- Research article
- Open Access
The relationship between the abundance of the Nigeria-Cameroon chimpanzee (Pan troglodytes ellioti) and its habitat: a conservation concern in Mbam-Djerem National Park, Cameroon
BMC Ecology volume 18, Article number: 40 (2018)
Understanding the relationship between great apes and their habitat is essential for the development of successful conservation strategies. The chimpanzee Pan troglodytes ellioti is endemic to Nigeria and Cameroon, and occupies an ecologically diverse range of habitats from forests to forest-savannah mosaic in Mbam-Djerem National Park (MDNP) in Cameroon. The habitat variation in chimpanzees is poorly understood in MDNP which provides an excellent opportunity to assess ecological factors that shape the abundance and distribution patterns of P. t. ellioti over a small geographic scale.
We counted 249 nests along 132 km of transects in total. Of these, 119 nests along 68 km occurred in dense forest and 130 nests along 64 km in forest-savannah mosaic. Chimpanzee density was 0.88 [95% CI (0.55–1.41)] individuals/km2 in the dense forest and 0.59 [95% CI (0.19–1.76)] in the forest-savannah mosaic. Nest abundance varied with vegetation type and was higher in areas with dense canopy cover, steeper slopes and relatively higher altitudes.
Our estimates of chimpanzee densities were lower than reported in other studied populations in the range of the Nigeria-Cameroon chimpanzee. However, we found that habitat features, slope and altitude likely play a role in shaping patterns of chimpanzee nesting ecology. Further studies need to be focused on nest decay rates and phenology of useful plants in order to model chimpanzee abundance and distribution in Mbam-Djerem National Park.
Great ape populations are currently threatened by hunting, habitat loss and infectious diseases [1, 2]. Understanding the relationship between each great ape species and its environment is therefore crucial for developing conservation policy . For chimpanzees, key requirements such as food and nesting materials are sensitive to environmental variation, including climate change and other anthropogenic factors such as habitat conversion and poaching. However, monitoring chimpanzee population size is inherently difficult, and few studies have demonstrated clear links between habitat variation and conservation value [4, 5]. The Mbam-Djerem National Park (MDNP) in Cameroon offers an excellent opportunity to assess ecological factors shaping the abundance and distribution of the Nigeria-Cameroon chimpanzee (Pan troglodytes ellioti) over a small geographic extent in the core zone of the protected area, which includes both dense forest, colonizing forest and savannah ecosystems. Until now, the distribution pattern and abundance of the Nigeria-Cameroon chimpanzee has not been completely understood in MDNP which may hamper their long-term conservation. Our research highlights this issue by providing data on chimpanzee density and the environmental drivers affecting their distribution. Moreover, as the forest is currently expanding  and replacing savannah in MDNP , understanding how chimpanzees use different habitats can inform conservation efforts by providing key monitoring parameters on behalf of this species.
Studies of the subspecies P. t. ellioti in the dry and gallery forests of Nigeria in Gashaka-Gumti National Park , in Cameroon at Ebo Forest  and MDNP have so far failed to address the relationship between abundance and habitat characteristics. Differences between chimpanzee populations regarding ecology, social organisation and genetics [10, 11], population size , home range size , feeding habits [14, 15] and nesting behavior  have been described, and appear to be related to differences in habitat types [17, 18], but few studies have quantified how these factors impact local population sizes and habitat use . Habitat assessment between Mahale Mountains and Gombe in Tanzania , at Lagoas de Cufada National Park in Guinea-Bissau , and between forests of Western Uganda  and Mount Assirik in Senegal [13, 14, 22] are examples of studies comparing chimpanzee ecological behavior across habitat types. Other studies have explored chimpanzee diet and habitat selection in the Democratic Republic of Congo  and in Uganda , and nesting ecology in Nigeria [24, 25] and Tanzania . Little is known, however about the Nigeria-Cameroon chimpanzee in MDNP.
The Nigeria-Cameroon chimpanzee was recognized since 1997 as the fourth subspecies of chimpanzees [26,27,28] and is the least studied among all subspecies of chimpanzees. Classified as Endangered by IUCN , with between 3500 and 9000 individuals remaining [25, 28, 29], their populations size is declining across their limited natural range . As is the case for other subspecies of chimpanzees, landscape fragmentation, habitat loss, disease, commercial bushmeat hunting and climate change are all substantial threats to the conservation of the Nigeria-Cameroon chimpanzee . The conservation status of this subspecies may also change rapidly in response to habitat change . It is therefore important to explore how habitat variation impacts the density and distribution of local chimpanzee populations.
Emerging methods such as the use of infra-red camera , the use of drones  and genetic material are also appropriate to reliably estimate the density and distribution of chimpanzee communities , but these studies are currently limited to relatively small areas and are outside the budgetary capacities of most protected area management plans within the country. Studying the distribution of nests is currently the most efficient means to estimate the distribution and density of chimpanzee populations [12, 33]. Although evidence of presence such as direct sighting, feeding remains and footprints are still frequently used to derive densities of chimpanzees, the most robust method of estimating population density continues to be based on nest counts . The main objective of this study was to estimate the density of the Nigeria-Cameroon chimpanzee in two main habitat types within the MNDP, namely forest-savannah mosaic and dense forest, and to study the nesting ecology of chimpanzees in these two main habitat types. We investigated how habitat variation in the forest-savannah mosaic and in the dense forests affects chimpanzee distribution in MNDP, and the importance of the availability of nesting materials, canopy cover, understory, slope and altitude. The results will help to design regular monitoring activities focusing on chimpanzee habitat suitability and to shape effective management practices in MDNP. Key activities might be focused on the phenology of useful plants for chimpanzees as well as human encroachment in their suitable habitats. Furthermore, the findings will be relevant to the update of the imminent revision of the 2011 IUCN Regional Conservation Action Plan for the subspecies .
