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3. Status of Bonobo Populations
3.1 Current Knowledge
Information on the distribution and abundance of bonobos is fragmented, as much of their geo-
graphical range has not been surveyed. Speculative population estimates have varied from 29,500
(Myers Thompson 1997) to 50,000 (Dupain & van Elsacker 2001). Fruth et al. (2008) advised caution
on the use of these figures, because of the wide confidence intervals – the estimate for Salonga
alone was 7,100–20,400 (Grossmann et al. 2008). Through analysis of all available data from recent
surveys (2003–2010), the modelling group ascertained that less than one third of the bonobo’s
range has been surveyed. Figure 1 shows the bonobo’s range as modelled for suitable conditions
(Hickey et al. 2012). Figure 2 shows the areas surveyed for bonobos between 2003 and 2010. The
total area surveyed (139,537 km²) represents almost 25% of the historic range (564,542 km²), thus
it was not possible to produce a rangewide estimate of bonobo density or abundance.
Although quantitative data are patchy, the sites that have been surveyed give a minimum population
estimate of 15,000–20,000 individuals (see Table 1). All available bonobo nest survey data collected
between 2003 and 2010 were used to develop a model to predict the spatial distribution of potentially
suitable conditions for bonobos throughout the area between the Kasaï and Congo rivers (Hickey et
al. 2012). The modelling software used for this exercise was MaxEnt (Phillips et al. 2006).
The predictive environmental variables used in the final analysis were:
• percent forest land cover
• forest edge density (a measure of forest fragmentation)
• distance from rivers
• distance from agriculture
The main caveats of the resulting predictive model, which were systematically addressed
2
, are:
• bias may exist due to some sites and habitat types being
sampled more intensively
than others
• nest location errors could be present due to a possible inconsistency in GPS settings
used across sites
• environmental predictor variables were limited to those available across the full range
in raster format, because MaxEnt requires spatially complete data. Highly detailed
biotic and abiotic data relevant to bonobos are lacking at this scale.
Table 1. Minimum bonobo population estimates
Landscape
Bonobo population size
Salonga-Lukenie-Sankuru
>5,000
Tshuapa-Lomami-Lualaba
>5,000
Lac Télé-Lac Tumba Swamp Forest Landscape
<5,000
Maringa-Lopori-Wamba Forest Landscape
<5,000
Outside protected areas
>1,000
Minimum total estimate
15,000-20,000
2 Iterative modelling with data from a single site at a time, followed by modelling with all data minus one site at a
time, provided an assessment of the potential bias. Based on this sensitivity analysis, any bias in the final model is
expected to be low. The resolution of predictor variables in the final model was 100-m pixels, and several predictor
variables were developed using a neighbourhood analysis such that the conditions (e.g., edge density or percent
forest) in neighbouring pixels were incorporated into a given pixel’s value. These steps reduced the effect of any
potential GPS location errors. Data points that did not meet basic quality assessment/quality control rules were
excluded from the final analysis. The unavoidable limitation of spatially complete environmental predictor variables
likely has the most influence on the model outcomes.
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Figure 3 indicates the relative probability of occurrence of suitable conditions for bonobos. The
model identified areas likely to provide suitable conditions for bonobos that have not yet been
surveyed. The model also indicates that, on a rangewide scale, the principal factors determining
the distribution of bonobo nests are a) distance from agriculture and b) forest edge density, both
of which suggest that bonobos avoid areas of higher human activities (Hickey et al. 2012). The
poaching associated with these measures of human activities is considered to be the common
determinant of current bonobo distribution, as for most other large species in the Congo Basin.
3.2 Priority Populations
The modelling exercise identified four strongholds (Fig. 4) that harbour the majority of bonobos
known to remain. We refer to these as the ‘northern block’ (Maringa-Lopori-Wamba), ‘eastern
block’ (Tshuapa-Lomami-Lualaba, TL2), ‘southern block’ (Salonga) and ‘western block’ (Lac
Tumba-Lac Mai Ndombe). Each of these forest blocks contains at least one proposed or exist-
ing protected area and large expanses of forests where most conservation and research projects
currently operate. The concentration of research and conservation activities in these blocks may
have introduced a bias and overestimation of the importance of these areas compared with other
less-intensively surveyed sites. The model also predicts that some unsurveyed areas outside of
these four strongholds likely contain suitable conditions for bonobos, and these will be priorities
for future survey efforts.
Northern block (Maringa-Lopori-Wamba)
This block corresponds approximately to the Maringa-Lopori-Wamba landscape adopted by
the Congo Basin Forest Partnership (CBFP) and the Commission des Forêts d’Afrique Centrale
(COMIFAC). Situated in the Maringa and Lopori river basins in Equateur Province, this landscape
covers approximately 74,000 km². The area is very far from urban centres, experiences high levels
of poverty and people are extremely dependent on natural resources obtained through slash-and-
burn agriculture, fishing and hunting. The human population is estimated at 586,700 inhabitants
with densities of 2–4 people/km² where the existing or proposed protected areas are located, and
up to 32 people/km² in agro-pastoral zones and urban centres. Forest covers approximately 67%
of the block with swamps covering an additional 26%. The rest is young secondary forest and rural
complex (Dupain et al. 2009). The block contains four areas offering various levels of protection:
• Lomako Yokokala Forest Reserve (3,625 km²)
• Luo Scientific Reserve (225 km²)
• Kokolopori Bonobo Reserve (4,000 km²), a community-based natural resource man-
agement (CBNRM) area
• Iyondji Community Bonobo Reserve (1,100 km²), an area of intact forest adjacent to
the Luo Scientific Reserve.
Since 2006, a major participative land-use planning exercise has been carried out, covering
approximately 70% of the landscape. This work has designated a mosaic of protected areas,
CBNRM areas, sylvo-agro-pastoral zones and logging concessions
3
. The objective is to maintain
forest cover and connectivity between ecologically important habitats in order to reconcile conser-
vation needs and human activities.
Bonobos are found in varying densities throughout this landscape. Although current data do not
allow estimation of the total number of bonobos in this stronghold, surveys suggest that this block
contains some of the most important populations in the bonobo’s range.
3 As of August 2012, one concession was operational (TRANS-M) and two more are planned (K7 and K2 have
been attributed to SIFORCO).