Termite diversity across an anthropogenic disturbance gradient in the humid forest zone of West Africa
Introduction
The humid forest zone of Africa stretches from Guinea in the west to Uganda in the east. It is formed of two large contiguous areas of continuous forest (the Guinea and Congo forest blocks), at various stages of anthropogenic degradation. The original forest systems were drier and poorer in tree species than Southeast Asian and South American wet tropical forests, and are on characteristically poor acidic soils.
The present forest is a mosaic of different land uses: patches of secondary forest and fallow, crop fields, some tree plantations and agroforestry and significant remnants of primary vegetation. The dominant soils are acidic (oxisols and ultisols derived from low activity clays), commonly exhibiting Al toxicity, low cation-exchange capacity, low base saturation and low P availability. The traditional food-production systems are those of shifting cultivation (slash and burn), with plantain, cocoyam, maize, cassava and groundnut as the principal staples, the last two of those having relatively low soil fertility requirements. Management schemes and agricultural rotations are variable, but cleared forest, first year or exhausted crop fields can all be short-fallowed for 2–4 years after productive use by the woody perennial weed Chromolaena odorata before recropping. Oil palm and cocoa may be introduced at a later stage, or planted directly after forest clearance. There is usually a progressive decline in the fertility and yield of foodcrop fields to about 5–6 years post-clearance, after which a long fallow of 10 or more years is desirable, returning land to secondary forest. Long fallows of as little as 4 years are increasingly common, however, reflecting socioeconomic changes, including population growth and declines in urban employment opportunities.
The fauna is increasingly recognised as a major influence on tropical soil fertility. In African forest biomes these are pre-eminently termites (Eggleton, 2000, Bignell and Eggleton, 2000. In particular, soil-inhabiting (especially soil-feeding) termites are thought to be important for the distribution, protection and stabilisation of organic matter, the genesis of soil micro-aggregates and porosity, humification, the release of immobilised N and P, the improvement of drainage and aeration, and an increase in exchangeable cations (Lavelle et al., 1997). Therefore, changes in the species richness, composition and functional characteristics of termite assemblages are likely to have major influences on soil properties. Termite diversity is known to decline where forest canopy cover is reduced or lost completely, soil-feeding termites being affected most severely (Eggleton et al., 1996, Dibog et al., 1999). This loss of diversity is examined here across a wider range of habitat/treatment types than have been previously examined for the humid forest zone, with an emphasis on functional characteristics.
The work described here forms part of the ‘Alternatives to Slash and Burn’ (ASB) Programme. The ASB is a global, system-wide programme designed to identify optimal schemes for tropical forest-based subsistence agriculture which are consistent with alleviating poverty, providing increased food security, enhancing environmental resilience and conserving biodiversity (Kenyatta, 1997). The general ASB objective is to answer the question: what is the effect of land use change on biodiversity and, what are the implications for ecosystem services and resilience, and for agricultural productivity?
Section snippets
Sites and treatments
In the humid forest zone of southern Cameroon, there is a general N/S ecogradient that also reflects land use intensification, with the greatest pressure on land and the shortest fallow at the northern end. This reflects both higher population density in the north and the greater opportunities for income from cash crops and hunting in the south of the country. Many villages maintain plantations of cocoa and other cash crops (e.g. pineapple or other fruit), but there is a tendency for these
Diversity
A total of 133 species were sampled. Of these some 40% were new to science, although most have been recognised as separate morphospecies in earlier studies (Eggleton et al., 1995, Eggleton et al., 1996, 2000; Dibog, 1998, Dibog et al., 1998, Dibog et al., 1999, Davies et al., 1999). Overall species richness showed a strong correlation between disturbance and species richness from the completely cleared to the cocoa plots (Fig. 1). However, within the forested plots there was little variation in
Conclusions
The changes in termite diversity observed across the Cameroon sequence consist largely of losses of soil-feeding species, wood-feeding and foraging species being less affected. Taken together with abundance and biomass data (Eggleton et al., 1996), this suggests that termite-mediated wood and litter decomposition would be unchanged under light and moderate disturbance intensity, whereas their soil-conditioning might be compromised. This may have negative effects on agricultural productivity as
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2021, Global Ecology and ConservationCitation Excerpt :In addition, Muvengwi et al. (2017) also found different termite feeding group structure between land uses primarily related to differences in soil and vegetation resources between sites. Differences in termite communities between land use types have also been reported in other studies (Dosso et al., 2012; Eggleton et al., 2002; Luke et al., 2014). However, the effect of land use on termite communities have been evaluated alone, despite possible interaction with other disturbances such as fire.