Mbam and Djerem National Park
Created in 2000, MDNP covers 4165.2 km2 and lies between 5°30′N and 6°14′N, and 12°20′E and 13°15′E  (Fig. 1). The rainy season extends between mid-April and mid-October and a dry season between mid-October and mid-April. Average rainfall is 1900 mm/year, average annual temperature is 24 °C . The area lies within the Guinea-Congolia/Sudania regional transition zone, between the Soudanian regional centre of endemism in the north and the Guinea-Congolian forest block in the south . The vegetation of the MDNP grades from savannah in the northwest through forest-savannah mosaic to closed canopy humid forest in the south-west  (Fig. 1). The relief is relatively flat and the altitude ranges from 650 to 930 m above sea level (a.s.l.). Approximately 30,000 human inhabitants live in 74 villages at the periphery of the MDNP . These people mostly depend on natural resources for their food, traditional medicine and income. The human population tends to be concentrated in the northern periphery where grazing lands are available and where the Mbakaou Dam was constructed in 1964, and in the eastern periphery of the MDNP where the Belabo-Ngaoudéré railway link is found as established in 1970  (Fig. 1).
We used data from a transect survey for large mammals collected between 2009 and 2014 to design a sampling plan for the assessment of chimpanzee density at MDNP. We used the encounter rate of chimpanzee nests derived from these previous surveys as an indicator of the effort required to obtain a density estimate. The coefficient of variation of 15% for forest-savannah mosaic and 20% for dense forest were chosen to perform equation 7.3 .
Thus, given the encounter rates of 1.7 nest/km and 0.93 nest/km, we found that 80 km and 88 km of effort, respectively in forest-savannah mosaic and in dense forest, were required to assess the chimpanzee nest density with the defined target precision. The effort to reach the specific target coefficient of variation was calculated using the value of 3 as dispersion parameter (b) in equation 7.3. Using these results, we developed a population survey protocol that included 84 transects of 2 km each (Fig. 2). The core zones included two strata (based on the physiognomy and structural characteristics using satellite imagery Landsat TM of April 2011) within the forest-savannah mosaic in the north and the dense forest in the south.
Standing crop nest count
Chimpanzees are elusive, difficult to see and occur at relatively low densities [28, 38,39,40], thus requiring an indirect method for density estimation. Nest counts are often used as all weaned chimpanzees from around 3 years of age generally build a night nest to sleep in . We used the standing crop nest count (SCNC) method [42, 43] to estimate the density of chimpanzees by completing unrepeated transects to count nests from January to June 2016 at MDNP. Two survey teams of six persons each comprising one MDNP biologist team leader, two rangers and three local guides were established. The teams were trained on the use of CyberTracker to collect field data following the Wildlife Conservation Society protocol . Along each transect, the coordinates of each nest were recorded as well as the age class of each nest. The age class of each nest was classified using the system developed by Tutin and Fernandez  as fresh (vegetation is still green, leaves are not yet wilted and urine and faeces may be present at the site); recent (nest contains leaves that are green but wilted); old (nest has leaves that are no longer green but remain intact); and rotting (nest has shed its leaves, leaving only bare branches).
Predicting the influence of habitat attributes on wildlife is useful for conservation and protected area management [45,46,47,48]. While walking along transects, we examined a set of variables to assess the habitat used by chimpanzees. For each nest encountered, we recorded the distance along the transect with a topofil, the perpendicular distance to the transect line of each nest spotted from the transect (using tape measure), the type of nest, the height above ground, the tree height, the tree species, and the diameter at breast height (dbh) of the tree (i.e. at 1.3 m above ground), the slope of the site, the vegetation type, the canopy cover and the age class of each nest in the nesting site. Slope was defined according to the following scheme: 0 = flat, 1 = low, 2 = moderate and 3= steep. Nest type was defined according to  as (a) Minimum (terrestrial nest with one or two stems of herbaceous plants); (b) Mixed (terrestrial nest with herbaceous plants and woody vegetation); (c) Tree (nest made in tree). The canopy cover was assigned as open (0–25%), low closure (26–50%), moderate closure (51–75%) and high closure (> 75%).
Habitat type included seven categories : (a) Colonising Forest (CF); (b) Gallery Forest (GF); (c) Liana Forest (LF); (d) Marantaceae Forest (MF); (e) Mixed Forest with Closed Understory and Marantaceae (MFCUM); (f) Mixed Forest with Closed Understory (MFCU); (g) Mixed Forest with Opened Understory (MFOU). These habitats are described in detail in Additional file 1. The plant species used for nesting were identified in the field. We used the Garoua Wildlife School herbarium to identify nesting plants from field samples. We assessed the relationship between habitat type and nest density using several parameters, including number of nests, nest height, dbh of the nesting tree, and encounter rates of nest sites registered for each strata and habitat type. We conducted non-parametric Kruskal–Wallis tests to compare dependent variables across habitat types and strata. We also used General Linear Models and contingency table  to explore the effects of habitat attributes (e.g. plant species, dbh of the nesting tree, slope, understory, canopy cover and altitude) on the nesting sites (e.g. nest abundance, nest height, nest encounter rate). We used the software program R for these analyses .
Estimating chimpanzee density, population size and distribution
Converting nest density into an estimate of chimpanzee density requires two parameters: a nest production rate and a nest decay rate [41, 42, 52]. Nest decay data were not available for MDNP. Therefore, similar to other studies where reliable nest production and decay data were unavailable, we used a range of possible nest decay rate values from previous studies [33, 52] to estimate the density of chimpanzees for this study. Nest production rates are estimated by averaging the number of nests built per day by a weaned chimpanzee from direct monitoring of habituated chimpanzees to then assess potential nest production rates in the given study site [42, 53]. Weaned chimpanzees generally make new sleeping nests every night  but they also sometimes build day nests in which to rest. Allowing for this, we used a value of 1.09 (± 0.5) nests per day reported in previous research [39, 42] for the present study.
