Printer Friendly

Are mammal communities occurring at a regional scale reliably represented in "hub" bushmeat markets? A case study with Bayelsa State (Niger Delta, Nigeria).

Abstract. Monitoring of bushmeat markets has traditionally been seen as a source of faunistic and ecological data on mammal communities in West Africa. Nonetheless, it is largely unexplored whether datasets coming from monitoring of large "hub" markets in towns can reliably picture the mammal faunas and community compositions at the local level. Here, Swali market in Bayelsa State, Nigeria, that is one of the largest bushmeat markets in the Niger Delta, was monitored for six months in 2013-2014. Data from Swali market were compared with those collected during regular field surveys at five protected forests situated within 15 km radius from the market. A total of 21 mammal species was recorded at Swali versus 29 in the five protected forests. The trade was more intense by wet season. There was a statistically significant linear relationship between mean weight of the sold mammal and its price. A considerable portion of species that occur at the protected forests did not occur in the market samples, including the very rare species and the small-sized species. However, the abundance in the market of the common species was positively related to their apparent field abundance in the forest reserves. Therefore, it is concluded that large-sized bushmeat markets did not depict reliably the whole faunal composition and the community structure of mammals in West Africa, although these types of surveys are sufficient to characterize the abundance distribution of the common species at the regional scale.

Key words: mammalia, hunting, marketing of wildlife, West Africa


In many parts of Africa, a sizeable amount of wild animal meat (the so-called "bushmeat") go into the market annually, to support the livelihood of hunters and other indigenous people (e.g. Fa et al. 2000, 2002, 2003, Bakarr et al. 2002). The bushmeat trade has obviously both economic (Davies 2002, Brown & Williams 2003) and conservation (Fa et al. 2005, 2006, Luiselli et al. 2013) implications, and therefore has been a subject of vigorous investigations in the recent years (Fa et al. 2005, 2006, MacDonald et al. 2012, Martin et al. 2012, Obioha et al. 2012).

It has been observed that the increase in bushmeat hunting is a cause of biodiversity loss and decline of wildlife populations throughout Africa (Robinson et al. 1999, Wilkie & Carpenter 1999, Redmond et al. 2006, Mfunda & Roskaft 2010). Nonetheless, noteworthy advances in the knowledge of the distribution of Afrotropical animals, as well as even for description of previously unknown species (especially mammals), are due to inspection and monitoring of bushmeat markets by scientists (Powell & Grubb 2002, Colyn et al. 2010).

In west Africa, commercial hunters provide the harvested animals to the traders, who in turn supply urban markets for profit. Whilst there are myriads of small-scale, often temporary, bushmeat markets that trade a small number of individuals mainly at a local scale, there are also several large markets in towns and cities (hereby, the "hub" markets) that represent the main points of sale for a large volume of species extracted from natural areas (Fa et al. 1995, Fa 2000). It is considered that these "hub" markets may offer valuable insights into (i) the supply and demand of bushmeat in human population centres, (ii) the assessment of the effect of hunting on the bushmeat species if data on prey densities are available, and (iii) comprehensive data on the taxonomic composition of mammal communities (e.g. Fa et al. 1995, Angelici et al. 1999, Fa 2000). However, it has never been investigated in detail whether these markets can be really used to have a reliable and comprehensive dataset on local mammal faunas.

Throughout the Niger Delta of southern Nigeria, the bushmeat trade is certainly rampant, and has probably produced considerable negative effects on the local biodiversity (Martin 1983, Okiwelu et al. 2009, Luiselli et al. 2013). In this report, data collected by monitoring a "hub" market (situated in Bayelsa State, Niger Delta of southern Nigeria) were used to compare the diversity and richness of mammal species at the market place with diversity and richness patterns observed in five forest reserves of the same studied region that were subjected to focused researches (Petrozzi et al., unpublished data). By comparing these datasets, it would be possible to infer whether "hub" city markets may be instrumental in determining the relative mammal diversity patterns for the surrounding areas. The a priori expectation was that, if regional mammal diversity is adequately sampled by "hub" markets, then the accurate monitoring of that market should reveal the entire spectrum of species potentially present in the area. Obviously, since small rodents and insectivores are usually uneaten by humans, these species cannot be considered in this kind of comparisons and have been excluded from further analyses.

