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TILLAGE AND CROPPING SYSTEMS EFFECTS ON CROP YIELDS ON A<br />

SOUTHERN GUINEA SAVANNA SOIL AT ILORIN, NIGERIA<br />

R. Lal<br />

Department of Agronomy, The Ohio State University<br />

Columbus, Ohio 43210 USA<br />

INTRODUCTION<br />

The savanna region in West Africa, with rainfall of 1000<br />

to 1200 mm per annum but concentrated in five to six months<br />

followed by a long dry season of six to seven months, is<br />

naturally suited for cultivation of grain crop annuals. The<br />

forest zone in the south, with rainfall of 1500 to 3000 mm<br />

received in a monomodal or bimodal pattern, is suited either<br />

for tree or root crop production. Rainfed agriculture in the<br />

semi-arid and Sahel regions of the north is prone to severe<br />

drought. The middle savanna belt has a potential to intensify<br />

agriculture and enhance food production. The research data,<br />

however, on appropriate methods of developing land, tillage<br />

and seedbed preparation, and appropriate cropping systems and<br />

crop combinations are not available for major soils and ecoregions.<br />

Despite the high potential to enhance production of food<br />

crop annuals, soils of the savanna regions are extremely<br />

vulnerable to degradation by several physical and chemical<br />

processes. Important physical processes of soil degradation<br />

are compaction, crusting, hard-setting, and accelerated runoff<br />

and erosion. These soils have low organic matter content,<br />

coarse texture, and clay fraction of low activity, e.g. low<br />

CEC. consequently, crusting and soil compaction are severe<br />

problems (Adeoye, 1982; 1985; Ike, 1988). Ley et al. (1989)<br />

reported that these soils are also structurally weak, and<br />

prone to hard setting. The hard setting behaviour is<br />

aggravated by rapid decline in soil organic matter content,<br />

raindrop impact on exposed soil, reduction in biotic activity<br />

of soil fauna during the cultivation phase, and ultradesiccation<br />

that occurs during the prolonged dry season.<br />

Because of weak structural attributes, these soils have<br />

relatively high erodibility (Van Elslande et al., 1987).<br />

Above all, high erosivity of rains is an important factor to<br />

be considered in land use planning. Localized rainfall<br />

intensities exceeding 100 mm h- 1 sustained for 10 to 15<br />

minutes are frequently observed (Kowal and kassam, 1976).<br />

Consequently soil erosion is a severe problem in the region<br />

especially at the onset of rains. The problem of soil erosion<br />

is further accentuated by the shallow depth of topsoil. A<br />

large proportion of soils developed on the mid-slope region<br />

along the catena are underlain by hardened plinthite at 15 to<br />

30 em depth.<br />

In view<br />

of several soil-related constraints to crop<br />

384

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