Measuring nest decay rates is more challenging, as it involves monitoring a sufficient number of fresh nests from the time they are built to the time they disappear . In addition, nest decay rates may vary considerably depending on the plant species used to build the nest and the local climatic parameters and therefore vary considerably between sites and vegetation type ; thus carrying an associated error which may affect the precision of density estimates [33, 53, 55]. Moreover, climate can affect the rate of re-use and building of nests as well as decay rates [21, 39, 54, 56]. Observations in Ebo Forest, Cameroon, which is close to the MDNP, suggest a nest decay rate of 88.2 (± 7.1) days. This is similar to the estimate from the Taï forests in the Ivory Coast (91.22 ± 5.8 days) . Both MDNP and Ebo forest are found in the northern side of the Sanaga River and within the same climatic domain of Cameroon (2°–6° of northern latitude), with a similar amount of annual rainfall (2400 mm in the Ebo Forest and 1900 mm in the MDNP). Much uncertainty remains, however, in these estimates [43, 57]. A value of 221 days was previously used in the MDNP to convert nest density into chimpanzee density. To assess the sensitivity of the density estimate to nest decay rate, we also used 120 and 221 days.
Conversion of nest density to chimpanzee density
We used the Distance 7.0 Program to derive nest and chimpanzee density estimates [37, 58]. This program implements a series of detection function models with their expansion series acquired from the data set (Additional file 2) to estimate the chimpanzee density by inference from the nest density . Different models are then compared based on the Akaike Information Criterion .
Single nests have been used to estimate chimpanzee nest density [12, 59]. Chimpanzee density was then derived from nest density using conversion parameters (nest production rate, nest decay rate and the proportion of nest builders).
We calculated encounter rates of nest sites for each transect and used this information to develop Inverse Distance Weighting-IDW interpolation using 30 neighbors and a power of 2 in ArcGIS 10.1 software [60, 61]. The corresponding raster layer was extracted by mask and exported as PNG file.
The model fits for the nest counts were as follows: hazard-rate simple polynomial truncated at 20 m of perpendicular distane for all data (Fig. 3a), Hazard-rate simple polynomial truncated at 25 m in the forest-savannah mosaic (Fig. 3b) and Hazard-rate cosine truncated at 20 m in the dense forest (Fig. 3c).
Chimpanzee density at Mbam-Djerem National Park
A total of 32 transects were surveyed in the forest-savannah mosaic and 34 transects in the dense forest. We observed 249 nests from these transects, of which 119 nests occurred in dense forest and 130 nests in forest-savannah mosaic. The nest detection probability was 0.58 (± 0.05) and 0.52 (± 0.06), respectively, in the forest-savannah mosaic and the dense forest. The effective strip width was 14.62 (± 1.37) m in the forest-savannah mosaic and 10.46 (± 1.30) m in the dense forest. Table 1 shows nest density estimates while Table 2 shows chimpanzee density estimates.
The density varies considerably depending on the nest decay rate used. The nest decay rate is inversely proportional to the nest density. Considering the same nest decay rate, chimpanzee densities were similar across strata although with different confidence interval.
Surveyed effort was assessed as well as the proportion of nests in each habitat type (Table 3).
A total distance of 48 km (36.36%) was covered in colonising forest and 46 km (34.85%) in gallery forest. These are the two main vegetation types where chimpanzee nests were recorded. The proportion of nests varies with habitat types (F6, 284 = 9.54, P < 0.001). The number of nests found in colonizing forest was 101 nests (40.56%) and 94 nests (37.75%) in gallery forest (Fig. 4).
We identified a total of 31 plant species used as nesting material. Species commonly used to build nests were Berlina sp. (Caesalpiniaceae) (18.84%), Diospyros sp. (Ebenaceae) (15.36%) and Uapaca guineensis (Euphorbiaceae) (14.78%) (Additional file 3) (Fig. 5).
No evidence for difference was found on the number of plant species used for nesting between the dense forest and the forest-savannah mosaic (Kruskal–Wallis X2 = 1.1, df = 1, P = 0.293) or between habitat types (Kruskal–Wallis X2 = 6, df = 6, P = 0.423).
There was no evidence for difference in nest density and chimpanzee density between the dense forest and the forest-savannah mosaic (Kruskal–Wallis X2 = 1, df = 1, P = 0.31). Similarly, there was no difference in nest encounter rates (Kruskal–Wallis X2 = 0.13, df = 1, P = 0.71) between the dense forest and forest-savannah mosaic.
The nest type frequency differed between dense forest and forest-savannah mosaic (Pearson’s X2 = 9.19, P = 0.046) and between habitat types (Pearson’s X2 = 14.84, P = 0.05). However, 98.88% of all nests (N = 249) were tree nests with 52.20% (N = 130) and 46.58% (N = 116) found, respectively in forest-savannah mosaic and in dense forest. Among all the nests registered (n = 249), only three (1.20%) were ground nests although there was no evidence as to whether chimpanzees slept in them over night or used them to rest during day. These nests were found in the dense forest and built with Marantaceae leaves (Additional file 4) (Table 4).
There was a strong evidence of the influence of canopy cover (F3, 284 = 31.75, P < 0.001) and slope (F3, 284 = 10.22, P < 0.001) on the nesting site. In forest-savannah mosaic, 38.99% of the nests where found under high closure canopy (> 75%) while in dense forest, 37.03 of the nests were found under moderate closure canopy (51–75%). As for the slope, 53.45% of the nests recorded in forest-savannah mosaic and 60% in dense forest were found in low slope, although 31.44% of the nests were found in steep slope in forest-savannah mosaic. Low slope may offer comfortable nesting conditions to chimpanzee in MDNP.
There was a significant positive correlation between nest height and dbh of the nesting trees (Additional file 5) (r = 0.365, t292 = 6.717, p < 0.001) (Fig. 6). The mean dbh of nesting tree was 10.03 (± 8.42) cm, while the mean nest height was 11.59 (± 7.83) m.
The spatial interpolation of the encounter rates of chimpanzee nests is shown in Fig. 7. Chimpanzee nests were found between the Djerem and the Mekié Rivers. Nests were most frequently encountered in the dense forest and especially in the middle, south and north-west of the core zone, and few nests were found in the north.