Material and Methods

Study area

The study was carried out in Swali market (4[degrees]55' N, 6[degrees]17' E). Swali market is the main centre for the sales of wildlife killed or captured alive, around Yenagoa and environs (Bayelsa State, Nigeria). Although the amount of traded carcasses in Swali is smaller than in other central markets studied to date (e.g. Kisangani in Congo, Vanvliet et al. 2012 or Malabo in Bioko Island, Fa et al. 2000), this marketplace appeared of special relevance for our study case because (i) it is situated between five forested reserves of the Niger Delta (Fig. 1), (ii) it is anyway larger than most bushmeat markets in the region, and (iii) because it is also used sometimes for sale of remotely captured animals. For instance, we recorded a few bushmeat items belonging to species that do not occur in the Niger Delta, such as the puff adder, Bitis arietans.

The study region is characterized by an alternation of flooded swamp forest patches and widely deforested areas, where cropping and forest-derived savannah-like grasslands are prevalent (Niger Delta Environmental Survey 1998). The market is located on the shore of the River Nun. Thus, hunters easily transport their bounties by rivercraft. Swali market is also accessible by good roads, recently constructed by the Bayelsa State government.

Most of the hunters catch the animals from the thick seasonally inundated swamp forests that are situated within 15 km radius from Swali market, i.e. Emeyal, Otuasega, Elebeli, Famgbe, Bebelebiri, Kolo Creek and Ogbia areas (Fig. 1). The importance of this marketplace is widely acknowledged at the local level because hunters prefer selling bushmeat to vendors in Yenagoa than to other locations of the state, because buyers price them better here (Akani et al., unpublished interviews with local hunters).

Taxonomic notes

We excluded most of the rodents, shrews and fruit bats (Eidolon helvum, Rousettus angolensis, Hypsignathus monstrosus, Epomophorus anurus, Epomophorus gambianus, and Epomops franqueti, see Happold 1987) from our investigations. Nomenclature for mammal species follows Nowak (1999) and Wilson & Reeder (2005). Identification of the recorded individuals was done to the most accurate taxonomic level possible. However, identification of some species remained ambiguous. In this case, either we report the genus name followed by "sp." or present the possible options. For instance, we indicated the genets as Genetta sp., with three species occurring in the study area, i.e. G. cristata, G. maculata, and G. thierryi (Powell & van Rompaey 1998). On the other hand, for the geospecies Galagoides demidovii (i.e. demidovii group according to Grubb et al. 2003), we indicated it as Galagoides demidovii/thomasi. For the geospecies Perodicticus potto (Grubb 2006), we indicated it as Perodicticus potto/edwardsi.

Sampling protocol

Swali market was surveyed both during the wet season (October 2013 and March 2014) and the dry season (November 2013 to February 2014). In our sampling protocol, a wet season day was not equivalent to a rainy day, as we intended as wet season days also dates with no rain falling. During the 24 weeks of study, the market was visited once every week to list and count the animals landed. Field effort was higher during the dry season (16 versus 8 visits in the wet season). Sampling was carried out only in the morning hours (7.00-11.00 a.m.), when hunters land their bounties and sell them to the bushmeat dealers. Animals killed in the previous night's hunting and animals trapped by snares must be brought to the market in the morning before they begin to putrefy and loose market value. Further information on the bushmeat trade (price of the animal on sale, place of capture, etc.) was acquired through interviews with the dealers and hunters. Overall, a total of 27 different hunters who were regular suppliers of bushmeat to the vendors were recorded, while five were occasional suppliers. The major hunting techniques were reportedly (i) shooting with local dane guns helped by hunt dogs, (ii) trapping with wire snares, and (iii) snap traps. At marketplace, mammals were sold as (i) living animals, (ii) whole carcasses, (iii) butchered parts, and (iv) dried or smoked parts. The condition of all the individuals at the time of examination was always recorded.

In order to explore whether the relative abundance of the various species at Swali market was influenced by their relative field abundance, we established an Abundance Index for all of the species occurring in the forest reserves surrounding Swali, by following Akani et al. (2014, 2015a). This Abundance Index was empirically determined on the basis of our interviews with selected hunters and on the relative number of our field sightings (for details, see Akani et al. 2014, 2015a). We categorized each species' abundance into three groups: very rare (score = 1), uncommon (= 2), and common (= 3). Although we acknowledge that this Abundance Index does not have full scientific support, nonetheless it may give a preliminary indication of the relative abundance of the various species for a region of tropical Africa where there is no data available on the population abundance of most mammal species (Akani et al. 2014, 2015a). Differences in the frequencies of animals (in terms of both number of individuals and traded biomass) sold in the wet versus dry season were examined by [chi square] test. Relationship between species' relative field abundance and frequency of occurrence at Swali market was analyzed by the Spearman's rank correlation coefficient. Relationship between mean weight of the sold mammal and its price was tested by the Pearson's correlation coefficient. Nonparametric tests were used when variables were not normally distributed. Alpha was set at 5 %. All statistical tests were performed with PAST software.


