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Agroforestry for Soil Conservation - World Agroforestry Centre

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22 <strong>Agro<strong>for</strong>estry</strong> <strong>for</strong> Control of <strong>Soil</strong> Erosion<br />

Trends in research and policy<br />

The traditional approach<br />

The earlier or traditional approach, as practised by soil-conservation or<br />

land-husbandry departments, is set out in standard texts and handbooks.<br />

Most textbooks were directed at US conditions, but that of Hudson (1981)<br />

is a clear summary, with a focus on the tropics, which has stood the test<br />

of time. Handbooks are texts directed at the design of soil-conservation<br />

measures in the field. Examples are FAO (1965), CTFT (<strong>Centre</strong> technique<br />

<strong>for</strong>estiere tropicale) (1979), Leblond and Guerlin (1983), Weber and Hoskins<br />

(1983a) and Hudson (1987), together with many national handbooks,<br />

<strong>for</strong> example those <strong>for</strong> Kenya (Wenner, 1981) and India (Singh et al. 1981b).<br />

The following is a summary of features of the traditional approach.<br />

Whilst it may be selective, to point out the contrast with recent trends<br />

discussed below, it is not intended as a parody! Features are:<br />

1. Most attention was given to erosion of croplands, much less to that of<br />

grazing lands.<br />

2. Attention was focused on rates of soil loss, as tonnes per hectare/tons<br />

per acre; as a consequence:<br />

a. research was directed mainly at measuring rates of soil loss;<br />

b. conservation measures were directed at reducing the rate of soil<br />

loss; in the USA, the aim was to design conservation measures which<br />

supposedly brought the rate below a specified level, called 'tolerable<br />

erosion', although not many countries followed this practice of setting<br />

a target figure.<br />

c. attempts to assess the consequences of erosion <strong>for</strong> productivity, and<br />

hence economic analysis, were directed at the effects of reduction<br />

in soil depth.<br />

3. The requirements of arable cropping with respect to soil cover were<br />

taken as fixed and unalterable; hence conservation works were directed<br />

at reducing runoff or breaking the <strong>for</strong>ce of downhill flow. This will be<br />

referred to as the barrier approach to conservation.<br />

4. Land-capability classification was widely employed as a basis <strong>for</strong> land-use<br />

planning. The approach originated in the USA (Klingebiel and<br />

Montgomery, 1961) and was adapted <strong>for</strong> many tropical countries, <strong>for</strong><br />

example in Africa, first by Zimbabwe (Conex, 1960) and subsequently<br />

Malawi (Shaxson et al., 1977) and Zambia (Zambia, Department of<br />

Agriculture, 1977). In this approach only land below a certain angle<br />

(depending on rainfall and soil type) is classified as suitable <strong>for</strong> arable<br />

use, primarily on grounds of erosion hazard. All steeper land should be<br />

used <strong>for</strong> grazing, <strong>for</strong>estry or recreation and conservation.<br />

5. Extension was conducted on the basis that soil conservation should come<br />

first, as a necessary prerequisite <strong>for</strong> other agricultural improvements.

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