Our findings suggest that gallery forest and colonizing forests are preferred habitats for chimpanzees in the MDNP. The forest-savannah mosaic with associated gallery forests provide suitable habitat for the Nigeria-Cameroon chimpanzee. The nest density estimates varied with strata and the chimpanzee density was similar to the density previously reported in the area, although with a relatively high coefficient of variation. The larger error associated with the chimpanzee density estimate might be explained by the use of a non-site specific nest decay rate as the later depends on the environmental variables of the study site  and the intrinsic limitations attributed to the survey method. On 25 of these transects (34% of the total) we found no chimpanzee nests. However, compared to the Ebo Forest in Cameroon where a nest decay rate of 88 days was used to obtain a chimpanzee density estimate of 0.67 animals/km2, our density estimate is lower than those from other Nigeria-Cameroon chimpanzee sites (Table 5).
Although chimpanzee density appears to be low in MDNP, the population may be more stable compared to other sites where hunting is considered to be a major threat . Our density estimate should be considered with caution because specific nest decay rates for MDNP are unavailable. We recommend the MNC method for future surveys because it does not require decay rate and direct observations, even though they are more costly and time-consuming.
We found no evidence that different types of plant species were used for nesting in the dense forest compared with the forest-savannah mosaic, even though considerably more plant species were found in the latter habitat type. Landolphia sp. and Diospyros sp. were also used by chimpanzees for nesting in Nigeria and Democratic Republic of Congo [23, 63]. The abundance of plant species found in nests in the forest-savannah mosaic might be explained by the high frequency of gallery forests and colonising forests. Both these contain food trees such as Uapaca guineensis and are relatively more diverse than dense forest. Thus, chimpanzees may not need to range so far as in dense forest for food, water and nesting materials.
Our results show that most nests occurred in trees, which is consistent with several other field studies of chimpanzee communities in other regions of Africa (i.e. Nigeria , Tanzania  and Kahuzi Biega National Park ). In our study, only 1.20% of nests were on the ground. This was the first time that ground nests have been recorded in the MDNP, and further monitoring is required to understand this behaviour: does it indicate the absence of predators or some aspect of social behaviour? In general, the construction of sleeping nests which are usually more elaborate than the day nests, and ground nesting is rarely observed in unhabituated chimpanzees . Ground nesting has been reported in Senegal in habitats with no or few predators  although predators were abundant at the ground nesting site of Bili . In south-east Cameroon, ground nests (3.47% of 1008 nests) were probably the consequence of a lack of nesting trees, or a reaction to hunting with guns or the abundance of terrestrial herbaceous vegetation . It could also indicate that the nest builders were sick . Previous reports of relatively high rates of ground nesting (6.1% of 994 nests) in the Nimba Mountains in Guinea  and (3.7% of 37 nests) at Yealé in Ivory Coast , have been hypothesized to result either from a male mating strategy, or a regional or seasonal fluctuation in the availability of ground nesting material . Disturbance by humans and seasonal effects may both affect whether chimpanzees construct their nests on the ground or in trees . While Pruetz et al. speculates arboreal nesting as anti-predator adaptation for chimpanzee, there is no evidence that in the absence of predators, chimpanzees switch to ground nesting [64, 69, 70]. Koops et al. suggested that the tendency to build ground nests may be genetically determined in the Nimba Mountains at Seringbara in Guinea. Males may also nest on the ground to guard an oestrous female in a tree above .
Over half of the nests were found in gallery forests, highlighting the importance of this habitat type for chimpanzee conservation. At the Ngel Nyaki Forest Reserve in Nigeria, chimpanzees most frequently built nests in gallery forests . Habitat attributes such as elevation also affect nest abundance. Nest encounter rates were higher with increasing elevation between 650 and 800 m a.s.l. in our study, still relatively lower than those of Budongo Forest in Uganda, where they were more likely to be found above 2000 m a.s.l. . Chimpanzee abundance was highly correlated with food availability in the Kibale National Park in Uganda  and in the Budongo Forest . In Kahuzi Biega National Park, in Ngel Nyaki Forest Reserve and in Kibale National Park chimpanzees preferred nesting in trees with ripe fruits . Canopy cover was also found to influence the choice of nesting site. Chimpanzees in MDNP appeared to prefer habitat with closed canopy for nesting. Previous studies in Senegal reported that chimpanzees also preferentially chose habitat with closed canopy for nesting [23, 66].
We also found that the nest height was related to the height and dbh of trees (R2 = 0.13), as has been described in previous studies . The average dbh of nesting trees at our site was c. 10.30 ± 8.42 cm compared to 54 cm in the Bili-Uele forest in Democratic Republic of Congo . While the average nest height (11.59 ± 7.83 m) was greater compared to 8 m found in Senegal  but lower than 20 m found in Nigeria . In the Nigerian study nest height were positively correlated to tree height.
In this study, we found that chimpanzee nests were concentrated in the middle of the core zone and relatively rare in the north and north-east. However, this may vary depending on season and food availability. Using only nests may fail to consider the seasonality of chimpanzees ranging, and should not imply that only areas where nests are observed are valuable for conservation [53, 73]. Further exploration of the effects of human pressure and the density of fruiting trees are required for a better understanding of chimpanzee distribution in the MDNP [17, 74]. Chimpanzees were most abundant in the middle and southern sections of the core zone which are the least accessible to park rangers, and consequently are relatively undisturbed.
The MDNP is the stronghold of Nigeria-Cameroon chimpanzee, noted for its exceptional conservation value  and the genetic distinctiveness of its population [10, 75]. Monitoring chimpanzee nesting and feeding sites will continue to be important for efficient conservation planning for this subspecies of great apes. More efforts are therefore needed to assess the chimpanzee nest decay rate to improve the reliability of density estimates. Regular monitoring and patrols should be focused in those areas to sustain this critical chimpanzee population and their habitat into future.