During the sampling period, a total of 21 mammal species were landed in Swali market for sales (Table 1). However, we were unable to identify genets to species level. Given the considerable species diversity of the genus Genetta in the Niger Delta (Powell & van Rompaey 1998), it is possible that more than one species was present in the samples, thus influencing the total number of species detected.

In total, 897 mammal individuals were examined, the great majority of them were already dead at the time of examination. Nonetheless, 12 Cercopithecus mona, 2 Cercopithecus sclateri, 8 Cercopithecus nictitans, and 5 pangolins were alive at the examination time. The landing rate was about 37 mammal carcasses per day of survey. Thryonomys swinderianus was the dominant species in the trade, accounting for 33 % of the total carcasses. Other common species were Cricetomys cf. emini, Atherurus africanus, Crossarchus platycephalus, antelopes, and monkeys (Table 1).

The collected data suggest a heavier trade during the wet months. Indeed, despite the stronger survey effort performed during the dry season, the numbers of traded carcasses were higher during the wet season at a marginally significant level ([chi square] = 30.9, df = 20, P = 0.0501). In addition, these inter-seasonal differences were highly significant in terms of traded biomass (higher by wet season; ([chi square] = 393.2, df = 20, P < 0.0001). The highest priced bushmeat were Tragelaphus spekei, T. scriptus, and Potamochoerus porcus (Table 2). There was a statistically significant linear relationship between mean weight of the sold mammal and its economic value (r = 0.970, [r.sup.2] = 0.940, n = 13, P < 0.001; Fig. 2).

Seven species recently (years 2010-2014) recorded in the forest reserves of Bayelsa State (data in Akani et al. 2014, 2015, Petrozzi et al., unpublished data) were not observed in the marketplace (Table 3). However, there was a significantly positive relationship between species' relative field abundance (Table 4) and its frequency of occurrence at Swali market (Spearman's r = 0.539, P < 0.01).


A total of twenty-nine species of mammals were recorded in five forest reserves situated in the same study region (i.e. Edumanon, Taylor Creek, Egbedi Creek, the River Nun and Upper Orashi Forest Reserves; see Petrozzi et al., unpublished data). The percentage of traded species in Swali market was high (72.4 % of the species that were certainly evidenced in the same forest region) and thus apparently well representative of the local mammalian diversity. In addition, the positive relationship between species' field abundance and its frequency of occurrence at the marketplace suggests that bushmeat market surveys may be useful to drawn quantitative information on the relative abundances of the various species of tropical forest mammal communities. Nonetheless, our data also revealed that inferences about mammal community structure from bushmeat market surveys may have serious limitations. Indeed, we showed that there are important subsets of the overall community of species that remained unrepresented in the market sample. For instance, all the very rare species (i.e. Cephalophus niger, Trichechus senegalensis, Arctocebus calabarensis, Pan troglodytes, Akani et al. 2014, Petrozzi et al., unpublished data) were never observed at the market site during the monitoring period. In addition, many species of smaller size (like squirrels) were also never observed at the market site despite they are common and widespread in the study region (Blench 2007, Akani et al. 2014, 2015a). Community ecology theory does make use of rare species and singletons in many diversity analyses (e.g. Magurran 1988, Gaston 1994, Novotny & Basset 2000, Luiselli 2006). Thus, the biased absence of such community components from bushmeat marketdata certainly introduces limitations in our understanding of tropical forest mammal community structures.

The reasons behind the absence of rare and small-sized species from marketplace are multiple. The absence of small-sized mammal species from bushmeat markets is due to the fact that they are directly consumed by the hunters and/or at the local level of the village as they are not economically viable, and are also hunted by different age groups (e.g. children) (Damania et al. 2005, Kamins et al. 2011). Indeed, rodents (as well as insectivore species and other small-sized animals), which are often consumed by the hunter and his family, hardly appear in the markets and therefore do not appear in the statistics (Colyn et al. 1987, Ntiamoa-Baidu 1997).

