Tropical rainforests sustain a large portion of the world's biological diversity and are vanishing more rapidly than any other biome (Laurance 1999, Achard et al. 2002). In Africa, tropical rainforests are mainly confined to an equatorial belt of varying width as vegetation change is more strictly associated with latitude (Terborgh 1992). African vegetation zones roughly form a series of parallel bands across the continent that correspond to rainfall patterns. Evergreen forests occur in a narrow band along the coasts of West Africa and Central Africa, and across the Congo Basin into East Africa. Because of their high biological diversity and uniqueness, African rainforests are a top global conservation priority (Olson and Dinerstein 1998; Kamdem-Toham et al. 2003; Mittermeier et al. 2004).
Well over half of all African rainforests have been cleared and fragmented, mainly from slash-and-burn farming. Forest loss has been most severe in West Africa, which currently has <12% of its original rainforest (declining from 1.25 to 0.15 million km²), and in eastern Africa, which has 8% of its original rainforest (declining from 0.36 to 0.03 million km²). In contrast, Central Africa's forests still comprise almost 60% of their original distribution (Naughton-Treves and Weber 2001).
Forest destruction has been fueled by the rapid growth of human populations and also by extensive road building for logging, oil, mineral, and infrastructure projects, which have greatly increased access to forests (Wilkie and Laporte 2001). Additionally, the total harvest of wildlife in the Afrotropical region is estimated to be about 5 million tons annually, making it the most intensively hunted tropical region in the world (Fa et al. 2002). Recurring wars, political instability, disease epidemics, and endemic corruption are also serious impediments to forest conservation. In recent years, nearly one-third of the 42 sub-Saharan countries in Africa have been involved in international or civil wars. As one example, as a means of combatting rebels in the eastern half of the country, the Democratic Republic of Congo (DRC) (formerly Zaire) has bartered access to timber, gemstones, and minerals to Zimbabwe, Uganda, Rwanda, and Burundi in exchange for military support (Vedder et al. 2001).
The Congo Basin Forest, also referred to as the Lower Guineo-Congolian Forest, comprises the second largest block of tropical rainforest on Earth. The Congo Basin Forest extends from the coast of the Atlantic Ocean in the west to the Albertine Rift in the east, and spans the equator by nearly 7 degrees north and south. This forest block is one of two remaining regions on Earth that still boast large interconnected tracts of tropical rainforest.
Current biodiversity patterns in the Congo Basin date to the Pleistocene epoch (15,000–250,000 B.P.). The last great ice age, which peaked about 18,000 years ago, had a profound influence on biodiversity in this region. Cool, dry conditions existed at the equator during the peak of the ice age when much of North America and Europe were covered by a thick sheet of ice. The dry conditions in the tropics created isolated forested refugia. With repeated expansions and contractions of these forests during the Pleistocene, the flora and fauna experienced considerable isolation and speciation. These refugia included forested mountains to the west and east of the Congo Basin and vast swamps within the Congo Basin (Colyn et al. 1991; Maley 1996; White 2001). As the climate warmed and the ice cap receded, equatorial forests in the Congo Basin and neighboring highlands greatly expanded to, once again, cover the Congo Basin.
The majority of the Congo Basin Forest lies within the Democratic Republic of Congo (DRC), the third largest country in Africa, covering some 2,344,000 km² at the center of the continent. Overall it is the single most biologically rich country in Africa, and, in terms of species richness, is near the top of the list for Africa for virtually every group of organisms. Evergreen forest canopy composition varies, from highly diverse mixed forests to forests dominated by one or a few tree species. Particularly noteworthy are the mono-dominant forests where a single species, Gilbertiodendron dewevrei, represents from 60% to over 80% of the canopy. DRC harbors important communities of megafauna, including gracile chimpanzee or bonobo (Pan paniscus), robust or common chimpanzee (Pan troglodytes), eastern gorilla (Gorilla beringei), forest elephant (Loxodonta cyclotis), and the okapi (Okapia johnstoni). DRC also has the second largest river system on Earth, the Congo, and one of the most diverse freshwater fish faunas. Conservation International (CI, Mittermeier et al. 2003) has identified the Congo Basin Forest as one of five High Biodiversity Wilderness Areas. As such, conservation of the Congo Basin Forest is a global biodiversity conservation priority.