This study provides the first systematic assessment of the effect of habitat variability on the density of chimpanzees in the MDNP, revealing that gallery forest and colonising forest are preferred by chimpanzees in the core area, while highlighting characteristics of habitat that are positively associated with nest abundance and therefore high conservation importance. Our study indicates that as long as these habitat types are protected, current management practices to maintain savannahs are compatible with chimpanzee conservation. Well-designed surveys are required to assess the sustainability of chimpanzee populations [41, 76]. Currently chimpanzees in the MDNP are becoming increasingly tolerant of humans (Additional file 6). The MDNP offers an excellent opportunity for long-term research on the Nigeria-Cameroon chimpanzee, the least studied great ape subspecies  and aimed at understanding and dealing with its potential threats there and elsewhere. To safeguard this area from anthropogenic threats, we recommend that intensive patrols and biomonitoring activities should be focused on the pattern of chimpanzee nesting ecology to prevent threats that could led to almost complete depletion of chimpanzee and other wildlife as has occurred in the Gashaka Gumti National Park and Ngel Nyaki Forest Reserve in Nigeria [63, 77,78,79]. Further studies need to be focused on nest decay rates and phenology of useful plants (Berlina sp., Diospyros sp., Uapaca guineensis, Xylopia aethiopica and Landolphia sp.) in order to model chimpanzee abundance and distribution in MDNP. Base on the field observations, human population and chimpanzee both make use of Xylopia aethiopica and awareness activities need to be developed to protect this tree species. Our findings were transferred to the park authorities to update the biomonitoring database and measure the progress of chimpanzee conservation in MDNP.
Williamson EA, Maisel F, Groves CP. Family hominid (Great Apes). In: Intermediary RA, Irelands AB, Wilson DE, editors. Handbook of the mammals of the world. 3rd ed. Barcelona: Lynx Dictions; 2013. p. 792–843.
IUCN. IUCN red list of threatened species 2017-3. Cambridge: IUCN; 2017.
Junker J, Blake S, Boesch C, Campbell G, du Toit L, Duvall C, Ekobo A, Etoga G, Galat-Luong A, Gamys J, Ganas-Swaray J, Gatti S, Ghiurghi A, Granier N, Hart J, Head J, Herbinger I, Hicks TC, Huijbregts B, Imong IS, Kuempel N, Lahm S, Lindsell J, Maisels F, McLennan M, Martinez L, Morgan B, Morgan D, Mulindahabi F, Mundry R, N’Goran KP, Normand E, Ntongho A, Okon DT, Petre C-A, Plumptre A, Rainey H, Regnaut S, Sanz C, Stokes E, Tondossama A, Tranquilli S, Sunderland-Groves J, Walsh P, Warren Y, Williamson EA, Kuehl HS. Recent decline in suitable environmental conditions for African great apes. Divers Distrib. 2012;18:1077–91. https://doi.org/10.1111/ddi.12005.
Torres J, Brito J, Vasconcelos M, Catarino L, Gonçalves J, Honrado J. Ensemble models of habitat suitability relate chimpanzee (Pan troglodytes) conservation to forest and landscape dynamics in Western Africa. Biol Conserv. 2010;143(2):416–25. https://doi.org/10.1016/j.biocon.2009.11.007.
Pintea L, Bauer ME, Bolstad PV, Pusey A. Matching multiscale remote sensing data to inter-disciplinary conservation needs: the case of chimpanzees in Western Tanzania. In: Remote Sensing Symposium/Land Satellite Information IV Conference and the ISPRS Commission: 2003. Citeseer.
Ernst C, Verhegghen A, Mayaux P, Hansen M, Defourny P, Kondjo K, Makak J-S, Biang J-DM, Musampa C, Motogo RN. Cartographie du couvert forestier et des changements du couvert forestier en Afrique centrale. Les forêts du Bassin du Congo: état des forêts. Commission of Central African Forest; 2010. p. 23–42.
Mitchard ETA, Saatchi SS, Gerard FF, Lewis SL, Meir P. Measuring woody encroachment along a forest-savanna boundary in Central Africa. Earth Interact. 2009;13(8):1–29. https://doi.org/10.1175/2009EI278.1.
Knight A, Chapman HM, Hale M. Habitat fragmentation and its implications for Endangered chimpanzee Pan troglodytes conservation. Oryx. 2015. https://doi.org/10.1017/S0030605315000332.
Morgan BJ, Abwe EE. Chimpanzees use stone hammers in Cameroon. Curr Biol. 2006;16(16):R632–3. https://doi.org/10.1016/j.cub.2006.07.045.
Mitchell MW, Locatelli S, Ghobrial L, Pokempner AA, Clee PRS, Abwe EE, Nicholas A, Nkembi L, Anthony NM, Morgan BJ. The population genetics of wild chimpanzees in Cameroon and Nigeria suggests a positive role for selection in the evolution of chimpanzee subspecies. BMC Evol Biol. 2015;15(3):1. https://doi.org/10.1186/s12862-014-0276-y.
Sesink-Clee PR, Abwe EE, Ambahe R, Anthony NM, Fotso R, Locatelli S, Maisels F, Mitchell MW, Morgan BJ, Pokempner A. Chimpanzee population structure in Cameroon and Nigeria is associated with habitat variation that may be lost under climate change. BMC Evol Biol. 2015;15:2. https://doi.org/10.1186/s12862-014-0275-z.
Kouakou CY, Boesch C, Kuehl H. Estimating chimpanzee population size with nest counts: validating methods in Taï National Park. Am J Primatol. 2009;71(6):447–57. https://doi.org/10.1002/ajp.20673.
Baldwin PJ, McGrew WC, Tutin CE. Wide-ranging chimpanzees at Mt. Assirik, Senegal. Int J Primatol. 1982;3(4):367–85. https://doi.org/10.1007/BF02693739.
McGrew W, Baldwin P, Tutin C. Diet of wild chimpanzees (Pan troglodytes verus) at Mt. Assirik, Senegal: I. Composition. Am J Primatol. 1988;16(3):213–26. https://doi.org/10.1002/ajp.1350160304.
Tweheyo M, Lye KA, Weladji RB. Chimpanzee diet and habitat selection in the Budongo Forest Reserve, Uganda. Forest Ecol Manag. 2004;188(1):267–78. https://doi.org/10.1016/j.foreco.2003.07.028.
Hernandez-Aguilar RA, Moore J, Stanford CB. Chimpanzee nesting patterns in savanna habitat: environmental influences and preferences. Am J Primatol. 2013;75(10):979–94. https://doi.org/10.1002/ajp.22163.