Concerning rare species, in theory it is possible that some species are not hunted because they are taboo (e.g. Oates et al. 2004, Baker et al. 2009) or because they are protected/forbidden to hunt in Nigeria and thus can be sold, but hidden (Oates 1999). However, several species, that officially are protected by Nigerian federal laws on Act 11, Schedule I (i.e. Atherurus africanus, Tragelaphus spekei, Hyemoschus aquaticus, Neotragus batesi, Aonyx capensis, Manis tricuspis, Uromanis tetradactyla) or Schedule II (i.e. Genetta sp., Nandinia binotata, Viverra civetta, and all Cercopithecus species), were regularly traded, thus showing that this type of legal impediment did not work to diminish the trade. Local taboos were also unlikely to affect the trade at Swali market, because this marketplace collated animals from a suite of different forest sites where hunting was performed by different ethnic groups.

The present study also revealed a higher trade by the wet season (more evident in terms of traded biomass than in terms of number of carcasses offered for sale). This result is in agreement with bushmeat market data for reptiles (Akani et al. 2015b). However, in reptiles it has been demonstrated a considerable intensification of above-ground activity (and hence of the encounter probability with hunters) during the rainy months (Akani et al. 2010, 2013), whereas the same inter-seasonal differences in phenology have, to our knowledge, never been reported for Niger Delta mammals. On the contrary, it has been reported that hunting was lower during rainy days, which occur generally in the wet season (e.g. Anadu et al. 1998, Wright & Priston 2010), because (i) of lower/more concentrated activities in mammals around water bodies (thus facilitating hunters, Bifarin et al. 2008) and (ii) agriculture cycle (Wright & Priston 2010). Therefore, our data suggest that the best hunting days were the dry days (and nights) within the wet season period.

In terms of economic value, the given data showed that the size of the traded animal determined for a great deal its price. Indeed, regardless of the type of traded animal, body weight predicted linearly ([r.sup.2] = 0.940) the economic value of its carcass. This result is in disagreement with Ntiamoa-Baidou (1997). In the bushmeat trade in Kantamanto market, Accra (Ghana), this author recorded a considerable interspecific variation in the average price/kg of the traded animals (see tables 3.7 and 3.8 in Ntiamoa-Baidou 1997). It is not known what may be the reasons behind these observed differences, but since we lack in our sample set the intermediary sized species (between 15 and 50 kg), our graphic (Fig. 2) is stretched between the two extremes, and this fact may have in part biased our conclusions.

Concerning the traded species, at Swali market there was an almost identical number of traded Tragelaphus scriptus and Tragelaphus spekei. Okiwelu et al. (2009) stated that the former species was recently replaced in the bushmeat market trade by the latter species, whereas it was dominant few decades before. Interestingly, clear dominance of Tragelaphus scriptus versus Tragelaphus spekei was also found by Angelici et al. (1999) in 1996-1997, thus independently confirming the "historical" observations by Okiwelu et al. (2009). It seems therefore demonstrated that these two species are really experiencing an inverse trend of occurrence in bushmeat markets. It is possible that this inversion of trends may depend on a progressive increased scarcity of Tragelaphus scriptus in the wild in the Niger Delta (at least in human-altered habitats), thus forcing hunters to enter deep inside the swamp forest places (typical habitat type for Tragelaphus spekei, see Antelope Specialist Group 2008) in order to hunt efficiently for antelopes. A deeper penetration of hunters inside mature forests was also seen in Gabon (Steel 1994).

Overall, the results of the present study suggest that central ("hub") bushmeat markets could not depict reliably the whole faunal composition and the community structure of mammals in West Africa, although the common species can be adequately sampled, even with quantitative estimates of their relative abundance mirroring true wild abundances. Thus, careful field surveys remain essential in order to establish the presence/absence, and obviously also the relative abundance, of a considerable portion of the mammal fauna of West African tropical forests.


We are grateful to Mr. George Amoru and Dorbra A., who were our field guides and contact men, and were also instrumental in our interviews with hunters and in arranging our logistics. Spartaco Gippoliti and Giovanni Amori helped with taxonomy of the traded species, Giuliano Milana with drafting the two figures, and two anonymous referees improved the submitted draft.


Akani G.C., Aifesehi P.E.E., Petrozzi F., Amadi N. & Luiselli L. 2014: Preliminary surveys of the terrestrial vertebrate fauna (mammals, reptiles, and amphibians) of the Edumanon Forest Reserve, Nigeria. Trop. Zool. 27: 63-72.

