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180                                         A. Branzini and M.S. Zubillaga

            in soils, as it negatively influences the activity of microorganisms and earthworms,
            thus retarding the breakdown of organic matter (Greany 2005). The Zn sources are
            soil, zinc oxide, zinc sulfate, and zinc chelate, and Zn 2+  cation is the predominate
            form taken up by plants.




            10.1.3 Cadmium

            Cadmium compounds are, compared to other heavy metals, relatively water solu-
            ble. Therefore, these compounds are further mobile and available in soil and tend to
            bioaccumulate. The average natural abundance of Cd in the earth’s crust has most
            often been reported from 0.1 to 0.5 ppm. In contaminated soils, Cd is derived from
            both natural and anthropogenic sources. Natural sources include underlying solid
            rock or transported parent material such as glacial till and alluvium. Anthropogenic
            input to soils occurs by aerial deposition and sewage sludge, manure, and phosphate
            fertilizer application. The major factors governing Cd speciation, adsorption, and
            distribution in soils are pH, soluble organic matter content, hydrous metal oxide
            content, clay content and type, presence of organic and inorganic ligands, and
            competition from other metal ions (Kim and Kim 2010). Its persistence in the
            environment and its relatively rapid uptake and accumulation by food chain crops
            are factors contributing to its potential environmental hazards. Cadmium
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            concentrations of air ambient rarely exceed 0.01 g m . However, cigarette smok-
            ing adds considerably to Cd input via inhalation. On the other hand, even though
            acute Cd toxicity caused by food consumption is rare, chronic exposure to high Cd
            levels in food can significantly increase the accumulation of Cd in certain body
            organs. Cd accumulates in the human body and especially in the kidneys. When Cd
            concentration in human body reaches levels considered to be harmful
            [>200 mg kg  1  wet weight in the kidney cortex according to Kjellstrom and
            Nordberg (1978)], this metal could induce kidney damage and led to its dysfunction
            with impaired reabsorption of, for instance, proteins, glucose, and amino acids.



            10.1.4 Nickel


            Nickel combined with other elements occurs naturally in the earth’s crust. It is
            found in all soils, and is emitted from volcanoes. However, it normally occurs at
            very low levels in the environment, and it is primarily found combined with oxygen
            or sulfur as oxides or sulfides. Soil usually contains between 4 and 80 parts of nickel
            in a million parts of soil (ppm). The highest soil concentrations (up to 9,000 ppm)
            are found near industries that extract nickel from ore. Ni can also be released in
            industrial wastewater. As a result, a lot of Ni released into the environment ends up
            in soil or sediment where it strongly attaches to particles containing iron or
            manganese. Under acidic conditions, Ni is more mobile in soil and might seep
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