Balcomb SR, Chapman CA, Wrangham RW. Relationship between chimpanzee (Pan troglodytes) density and large, fleshy-fruit tree density: conservation implications. Am J Primatol. 2000;51(3):197–203. https://doi.org/10.1002/1098-2345(200007)51:3%3c197:AID-AJP4%3e3.0.CO;2-C.
Carvalho JS, Meyer CF, Vicente L, Marques TA. Where to nest? Ecological determinants of chimpanzee nest abundance and distribution at the habitat and tree species scale. Am J Primatol. 2015;77(2):186–99. https://doi.org/10.1002/ajp.22321.
Morgan D, Mundry R, Sanz C, Ayina CE, Strindberg S, Lonsdorf E, Kühl HS. African apes coexisting with logging: comparing chimpanzee (Pan troglodytes troglodytes) and gorilla (Gorilla gorilla gorilla) resource needs and responses to forestry activities. Biol Conserv. 2017. https://doi.org/10.1016/j.biocon.2017.10.026.
Collins DA, McGrew WC. Habitats of three groups of chimpanzees (Pan troglodytes) in western Tanzania compared. J Hum Evol. 1988;17(6):553–74. https://doi.org/10.1016/0047-2484(88)90084-X.
Plumptre AJ, Cox D. Counting primates for conservation: primate surveys in Uganda. Primates. 2006;47(1):65–73. https://doi.org/10.1007/s10329-005-0146-8.
McGrew WC, Baldwin PJ, Tutin CE. Chimpanzees in a hot, dry and open habitat: Mt. Assirik, Senegal, West Africa. J Hum Evol. 1981;10(3):227–44. https://doi.org/10.1016/S0047-2484(81)80061-9.
Hicks TC, Tranquilli S, Swinkels J, Faustin L, Roessingh P. Morphology, distribution, nesting, and diet of the Bili apes. A Chimpanzee Mega Culture 2010.
Sommer V, Adanu J, Faucher I, Fowler A. Nigerian chimpanzees (Pan troglodytes vellerosus) at Gashaka: two years of habituation efforts. Folia Primatol. 2004;75(5):295–316. https://doi.org/10.1159/000080208.
Beck J, Chapman H. A population estimate of the Endangered chimpanzee Pan troglodytes vellerosus in a Nigerian montane forest: implications for conservation. Oryx. 2008;42(03):448–51. https://doi.org/10.1017/S0030605308001397.
Gonder MK, Oates JF, Disotell TR, Forstner MR, Morales JC, Melnick DJ. A new west African chimpanzee subspecies? Nature. 1997;388(6640):337. https://doi.org/10.1038/41005.
Oates JF, Groves CP, Jenkins PD. The type locality of Pan troglodytes vellerosus (Gray, 1862), and implications for the nomenclature of West African chimpanzees. Primates. 2009;50(1):78–80. https://doi.org/10.1007/s10329-008-0116-z.
Morgan BJ, Adeleke A, Bassey T, Bergl R, Dunn A, Fotso R, Gadsby E, Gonder MK, Greengrass E, Koulagna DK. Regional action plan for the conservation of the Nigeria-Cameroon chimpanzee (Pan troglodytes ellioti). San Diego: IUCN/SSC Primate Specialist Group and Zoological Society of San Diego; 2011.
Oates JF, Doumbe O, Dunn A, Gonder MK, Ikemeh R, Imong I, Morgan BJ, Ogunjemite B, Sommer V. Pan troglodytes ssp. ellioti. The IUCN red list of Threatened Species 2016: e.T40014A17990330. Downloaded on 20 October 2016. 2016.
Després-Einspenner M-L. Utilisation des caméras de piégeage et des modèles de capture-recapture pour l’estimation des densités de chimpanzés d’Afrique occidentale (Pan troglodytes verus) en Côte d’Ivoire. 2016.
Bonnin N, van Andel S, Kerby J, Piel AK, Pintea L, Wich SA. Assessment of chimpanzee nests detectability on drone-acquired images. Drones. 2018;2(2):17. https://doi.org/10.3390/drones2020017.
Arandjelovic MHJ, Rabanal LI, Schubert G, Mettke E, et al. Non-invasive genetic monitoring of wild Central chimpanzees. PLoS ONE. 2011;6(3):e14761. https://doi.org/10.1371/journal.pone.0014761.
Laing S, Buckland S, Burn R, Lambie D, Amphlett A. Dung and nest surveys: estimating decay rates. J Appl Ecol. 2003;40(6):1102–11. https://doi.org/10.1111/j.1365-2664.2003.00861.x.
Kühl H. Best practice guidelines for the surveys and monitoring of great ape populations. Gland: IUCN; 2008.
MINFOF. Plan d’aménagement du Parc National de Mbam et Djerem et sa zone périphérique 2007–2011. Yaounde: MINFOF; 2007.
White F. The vegetation of Africa, a descriptive memoir to accompany the UNESCO/AETFAT/UNSO vegetation map of Africa (3 Plates, Northwestern Africa, Northeastern Africa, and Southern Africa, 1: 5,000,000). Paris: UNESCO; 1983.
Buckland ST, Anderson DR, Burnham KP, Laake JL, Borchers D, Thomas L. Introduction to distance sampling estimating abundance of biological populations. Oxford: Oxford University Press; 2001.
Marques TA, Thomas L, Martin SW, Mellinger DK, Ward JA, Moretti DJ, Harris D, Tyack PL. Estimating animal population density using passive acoustics. Biol Rev. 2013;88(2):287–309. https://doi.org/10.1111/brv.12001.
Plumptre A, Reynolds V. Censusing chimpanzees in the Budongo forest, Uganda. Int J Primatol. 1996;17(1):85–99. https://doi.org/10.1007/BF02696160.
Guschanski K, Vigilant L, McNeilage A, Gray M, Kagoda E, Robbins MM. Counting elusive animals: comparing field and genetic census of the entire mountain gorilla population of Bwindi Impenetrable National Park, Uganda. Biol Conserv. 2009;142(2):290–300. https://doi.org/10.1016/j.biocon.2008.10.024.