Akani G.C., Aifesehi P.E.E., Petrozzi F., Amadi N. & Luiselli L. 2015a: Diversity of terrestrial vertebrates in Taylor Creek Forest Reserve, an area of high environmental value in the River Niger delta (Bayelsa State, Nigeria). Vie Milieu 64: 59-68.

Akani G.C., Ebere N., Franco D., Eniang E.A., Petrozzi F., Politano E. & Luiselli L. 2013: Correlation between annual activity patterns of venomous snakes and rural people in the Niger Delta, southern Nigeria. J. Venom. Anim. Toxins 19: 1-8.

Akani G.C., Luiselli L., Ogbeibu A.E., Onwuteaka J.N., Chuku E., Osakwe J.A., Bombi P., Amuzie C.C., Uwagbae M. & Gijo H.A. 2010: Aspects of species richness and seasonality of amphibians and reptiles in the coastal barrier island of Brass (Nigeria). Rev. Ecol. 65: 151-161.

Akani G.C., Petrozzi F., Segniagbeto G.H. & Luiselli L. 2015b: Notes on morphology, biology and domestic consumption of Pelusios niger (Dumeril & Bibron, 1835) from Forcados River, Nigeria. Herpetozoa, in press.

Anadu P.A., Elamah P.O. & Oates J.F. 1998: The bushmeat trade in south-western Nigeria: a case study. Hum. Ecol. 16: 199-208.

Angelici F.M., Grimod I. & Politano E. 1999: Mammals of the eastern Niger Delta (Rivers and Bayelsa States, Nigeria): an environment affected by a gas-pipeline. Folia Zool. 48: 249-264.

Antelope Specialist Group 2008: Tragelaphus spekii. The IUCN Red List of Threatened Species, version 2014.3. Accessed 2 December 2014.

Bakarr M.I., Ampadu-Agyei O., Adomako E. & Ham R. 2002: Bushmeat utilisation, human livelihoods and conservation of large mammals in West Africa. In: Mainka S.A. & Trivedi M. (eds.), Links between biodiversity conservation, livelihoods and food security: the sustainable use of wild species for meat. IUCN, Gland: 45-53.

Baker L.R., Tanimola A.A., Olubode O.S. & Garshelis D.L. 2009: Distribution and abundance of sacred monkeys in Igboland, southern Nigeria. Am. J. Primatol. 71: 574-586.

Bifarin J.O., Ajibola M.E. & Fadiyimu A.A. 2008: Analysis of marketing bushmeat in Idanre Local Government Area of Ondo State, Nigeria. Afr. J. Agric. Res. 3: 667-671.

Blench R. 2007: Mammals of the Niger Delta, Nigeria. Privately printed, Cambridge.

Brown D. & Williams A. 2003: The case for bushmeat as a component of development policy: issues and challenges. Int. For. Rev. 5: 148-155.

Colyn M., Dudu A. & Mbaele M. 1987: Data on small and medium scaled game utilization in the rainforest of Zaire. In: Clers B.D. (ed.), Proceedings of the International Symposium and Conference on Wildlife Management in Sub-Saharan Africa. FAO, Harare: 109-141.

Colyn M., Hulselmans J., Sonet G., Oude P., De Winter J., Natta A., Nagy T.Z. & Verheyen E.K. 2010: Discovery of a new duiker species (Bovidae: Cephalophinae) from the Dahomey Gap, West Africa. Zootaxa 2637: 1-30.

Damania R., Milner-Gulland E.J. & Crookes D.J. 2005: A bioeconomic analysis of bushmeat hunting. Proc. R. Soc. Lond. B 272: 259-266.

Davies G. 2002: Bushmeat and international development. Conserv. Biol. 16: 587-589.

Fa J.E. 2000: Hunted animals in Bioko Island, West Africa: sustainability and future. In: Robinson J.G. & Bennett E. (eds.), Sustainability of hunting in tropical forests. Columbia University Press, Columbia, New York: 168-198.

Fa J.E., Currie D. & Meeuwig J. 2003: Bushmeat and food security in the Congo Basin: linkages between wildlife and people's future. Environ. Conserv. 30: 71-78.

Fa J.E., Garcia Yuste J.E. & Castelo R. 2000: Bushmeat markets on Bioko Island as a measure of hunting pressure. Conserv. Biol. 14: 1602-1613.

