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World’s Soil Resources

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Prepared by K. Van Oost<br />

Figure 6.1 Spatial variation of soil erosion by water. High rates (>ca. 20 t ha -1 y -1 ) mainly occur on cropland in tropical areas.<br />

The map gives an indication of current erosion rates and does not assess the degradation status of the soils.<br />

The map is derived from Van Oost et al., 2007 using a quantile classification.<br />

The redistribution of soil within fields due to tillage erosion rates may lead to (very) high erosion rates<br />

on convexities (knolls) exceeding 30 tonnes ha -1 yr -1 ; and to deposition rates in hollows and at down slope<br />

field borders exceeding 100 tonnes ha -1 yr -1 . These rates are not directly comparable to wind or water erosion<br />

rates, as soil eroded by tillage will not leave the field. However, tillage erosion may significantly reduce crop<br />

productivity on convexities and near upslope field or terrace borders.<br />

Evidence of past erosion is extensive. This is demonstrated by wind-blown sands of sandstone bedrock,<br />

extensive loess accumulations of silt-sized aeolian sediments, and other formerly aeolian-affected landscapes.<br />

Large areas of sand seas, dune fields and other aeolian features and observations of activity provide further<br />

evidence of past wind erosion (Figure 6.2).<br />

USDA estimates place wind erosion rates at ca. 2.5 tonnes ha -1 yr -1 on average over all cropland of the United<br />

States while the average erosion rate for pastureland is ca. 0.1 tonnes ha -1 yr -1 . There are very few quantitative<br />

assessments of wind erosion rates on arable land outside of the United States.<br />

Status of the <strong>World’s</strong> <strong>Soil</strong> <strong>Resources</strong> | Main Report Global soil status, processes and trends<br />

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