Tutin CE, Fernandez M. Nationwide census of gorilla (Gorilla g. gorilla) and chimpanzee (Pan t. troglodytes) populations in Gabon. Am J Primatol. 1984;6(4):313–36. https://doi.org/10.1002/ajp.1350060403.
Morgan D, Sanz C, Onononga JR, Strindberg S. Ape abundance and habitat use in the Goualougo Triangle, Republic of Congo. Int J Primatol. 2006;27(1):147–79. https://doi.org/10.1007/s10764-005-9013-0.
Fleury-Brugiere M-C, Brugiere D. High population density of Pan troglodytes verus in the Haut Niger National Park, Republic of Guinea: implications for local and regional conservation. Int J Primatol. 2010;31(3):383–92.
Kühl H, Maisels F, Ancrenaz M, Williamson EA. Lignes Directrices pour de Meilleures Pratiques en Matière d’Inventaire et de suivi des Populations de Grands Singes. Gland: IUCN; 2009.
Dormann C, McPherson JM, Araújo MB, Bivand R, Bolliger J, Carl G, Davies RG, Hirzel A, Jetz W, Daniel Kissling W. Methods to account for spatial autocorrelation in the analysis of species distributional data: a review. Ecography. 2007;30(5):609–28. https://doi.org/10.1111/j.2007.0906-7590.05171.x.
Burgess ND, Balmford A, Cordeiro NJ, Fjeldsa J, Kueper W, Rahbek C, Sanderson EW, Scharlemann JPW, Sommer JH, Williams PH. Correlations among species distributions, human density and human infrastructure across the high biodiversity tropical mountains of Africa. Biol Conserv. 2007;134(2):164–77. https://doi.org/10.1016/j.biocon.2006.08.024.
Hedley SL, Buckland ST. Spatial models for line transect sampling. J Agric Biol Environ Stat. 2004;9(2):181–99. https://doi.org/10.1198/1085711043578.
Guisan A, Zimmermann NE. Predictive habitat distribution models in ecology. Ecol Model. 2000;135(2):147–86. https://doi.org/10.1016/S0304-3800(00)00354-9.
Tutin CE, Parnell RJ, White LJ, Fernandez M. Nest building by lowland gorillas in the Lopé Reserve, Gabon: environmental influences and implications for censusing. Int J Primatol. 1995;16(1):53–76. https://doi.org/10.1007/BF02700153.
White L, Edwards A. Conservation research in the African rain forests: a technical handbook. New York: Wildlife Conservation Society; 2000. p. 444.
Team. RDC. A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria. http://www-project.org/. 2016. Accessed 22 Sept 2016.
Hicks TC, Tranquilli S, Kuehl H, Campbell G, Swinkels J, Darby L, Boesch C, Hart J, Menken SB. Absence of evidence is not evidence of absence: discovery of a large, continuous population of Pan troglodytes schweinfurthii in the Central Uele region of northern DRC. Biol Conserv. 2014;171:107–13. https://doi.org/10.1016/j.biocon.2014.01.002.
Mathewson P, Spehar S, Meijaard E, Sasmirul A, Marshall AJ. Evaluating orangutan census techniques using nest decay rates: implications for population estimates. Ecol Appl. 2008;18(1):208–21. https://doi.org/10.1890/07-0385.1.
Plumptre AJ, Reynolds V. Nesting behavior of chimpanzees: implications for censuses. Int J Primatol. 1997;18(4):475–85. https://doi.org/10.1023/A:1026302920674.
Plumptre AJ. Monitoring mammal populations with line transect techniques in African forests. J Appl Ecol. 2000;37(2):356–68. https://doi.org/10.1046/j.1365-2664.2000.00499.x.
Stewart FA. The evolution of shelter: ecology and ethology of chimpanzee nest building. University of Cambridge; 2011. https://doi.org/10.17863/CAM.13968.
Wrogemann D. Wild chimpanzees in Lope, Gabon: Census method and habitat use. Univ. Zugl.: Bremen; 1992. http://hdl.handle.net/11858/00-001M-0000-0012-72D1-8.
Thomas L, Buckland ST, Rexstad EA, Laake JL, Strindberg S, Hedley SL, Bishop JR, Marques TA, Burnham KP. Distance software: design and analysis of distance sampling surveys for estimating population size. J Appl Ecol. 2010;47(1):5–14. https://doi.org/10.1111/j.1365-2664.2009.01737.x.
Grossmann F, Hart JA, Vosper A, Ilambu O. Range occupation and population estimates of bonobos in the Salonga National Park: application to large-scale surveys of bonobos in the Democratic Republic of Congo. In: The Bonobos. Springer; 2008. p. 189–216. https://doi.org/10.1007/978-0-387-74787-3_11.
McCoy J, Johnston K, institute Esr. Using ArcGIS spatial analyst: GIS by ESRI. Redlands: Environmental Systems Research Institute; 2001.
Ling F, Du Y, Li X, Li W, Xiao F, Zhang Y. Interpolation-based super-resolution land cover mapping. Remote Sens Lett. 2013;4(7):629–38. https://doi.org/10.1080/2150704X.2013.781284.
Dutton PE. Chimpanzee (Pan troglodytes ellioti) ecology in a Nigerian montane forest. University of Canterburyy. 2012; 221.
Dutton PE. Chimpanzee (Pan troglodytes ellioti) ecology in a Nigerian montane forest. 2012.
Basabose AK, Yamagiwa J. Factors affecting nesting site choice in chimpanzees at Tshibati, Kahuzi-Biega National Park: influence of sympatric gorillas. Int J Primatol. 2002;23(2):263–82. https://doi.org/10.1023/A:1013879427335.
Koops K, Humle T, Sterck EH, Matsuzawa T. Ground-nesting by the chimpanzees of the Nimba Mountains, Guinea: environmentally or socially determined? Am J Primatol. 2007;69(4):407–19. https://doi.org/10.1002/ajp.20358.