Fa J.E., Juste J., Perez del Val J. & Castroviejo J. 1995: Impact of market hunting on mammal species in Equatorial Guinea. Conserv. Biol. 9: 1107-1115.

Fa J.E., Peres C.A. & Meeuwig J.A. 2002: Bushmeat exploitation in tropical forests: an intercontinental comparison. Conserv. Biol. 16: 232-237.

Fa J.E., Ryan S.F. & Bell D.J. 2005: Hunting vulnerability, ecological characteristics and harvest rates of bushmeat species in Afrotropical forests. Biol. Conserv. 121: 167-176.

Fa J.E., Seymour S., Dupain J., Amin R., Albrechtsen L. & Mcdonald D. 2006: Getting to grips with the magnitude of exploitation: bushmeat in the Cross-Sanaga rivers region, Nigeria and Cameroun. Biol. Conserv. 129: 497-510.

Gaston K.J. 1994: Rarity. Chapman & Hall, London.

Grubb P.J. 2006: Geospecies and superspecies in the African primate fauna. Primate Conserv. 20: 65-73.

Grubb P.J., Butyinski T.M., Oates J.F., Bearder S.K., Disotell T.R., Groves C.P. & Struhsaker T.T. 2003: Assessment of the diversity of African primates. Int. J. Primatol. 24: 1301-1357.

Happold D.C.D. 1987: The mammals of Nigeria. Clarendon Press, Oxford.

Kamins A.O., Restif O., Ntiamoa-Baidu Y., Suu-Ire R., Hayman D.T.S., Cunningham A.A., Wood J.L.N. & Rowcliffe J.M. 2011: Uncovering fruit bat bushmeat commodity chain and true extent of fruit bat hunting in Ghana, West Africa. Biol. Conserv. 144: 3000-3008.

Luiselli L. 2006: Testing hypotheses on the ecological patterns of rarity using a novel model of study: snake communities worldwide. Web Ecol. 6: 44-58.

Luiselli L., Petrozzi F. & Akani G.C. 2013: Long-term comparison reveals trends in turtle trade in bushmeat markets of southern Nigeria. Herpetozoa 26: 57-64.

Macdonald D.W., Johnson P.J., Albrechtsen L., Seymour S., Dupain J., Hall A. & Fa J.E. 2012: Bushmeat trade in the Cross-Sanaga rivers region: evidence for the importance of protected areas. Biol. Conserv. 147: 107-114.

Magurran A.E. 1988: Ecological diversity and its measurement. Princeton University Press, Princeton, New Jersey.

Martin G.H.G. 1983: Bushmeat in Nigeria as a natural resource with environmental implications. Environ. Conserv. 10: 125-132.

Martin A., Caro T. & Mulder M.B. 2012: Bushmeat consumption in western Tanzania: a comparative analysis from the same ecosystem. Trop. Conserv. Sci. 5: 352-364.

Mfunda I.M. & Roskaft E. 2010: Bushmeat hunting in Serengeti, Tanzania: an important economic activity to local people. Int. J. Biodivers. Conserv. 2: 263-272.

Niger Delta Environmental Survey 1998: Environmental and socio-economic characteristics, Vol. 1. NDES, Port Harcourt, Nigeria.

Novotny V. & Basset Y. 2000: Rare species in communities of tropical insect herbivores: pondering the mystery of singletons. Oikos 89: 564-572.

Nowak R.M. 1999: Walker's mammals of the world, vol. 1, 6th ed. Johns Hopkins University Press, Baltimore.

Ntiamoa-Baidu Y. 1997: Wildlife and food security in Africa. FAO Conservation Guide--Technical papers no. 33, Rome.

Oates J.F. 1999: Myth and reality in the rain forest: how conservation strategies are failing in West Africa. University of California Press, Berkeley.

Oates J.F., Bergl R.A. & Linder J.M. 2004: Africa's Gulf of Guinea forests: biodiversity patterns and conservation priorities. Adv. Appl. Biodivers. Sci. 6: 1-91.

Obioha E.E., Isiugo P.N., Jimoh S.O., Ikyaagba E., Ngoufo R., Bobo K.S. & Waltert M. 2012: Bushmeat harvesting and human subsistence nexus in the Oban Hill Communities of Nigeria. J. Hum. Ecol. 38: 49-64.

Okiwelu S.N., Ewurum N. & Noutcha M.A.E. 2009: Wildlife harvesting and bushmeat trade in Rivers State, Nigeria: 1 - Species composition, seasonal abundance and cost. Sci. Afr. 8 (2): 1-8.