Lokutu
Lokutu (formerly named ‘Elizabetha’), within the Territory of Basoko, DRC, lies on the southern boundary of the northern-most extent of the Congo River and still has forested areas, some of them within Unilever's Lokutu Oil Palm Plantation concession (N 01° 08′ 43.2 2″ E 23° 36′ 53.7″)). The climate at Lokutu is probably very similar to that for Kisangani, 250 km up the Congo River to the east. At Kisangani, the mean annual temperature is approximately 25o C. Climate type is equatorial (Stock 2004) with no monthly mean temperature below18°C. Mean monthly rainfall is between 100 mm and 199 mm (Stock 2004). Total annual rainfall varies between 1400 mm and 2200 mm (Goudie 1996). Thus, there is little seasonality in the climate of the region, although rainfall tends to be highest during April and October (Anon. 2005). The soils of the area are pedalfers (ferrasols) (Areola 1996), acidic soils in which iron and aluminum oxides have accumulated.
Lokutu Plantation Concession (630 km²) was granted in 1911 and the first oil palms (Elaeis guineensis) were planted in 1922. Today, this is an active plantation of which ca. 100 km² are covered with oil palm (and some cocoa and coffee). The remaining ca. 530 km² are lightly to heavily degraded (i.e., covered with secondary forest, scrub, fallow fields, or garden crops grown by plantation workers and settlers — especially cassava and bananas). At one time, the Lokutu area was completely covered with lowland moist forest (Grainger 1996). The plantation has been cleared except for narrow strips of forest along streams and rivers, and two (ca. 50 km² each) forest blocks in the northwest of the concession. These two blocks, as well as the forests surrounding the Plantation, have been selectively logged.
Lokutu Plantation employs ca. 1,900 people. The total population of the Lokutu area is ca. 10,000 people. During this survey, the streams and rivers within the interior of these forests were flowing normally for this time of year.
Lokutu is located in the northeastern section of the region south of the Great Bend of the Congo River, sometimes referred to as the Cuvette Centrale. Lokutu is adjacent to the Maringa-Wamba-Lopori landscape, targeted for conservation and development activities under the Congo Basin Forest Partnership (CBFP). Despite the high conservation importance of this landscape, there are no protected areas in this region. Lokutu forms a significant demographic and economic center in this otherwise sparsely populated area.
A first short survey of the area around the village of Lokutu in September 2002 examined the opportunity of an involvement of CI in the logging and oil palm concession of Unilever. A CI team reported the area to be of little or negligible conservation value. We investigated this statement with a much stronger biological emphasis. On the basis of a two-week survey, we herein present a preliminary inventory of the flora and fauna of the Lokutu region.
RAP STUDY SITES
We conducted surveys during the dry season over 14 days (25 October – 8 November 2004) in forests within and near Unilever's Lokutu Plantation Concession. Surveys focused mainly on four forest sites (see Map, Table 1.1). Lobolo (Site 2) is located ca. 31 km to the northwest of Lokutu Village, and Lukumete (Site 4) is located about ca. 26 km to the northwest of Lokutu Village. AshortflightovertheareaA short flight over the area confirmed that a large part of the forest around Lokutu Village had been either destroyed or heavily altered for oil palm plantations and other agricultural uses.
The original RAP plan was to survey sites far to the south of Lokutu, beyond where significant levels of logging or hunting would have occurred. The data from such sites would have provided a useful baseline and insights into what species of plants and animals might have been present at Lokutu prior to the establishment of the oil palm plantation and the related large influx of people. However, due to permit restrictions and the inflexibility of the local authorities, we had access to only a few selected areas of slightly to highly degraded natural forests within and close to the Lokutu Plantation. This was a severe impediment to our evaluation of the Lokutu area as a site for conservation investment and action. Nevertheless, while we were unable to compare low impact sites with the high impact sites we surveyed, our conclusions regarding the current value of the Lokutu Oil Palm Plantation as a site for conservation are firmly grounded.
Table 1.1. Principal survey sites in the Lokutu area, Democratic Republic of Congo.
