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soil, result in loss of soil aggregates stability (see Section 3.3.2) and soil structure, which in turn<br />

results in soil compaction, increased bulk density and decreased infiltration rate and water<br />

holding capacity of the soil. This leads to an increase in overland flow and further increase in<br />

erosion and degradation of topsoil. The practice of tillage also destroys the topsoil thin (3-5 cm)<br />

A 1 organic horizon, which is present under the virgin forest (see Section 4.3.1). This A 1 horizon<br />

is humic, very rich in fine roots, very friable, very porous, with granular subangular structure<br />

induced by a network of fine roots. It is within this A 1 horizon that farmers plant with zerotillage,<br />

cucumber (Cucumeropsis mannii) and maize (Zea mays) seeds when they clear an old<br />

forest.<br />

Erosion. The accelerated erosion is considered as man-induced erosion. The change of the soil<br />

chemical and physical properties under land cropping leads to an increased soil loss hazard due to<br />

detachment and transportation. In general, agricultural land in the study area are mostly located in<br />

dissected plains and rolling uplands landform units (van Gemerden and Hazeu, 1999) where the<br />

existing gentle slopes limit the effects of soil erosion processes. This partially explains the low<br />

sediment yields in the rivers reported by Waterloo et al. (2000). However, the soil type and the<br />

cropping systems / farming systems are the most important factors affecting erosion hazard<br />

variation in the area. From our field observation in the study area, sheet erosion occurs under the<br />

impact of the early rains at the beginning of the cropping period in annual crop fields. The<br />

consequence of this erosion is the rapid deterioration of the physical condition of the soil surface<br />

and leaching of nutrients from ashes. This process is lessened when the first crops cover the<br />

ground. When the first crop has been harvested, the soil surface is again exposed to some extent,<br />

but intercrops, weeds and the residues from the harvest provide some protection.<br />

Soil fauna. Soil micro-organisms together with soil macrofauna act as agents of nutrient cycling<br />

by regulating the retention and flux of nutrients in the soil system through processes of<br />

decomposition, mineralisation and immobilisation. Soil micro-organisms also enhance the<br />

amount and efficiency of nutrient acquisition by plants through the role of plant symbionts such<br />

as mycorrhiza and nitrogen fixing bacteria (see also Onguene, 2000). These functional<br />

relationships might be most evident in the natural ecosystems but also play a key role in<br />

determining the productivity and sustainability of agricultural systems. The activity of soil<br />

microbiota can be measured by what is called ‘microbial biomass’. This aspect should not be left<br />

out when one is to deem thoroughly the effect of shifting cultivation on soil degradation.<br />

Other factors<br />

Weeds, diseases, pests and insects. Weed growth is often of profound hindrance to crop<br />

production in tropical agriculture. Weed competition to crops is considered a factor that limits the<br />

effectiveness of soil available nutrients in increasing crop yields. However, weeds invasion has a<br />

positive effect as soil cover and protect soil against high erosive rainfall. Nematode and insect<br />

fauna and pathogenic microbes are also diverse in the tropics. High population of these parasite<br />

species often cause significant damage to crops. The parasite population, which might have built<br />

up during the cropping phase, is likely to be greatly reduced in numbers after several years of<br />

fallow.<br />

Phytomass reduction. In selecting a site for clearing, shifting cultivators, in general, judge the<br />

suitability of a prospective cropping site on the basis of existing vegetation rather than on soil<br />

characteristics (see Tables 2.11 and 2.15). In the study area, soils are classified in general lower<br />

chemical fertility levels (van Gemerden and Hazeu, 1999). A large part of nutrients is stored in<br />

the phytomass (vegetation biomass). The mature forest has adapted to the low nutrient level of<br />

soil by maintaining an almost closed nutrient cycle. Through recycling, these nutrient stocks<br />

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