Powell C.B. & Grubb P. 2002: Range extension of black-fronted duiker (Cephalophus nigrifrons Gray 1871, Artiodactyla Bovidae): first records from Nigeria. Trop. Zool. 15: 89-95.

Powell C.B. & van Rompaey H. 1998: Genets of the Niger Delta, Nigeria. Small Carniv. Conserv. 19: 1-7.

Redmond I., Aldred T., Jedamzik K. & Westwood M. 2006: Recipes for survival: controlling the bushmeat trade ape alliance report. Accessed 12 November 2014.

Robinson J.G., Redford K.H. & Bennet E.L. 1999: Wildlife harvest in logged tropical forests. Science 285: 595-596.

Steel E.A. 1994: Study of the value and volume of bushmeat commerce in Gabon. In: Bowen-Jones E. (ed.), The African bushmeat trade - a recipe for extinction. Fauna & Flora International, Great Eastern House, Cambridge: 144-149.

Vanvliet N., Besse C., Gambalemoke S., Akaibe D. & Nasi R. 2012: The bushmeat market in Kisangani, Democratic Republic of Congo: implications for conservation and food security. Oryx 46: 196-203.

Wilkie D.S. & Carpenter J.F. 1999: Bushmeat hunting in the Congo Basin: an assessment of impacts and options for mitigation. Biodivers. Conserv. 8: 927-955.

Wilson D.E. & Reeder D.R. 2005: Mammal species of the world: a taxonomic and geographic reference, 3rd ed. John Hopkins University Press, Baltimore.

Wright J.H. & Priston N.E.C. 2010: Hunting and trapping in Lebialem Division, Cameroon: bushmeat harvesting practice and human reliance. Endanger. Species Res. 11: 1-12.

Godfrey C. AKANI (1), Nioking AMADI (1), Edem A. ENIANG (2), Luca LUISELLI (1,3*) and Fabio PETROZZI (1,4)

(1) Niger Delta Ecology and Biodiversity Conservation Unit, Department of Applied and Environmental Biology, Rivers State University of Science & Technology, P.M.B. 5080, Port Harcourt, Nigeria; e-mail:,

(2) Department of Forestry and Wildlife, University of Uyo, P.M.B. 1017, Uyo, Akwa-Ibom State, Nigeria; e-mail:

(3) Centre of Environmental Studies DEMETRA, via Olona 7, 00198 Rome, Italy; e-mail:

(4) Ecologia Applicata Italia, via Edoardo Jenner 70, 00151 Rome, Italy; e-mail:

Received 10 December 2014; Accepted 23 January 2015

(*) Corresponding Author

Table 1. Synopsis of the data on mammals traded in Swali market of
Bayelsa State, Nigeria.


Species                      Wet season    Dry season    Total

Cricetomys cfr. emini            45            29         74
Thryonomys swinderianus         184           112        296
Atherurus africanus              27            31         58
Philantomba walteri              18            11         29
Tragelaphus scriptus             14            15         29
Tragelaphus spekei               11            17         28
Hymenoschus aquaticus             4             7         11
Neotragus batesi                 10             3         13
Potamochoerus porcus              6             8         14
Viverra civetta                  16            11         27
Genetta sp.                      15            12         27
Nandinia binotata                19            10         29
Crossarchus platycephalus        28            32         60
Aonyx capensis                   10             4         14
Uromanis tetradactyla            18            12         30
Manis tricuspis                   8             5         13
Cercopithecus mona               26            22         48
Cercopithecus nictitans          13            18         31
Cercopithecus spp. (smoked       25            30         55
and unidentified)
Cercopithecus sclateri            4             2          6
Perodicticus potto/edwardsi       5             0          5


Species                   Mean weight (kg)  % biomass (total = 9345.73)

Cricetomys cfr. emini         1.2                     0.95
Thryonomys swinderianus       6.65                   21.06
Atherurus africanus           2.75                    1.71
Philantomba walteri           8                       2.48
Tragelaphus scriptus         52                      16.14
Tragelaphus spekei           85                      25.47
Hymenoschus aquaticus        11.5                     1.35
Neotragus batesi              3.75                    0.52
Potamochoerus porcus         80                      11.98
Viverra civetta              13.5                     3.90
Genetta sp.                   2.15                    0.62
Nandinia binotata             2.6                     0.81
Crossarchus platycephalus     3.15                    2.02
Aonyx capensis               23                       3.45
Uromanis tetradactyla         2.725                   0.87
Manis tricuspis               2.3                     0.32
Cercopithecus mona            4.5                     2.31
Cercopithecus nictitans       5.53                    1.83
Cercopithecus spp. (smoked    3.25                    1.91
and unidentified)
Cercopithecus sclateri        3.5                     0.22
Perodicticus potto/edwardsi   1.2                     0.06

Table 2. Price range of adult mammal carcasses in Swali market of
Bayelsa State (as at February 2014).