Pruetz JD, Fulton S, Marchant LF, McGrew WC, Schiel M, Waller M. Arboreal nesting as anti-predator adaptation by savanna chimpanzees (Pan troglodytes verus) in southeastern Senegal. Am J Primatol. 2008;70(4):393. https://doi.org/10.1002/ajp.20508.
Tagg N, Willie J, Petre C-A, Haggis O. Ground night nesting in chimpanzees: new insights from central chimpanzees (Pan troglodytes troglodytes) in South-East Cameroon. Folia Primatol. 2013;84(6):362–83. https://doi.org/10.1159/000353172.
Humle T. Culture and variation in wild chimpanzee behaviour: a study of three communities in West Africa. University of Stirling; 2003.
Blom A, Almaši A, Heitkönig I, Kpanou JB, Prins H. A survey of the apes in the Dzanga-Ndoki National Park, Central African Republic: a comparison between the census and survey methods of estimating the gorilla (Gorilla gorilla gorilla) and chimpanzee (Pan troglodytes) nest group density. Afr J Ecol. 2001;39(1):98–105. https://doi.org/10.1046/j.0141-6707.2000.00280.x.
Yamagiwa J. Factors influencing the formation of ground nests by eastern lowland gorillas in Kahuzi-Biega National Park: some evolutionary implications of nesting behavior. J Hum Evol. 2001;40(2):99–109. https://doi.org/10.1006/jhev.2000.0444.
Koops K, McGrew WC, Matsuzawa T, Knapp LA. Terrestrial nest-building by wild chimpanzees (Pan troglodytes): implications for the tree-to-ground sleep transition in early hominins. Am J Phys Anthropol. 2012;148(3):351–61. https://doi.org/10.1002/ajpa.22056.
Dutton P, Chapman H. Dietary preferences of a submontane population of the rare Nigerian-Cameroon chimpanzee (Pan troglodytes ellioti) in Ngel Nyaki Forest Reserve, Nigeria. Am J Primatol. 2015;77(1):86–97. https://doi.org/10.1002/ajp.22313.
Ban SD, Boesch C, N’Guessan A, N’Goran EK, Tako A, Janmaat KR. Taï chimpanzees change their travel direction for rare feeding trees providing fatty fruits. Anim Behav. 2016;118:135–47. https://doi.org/10.1016/j.anbehav.2016.05.014.
Hohmann G, Potts K, N’Guessan A, Fowler A, Mundry R, Ganzhorn JU, Ortmann S. Plant foods consumed by Pan: exploring the variation of nutritional ecology across Africa. Am J Phys Anthropol. 2010;141(3):476–85. https://doi.org/10.1002/ajpa.21168.
Mitchell MW, Locatelli S, Clee PRS, Thomassen HA, Gonder MK. Environmental variation and rivers govern the structure of chimpanzee genetic diversity in a biodiversity hotspot. BMC Evol Biol. 2015;15(1):1. https://doi.org/10.1186/s12862-014-0274-0.
Plumptre AJ. Eastern chimpanzee (Pan troglodytes schweinfurthii): status survey and conservation action plan, 2010–2020. Gland: IUCN; 2010. https://doi.org/10.1007/s10980-008-9231-x.
Duvall CS. Human settlement ecology and chimpanzee habitat selection in Mali. Landsc Ecol. 2008;23(6):699–716. https://doi.org/10.1007/s10980-008-9231-x.
Junker J, Blake S, Boesch C, Campbell G, Toit LD, Duvall C, Ekobo A, Etoga G, Galat-Luong A, Gamys J. Recent decline in suitable environmental conditions for African great apes. Divers Distrib. 2012;18(11):1077–91. https://doi.org/10.1111/ddi.12005.
Eniang E, Ijeomah H, Okeyoyin G, Uwatt A. Assessment of human–wildlife conflicts in Filinga range of Gashaka Gumti National Park, Nigeria. Prod Agric Technol J. 2011;1:15–35.
SAK, KSB, MKG and BS designed the research and SAK, RDDA and DEAO implemented the research. SAK, JM and PJ performed data analysis. SAK, KSB, PJ and JM wrote the paper. FM helped the design of the study, advised the data analysis. All authors read and approved the final manuscript.
This research was implemented with the generous support of the Rufford Foundation, the World Wide Fund for Nature (WWF) Russell E. Train Education for Nature and the Garoua Wildlife School via its US Fish and Wildlife Service capacity-building program to which we are grateful. We thank the Director of the Wildlife Conservation Society Project in Mbakaou Mr. Fosso Bernard and park manager Mr. Mounga Albert for their collaboration and logistical support during fieldwork. We also thank all of the survey teams and biomonitoring unit staff, for their help with data collection. We thank the Central African Biodiversity Alliance for the logistic support and to Dr. Zacharie Nzooh Dongmo of the WWF Cameroon for his technical advice on the research proposal and survey design. We are grateful to the Wildlife Conservation Research Unit of the University of Oxford, and to Dr. Christos Astaras, for providing the opportunity to participate in the Postgraduate International Diploma on Wildlife Conservation Practice and to analyse the data as part of my training. Finally, we acknowledge Professor Robert Weladji of the University of Concordia in Canada and the anonymous reviewers for their helpful comments on the revised manuscript of this paper.
There are no competing interests. Our connection with World Wide Fund for Nature and Rufford Foundation is simply a donor/grantee relation. This does not hinder our commitment to the editorial policies of BMC Ecology on publishing findings, data and materials.
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This research was funded by grants awarded to Serge Alexis Kamgang from World Wide Fund for Nature (ST68) and the Rufford Foundation (13184_1, 20258_2). The funders had no role in study design, data collection and analysis or the decision to publish the findings.
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Kamgang, S.A., Bobo, K.S., Maisels, F. et al. The relationship between the abundance of the Nigeria-Cameroon chimpanzee (Pan troglodytes ellioti) and its habitat: a conservation concern in Mbam-Djerem National Park, Cameroon. BMC Ecol 18, 40 (2018). https://doi.org/10.1186/s12898-018-0199-3
- Great apes
- Mbam-Djerem National Park
- Pan troglodytes ellioti
- Habitat variation
- Nest abundance
- Distance sampling