles and travel allowances that would enable ICCN to better protect
Salonga and other protected areas under its direct supervision.
STAFF In 1990 there were 150 guards with 7 officers
under the Chief Conservator at Anga and his deputy, the Conservator. There
are now six staff posts staffed by ICCN: 3 in the north block, at Watshi-Kengo,
Mondjoku and Lomela and three in the south block, Monkoto, Mundja and
Anga. Staff numbers have not been recently confirmed.
BUDGET In 1987 this was approximately 300,000
zaïres. From 1997 LWRP organized and delivered supplies and resources
of every kind to ICCN posts (Thompson, 2003). In 1999 the United Nations
Fund promised US$ 4,186,600, two-thirds of it outright, to compensate
staff and pay salaries and allowances for all five D.R.C. World Heritage
sites from 2000-2004. Almost US$200,000 was pledged for the protection
of the bonobo by the ZSM. In 2000 the Belgian government also promised
US$500,000 for the five D.R.C.parks from 2001-2004 (UNESCO, 2001). In
2002 at Johannesberg the U.S.Government proposed to invest up to $53 million
dollars in the Congo Basin Forest Partnership through 2005. The Salonga
region will be among the beneficiaries (USDS, 2003).
ADDRESSES
M. le Président Délégué Général,
Institut Congolais pour la Conservation de la Nature (ICCN), Avenue des
Cliniques 13, BP 868, Kinshasa 1, Democratic Republic of Congo.
M. le Conservateur Principal, Parc National de Salonga, BP 10 à
Monkoto (via Boende), Region de l’Equateur, Democratic Republic
of Congo.
REFERENCES
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Report to IUCN, Gland, Switzerland, 64pp.
Doumenge, C. (1990) La Conservation des Ecosystèmes
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U.K.
Draulens ,D. & van Krunkelsven, E. (2002). The impact
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IUCN/WWF (1985). Rapport d'une Mission au Zaïre et
Rwanda. IUCN/WWF, Gland, Switzerland.
Meder, A.,Herman, P.& Bresch, C.(1998).Pan paniscus
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UNESCO/IZCN/IUCN (1987). Premier Seminaire Internationale
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UNESCO World Heritage Committee (2001). Report on
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UNESCO World Heritage Committee (2002). Report
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United States Department of State (USDS), Bureau of Oceans
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Basin Forest Partnership - U.S.Contribution.
Van Krunkelsven, E. (2000). A first list of birds from Salonga National
Park, Congo. Gerfaut, 87.
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Vogel, G (2000). Conflict in Congo threatens bonobos and rare gorillas.
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World Heritage Nomination Form submitted to UNESCO, 1988.
DATE 1984. Updated 5/1990, 2/2002, 7/2003, Updated
Oct.2003. |