Species                    Sample size     Price range (Naira)

Tragelaphus spekei             20             75000-86000
Tragelaphus scriptus           16             72000-85000
Potamochoerus porcus           14             72000-80000
Philantomba walteri            10             10000-12000
Thryonomys swinderianus        55               4000-4500
Atherurus africanus            32               3000-4200
Pangolins                      15               3500-4400
Cricetomys cfr. emini          28                600-1000
Viverra civetta                10              8000-10000
Genets                         18               3500-4500
Crossarchus platycephalus      15               2800-3200
Cercopithecus spp.             18               4200-5800
Cercopithecus nictitans        22               4000-5800
Cercopithecus mona             10               4200-5500

Species                   Mean price (Naira)

Tragelaphus spekei             80000
Tragelaphus scriptus           78000
Potamochoerus porcus           75000
Philantomba walteri            10780
Thryonomys swinderianus         4260
Atherurus africanus             4100
Pangolins                       4000
Cricetomys cfr. emini            850
Viverra civetta                 8950
Genets                          4200
Crossarchus platycephalus       2970
Cercopithecus spp.              5200
Cercopithecus nictitans         5000
Cercopithecus mona              5000

Table 3. List of the mammal species that although recorded in recent
years (2010-2014) in five forest reserves (FRs) of Bayelsa State
(Petrozzi et al., unpublished data) were not observed at Swali bushmeat
markets. The apparent abundance of these species in the forest reserves
is also reported.

Species                       Status in the FRs

Arctocebus calabarensis       rare
Cephalophus niger             very rare
Herpestes ichneumon           rare
Funisciurus sp.               common
Galagoides demidovii/thomasi  rare
Pan troglodytes               very rare
Trichechus senegalensis       very rare

Table 4. Comparison between number of traded individuals per species at
Swali market and empirical Abundance Index of each species in the five
forest reserves surroundings the marketplace. For methodological
details, see the text.

Species                        No.     Abundance
                            in Swali    Index

Cricetomys emini               74        3
Thryonomys swinderianus       296        3
Xerus erythropus                0        3
Funisciurus sp.                 0        2
Atherurus africanus            58        3
Philantomba walteri            29        2.2
Cephalophus niger               0        1
Tragelaphus scriptus           29        2
Tragelaphus spekei             28        1
Hyemoschus aquaticus           11        1
Neotragus batesi               13        2
Potamochoerus porcus           14        3
Viverra civetta                27        2
Genetta sp.                    27        1
Nandinia binotata              29        1
Herpestes ichneumon             0        1
Crossarchus platycephalus      60        1.8
Aonyx capensis                  2        1
Uromanis tetradactyla          30        1
Manis tricuspis                13        1
Galagoides demidovii/thomasi    0        1
Perodicticus potto/edwardsi     5        1
Arctocebus calabarensis         0        1
Cercopithecus mona             48        2
Cercopithecus nictitans        12        1
Cercopithecus sclateri          6        1
Pan troglodytes                 0        0.6
Trichechus senegalensis         0        0.6
COPYRIGHT 2015 Institute of Vertebrate Biology ASCR
No portion of this article can be reproduced without the express written permission from the copyright holder.
Copyright 2015 Gale, Cengage Learning. All rights reserved.

Article Details
Printer friendly Cite/link Email Feedback
Author:Akani, Godfrey C.; Amadi, Nioking; Eniang, Edem A.; Luiselli, Luca; Petrozzi, Fabio
Publication:Folia Zoologica
Article Type:Case study
Geographic Code:6NIGR
Date:May 1, 2015
Previous Article:Does the European wildcat (Felis silvestris) show a change in weight and body size with global warming?
Next Article:Population genetic structure of the tropical eel Anguilla bicolor in Indonesian waters based on microsatellite markers.

Terms of use | Privacy policy | Copyright © 2022 Farlex, Inc. | Feedback | For webmasters |