THREATS TO BIODIVERSITY
Africa's tropical rainforests and wildlife have been severely degraded in recent decades by many threats, including industrial logging, slash-and-burn agriculture, over-hunting, disease and increasing infrastructure development. In DRC, vast timber leases have been granted to Zimbabwean, German, Malaysian, and Chinese corporations. Logging has important impacts on tropical ecosystems and wildlife (Malcolm and Ray 2000; Laurance et al. 2006), but often its most pervasive effects are secondary: by creating extensive networks of roads and bulldozer tracks, logging greatly increases physical access to forests for hunters, miners, and farmers that can severely degrade or destroy forests (Wilkie et al. 1992; Laurance 2001).
As the human population has increased, traditional forms of forest exploitation, like the gathering of fuelwood and building poles, have grown sharply. Hunting pressure is growing rapidly throughout Central Africa, as road networks expand and the area of forest accessible to hunters increases (Wilkie et al. 1992; Barnes et al. 1997; Fa et al. 2005). Moreover, the efficiency of hunters has increased because shotguns and cable snares have replaced traditional cross-bows, spears, nets, snares made from bush rope (Noss 1998; Lahm 2001). Few remaining areas of forest are inaccessible to hunters (Wilkie et al. 2000). Populations of hunted wildlife, especially larger-bodied species like duikers, buffalo, elephants, monkeys and apes, have declined sharply within 10–15 km of villages and roads (Barnes et al. 1991; Lahm et al. 1998, Fa et al. 2000; Lahm 2001). In addition, commercial hunters use hunting and logging camps to penetrate deep into remaining forest tracts (Wilkie et al. 1992; 2000; Lahm 2001).
Wild meat is a key protein source in rural areas and is favored in towns and cities. Improved road networks drive a burgeoning commercial bushmeat trade (Milner-Gulland et al. 2003). Hunting typically contributes between 30 to 80% of protein consumed by forest-dwelling families in the Congo Basin (Koppert et al. 1996), representing almost all animal-based protein consumed. It is estimated that more than 1 million tons of antelope, pigs, rodents and other wildlife are killed and eaten every year in Central Africa (Wilkie and Carpenter 1999). Of 57 mammal, bird, and reptile species hunted in the Congo Basin, 60% are exploited unsustainably (Fa et al. 2002).
In DRC, the human population is expected to double (from 50–60 million to 100–120 million) by 2020 (CBFP 2005). Human population pressure is the root cause of many of the threats mentioned above, driving demand for natural resource consumption in DRC. Immigration to DRC from West Africa is also likely to increase, exacerbating demands on the natural resource base.
Armed conflicts in countries neighboring DRC (Rwanda, Burundi, Uganda, Congo, Sudan, Central African Republic, and Angola) have killed millions of people with associated impacts on forests, wildlife, and national-park staff and infrastructure. In eastern DRC, fighting has pushed refugees west and has also displaced rural populations away from major roads and into the forest and protected areas where they are less likely to encounter soldiers and armed bands. Such conflict-triggered displacement has significant ecological and social impacts (CBFP 2005). Moreover, corruption is a serious impediment to conservation. In a recent report commissioned by the European Community, a complete moratorium on logging in five African nations — including DRC — was recommended in response to issues of corruption (Laurance 2000; Sizer and Plouvier 2000).
OPPORTUNITIES FOR CONSERVATION
Recent developments in the Congo Basin Forest are working to address the situation and propel conservation forward. In March 1999, six heads of state from Central African nations signed the ‘Yaoundé Declaration.’ This Declaration contains commitments to forest conservation and sustainable forest management, including conserving, in protected areas, a minimum of 10% of each nations' forests (Kamdem-Toham et al. 2003). Since 1999, there has been a 36% increase (40,607 km²) in the coverage of protected areas across the region's forests. In Gabon, 13 new national parks covering 30,000 km² (10% of the country) have been gazetted, and similar processes are underway in Cameroon, Congo, Equatorial Guinea and DRC.
