Abstract
Understanding the capacity for humans to share resources (crops, wild foods, space) with large-bodied wildlife is vital for biodiversity conservation and human wellbeing, and requires comprehensive examination of their temporal interactions over fine spatial scales. We combined ecological (plant identification, wild fruit availability plots, animal faecal and trace sampling) and social science (free-listing, semi-structured interviews, participant observation) methods to systematically and simultaneously collect data on the availability and selection of fruits from wild plants by humans and critically-endangered chimpanzees (Pan troglodytes verus), a national conservation flagship species at Cantanhez National Park, Guinea-Bissau. Within an area of 12.7 km2, we demonstrate that local people’s monthly use of wild fruits was driven by its overall availability in the habitat, whereas chimpanzees, as ripe fruit specialists, sought out fruits year-round. Humans and chimpanzees overlap in the selection of fruits from at least 27 wild plant species. The ranked use of fruits from species which were used by both chimpanzees and humans was significantly positively correlated, suggesting they preferentially target fruits of the same wild plant species. Each month, humans and chimpanzees selected three to six of the same wild fruit species. Chimpanzees fed significantly more on wild fruit species that were available for longer periods, with no effect of that plant species density. Neither plant density nor number of fruiting months impacted human selection of fruit from a plant species, suggesting people might seek out desired resources irrespective of a species’ abundance in the landscape. These findings are important for the development of a shared knowledge base to establish culturally relevant conservation management strategies. We recommend the active management of plant species that are exploited for their fruits by both humans and chimpanzees at Cantanhez National Park, including figs (Ficus spp), oil-palm (Elaeis guineensis) and velvet tamarind (Dialium guineense). This can be achieved through supporting traditional resource management practices and the strategic replanting of shared plants in deforested areas and degraded corridors between forest fragments. This situation is representative of human-chimpanzee coexistence scenarios found across West Africa; the importance of shared resource use should be incorporated into local, national and regional conservation strategies.
Highlights
Expanding human populations have meant that wildlife increasingly inhabit landscapes in proximity to people (Woodroffe et al, 2005; Karanth et al, 2010; Hockings et al, 2015; Angelici, 2016)
If access to plant resources is restricted, for example through government regulations preventing the harvest of rare plant species, this can create hostility between local user groups, and between local people and authorities, which might compromise wildlife conservation objectives (Sheil et al, 2012; Redpath et al, 2013)
Chimpanzees consumed a minimum of 57 wild plant species, from at least 25 families, including six plant parts
Summary
Expanding human populations have meant that wildlife increasingly inhabit landscapes in proximity to people (Woodroffe et al, 2005; Karanth et al, 2010; Hockings et al, 2015; Angelici, 2016). Humans change wildlife habitats and ecological systems in numerous ways through highly conspicuous land-use changes, such as large-scale clearing of forests for cultivation, and through smaller-scale resource exploitation, such as harvesting of wild plants (i.e., non-cultivated) for subsistence and medicinal purposes (Winterhalder, 2001). The use of wild plants by local people is part of traditional subsistence systems and often linked with financial security (Belcher et al, 2005), for highly valuable fruiting species. If certain wild plant resources are exploited heavily or destructively by people and wildlife, and these resources show low temporal or spatial availability, this might lead to their decline over time. Understanding which plant resources are selected and why, by humans and wildlife within and outside protected areas, is for the most-part lacking, yet is important for integrating the needs of local people with conservation objectives
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