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24                                    1  Soil Resources and Soil Degradation

              time by runoff from higher areas. Some Torrerts are found in the southwest of the
              USA. These soils are commonly used for rangeland.


                Uderts:   Uderts are the Vertisols of humid areas. They have a udic soil moisture
              regime. The cracks may not open completely some years due to high precipita-
              tion. In the USA, the soils occur on gentle slopes and are derived dominantly
              from marine shales, marls, and alluvium. Many of these soils supported grass,
              but some support hardwood or pine forests.


                Usterts:  These are the Vertisols in temperate areas that do not receive high amounts

              of rainfall during the summer. They have an ustic soil moisture regime. Cracks
              open and close once or twice during the year. They are found extensively in the
              USA, Australia, Africa, and India. If irrigated, Usterts can be used intensively,
              but large areas are used for grazing due to a lack of machinery to till soils.


                Xererts:   Xererts are the Vertisols of Mediterranean climates, which have xeric soil
              moisture regime. These soils have cracks that regularly close and open each year.
              In the USA, most of the soils supported grasses.


            1.7         Soil Degradation


              Land degradation is said to have taken place when the land within an ecosystem is
            no longer able to perform its environmental regulatory functions of accepting, stor-
            ing, and recycling water, energy, and nutrients and when the potential productivity
            associated with a land-use system becomes non-sustainable (Oldeman et al.  1991 ).
            Again, soil degradation is considered as the measurable loss or reduction of the
              current or potential capability of soils to produce plant materials of desired quantity
            and quality. According to some authors (Blaikie and Brookfi eld  1987 ; Chisholm
            and Dumsday  1987 ; Blum and Eswaran  2004 ), land degradation is a broader term
            than soil degradation. But for synonymous use of the terms land and soil in most soil
            management literature, land degradation and soil degradation will be used inter-
            changeably in the following sections.
                Several physical, chemical, and biological processes are responsible for the
              degradation of soil (Lal  1994 ; Eswaran et al.  2001 ). The physical processes include
            deterioration of soil structure, crusting, hardsetting, compaction, erosion, and

            desertification. The chemical processes include leaching, fertility depletion, acidifi -
            cation, salinization, and pollution.  The biological processes of soil degradation
            include reduction in carbon and decline in soil biodiversity. According to Beinroth
               .
            et al   ( 1994 ), land degradation results from a mismatch between land quality and
            land use.
                Yield reductions of 30–90 % by erosion in some root-restrictive shallow soils of
            West Africa were reported by Mbagwu et al   ( 1984 ) and Lal ( 1987 ). Erosion reduced
                                              .
            20–40 % yield of row crops in Ohio (Fahnestock et al    1995 ) and elsewhere in
                                                         .
            Midwest USA (Schumacher et al.  1994 ). In the  Andean region of Colombia,
            Ruppenthal (  1995 ) have observed severe losses due to accelerated erosion on some
            lands. The productivity of some lands in Africa has declined by 50 % (Dregne  1990 )
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