The Congo Basin Forest Partnership (CBFP) conservation activities focus on 11 landscapes that were selected by more than 160 regional and international experts at a workshop in Libreville in April 2000. Landscapes were selected because of their outstanding biodiversity (including their concentration of endemic species), because they encompass intact populations of larger mammals (e.g., elephant, buffalo, robust chimpanzee and gorilla in forest wilderness), or because they represent important and distinctive habitats and communities of species. Priority landscapes represent zones within which conservation should play a prominent role, through various activities in protected areas and corridors, and through sustainable forestry management and community-based natural resource management. Within these landscapes, the CBFP is working with a range of government and nongovernmental organizations to conserve biodiversity and promote sustainable land use practices.
REFERENCES
1
2
Anonymous 2005ClimateControls. Climographs/Africa. Climate Controls.Climographs / Web site: http://people.cas.sc.edu/carbone/modules/mods4car/ccontrol/questions/africa.htmlGoogle Scholar
3
AreaolaO. 1996Soils.In AdamsW. M. A. S.Goudie A. R.Orme (eds.)The Physical Geography of Africapp134147Oxford University PressOxford, UKGoogle Scholar
4
5
6
[CBFP] Congo Basin Forest Partnership 2005The Forests of the Congo Basin: a Preliminary Assessment.Available online, 15 Oct 2006. http://carpe.umd.edu/products/PDF_Files/FOCB_APrelimAssess.pdfGoogle Scholar
7
8
9
10
11
GoudieA. S. 1996Climate: past and present.In AdamsW. M. A. S.Goudie A. R.Orme (eds.)The Physical Geography of Africapp3459Oxford University PressOxford, UKGoogle Scholar
12
13
KoppertG. J. A. E.Dounias A.Froment P.Pasquet 1996Consommation alimentaire dans trois populations forestières de la region côtière du Cameroun: Yassa, Mvae et Bakola.In HladikC. M. A.Hladik H.Pagezy (eds.)L'alimentationen for êttropicale. Interactions L'alimentation en forêt tropicale. Interactions bioculturelles et perspectives de développementpp477496OrstomParisGoogle Scholar
14
LahmS. A. 2001Hunting and wildlife in northeastern Gabon: why conservation should extend beyond park boundaries.In WeberW. L. J. T.White A.Vedder N.Naughton-Treves (eds.)African Rain Forest Ecology and Conservationpp344354Yale University PressNew Haven, CTGoogle Scholar
15
16
17
18
19
20
21
22
23
MittermeierR. A. P. R.Gil M.Hoffmann J.Pilgrim T.Brooks C. G.Mittermeier J.Lamoreux G. A. B.da Fonseca 2004Hotspots RevisitedCemexMexico CityGoogle Scholar
24
25
Naughton-TrevesL. W.Weber 2001Human dimensions of the African rain forest.In WeberW. L. J. T.White A.Vedder N.Naughton-Treves (eds.)African Rain Forest Ecology and Conservationpp2046Yale University PressNew Haven, CTGoogle Scholar
26
27
28
SizerN. D.Plouvier 2000Increased Investment and Trade by Transnational Logging Companies in Africa, the Caribbean and the Pacific.Joint report of the World Wide Fund for Nature-Belgium, World Resources Institute, and WWF-InternationalGoogle Scholar
29
StockR. 2004Africa South of the Sahara: a Geographical Interpretation2nd EditionThe Guilford PressNew York, USAGoogle Scholar
30
TerborghJ. 1992Diversity and the Tropical Rain ForestW.H. Freeman and CompanyNew YorkGoogle Scholar
31
VedderA. L.Naughton-Treves A.Plumptre L.Mubalama E.Rutagarama W.Weber 2001Conflict and conservation in the African rain forest.In WeberW. L. J. T.White A.Vedder N.Naughton-Treves (eds.)African Rain Forest Ecology and Conservationpp557562Yale University PressNew Haven, CTGoogle Scholar
32
WhiteL. 2001The African rain forest: climate and vegetation.In WeberW. L. J. T.White A.Vedder N.Naughton-Treves (eds.)African Rain Forest Ecology and Conservationpp229Yale University PressNew Haven, CTGoogle Scholar
33
34
WilkieD. S. N.Laporte 2001Forest area and deforestation in central Africa: current knowledge and future directions.In WeberW. L. J. T.White A.Vedder N.Naughton-Treves (eds.)African Rain Forest Ecology and Conservationpp119139Yale University PressNew Haven, CTGoogle Scholar
35
36