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6.2   Sources of Soil Pollutants                                205



            6.2.12.4   Heavy Metals in Plant Food
              The levels of heavy metals in edible plant parts collected from crop fi elds and
            markets of vegetables, cereals, fruits, and spices have considerably been investigated.
            Metal contamination of plant materials have been reported from metal- contaminated
            places such as mining and industrial areas and in crop fields amended with sludge-

            based fertilizers or irrigated with contaminated water.
                Lead concentration in polished rice from paddy grown in a contaminated site
                                     − 1
            of China reached 0.69 mg kg   , which is higher than the maximum allowable
                                                                           − 1
            concentration by the safety criteria for milled rice for China (0.20 mg kg   ).
            Cadmium contents in 31 % of the rice samples exceeded the national maximum
            allowable concentration (Fu et al.  2008 ). Levels of Cd, Zn, Pb, and Cr in roots, stems,
            and leaves of the vegetable plants  Amaranthus viridis  and  Talinum triangulare
            planted on poultry dumpsite of Nigeria were 0.62–2.74, 50.67–102.98, 2.27–7.21, and
                          − 1
            0.64–4.45 mg kg   , respectively. Some of these values were above the safe levels

            (Adefila et al.  2010 ). Metal levels in vegetables, including parsley, onion, lettuce,
            garlic, peppermint, spinach, broad bean, chard, purslane, grapevine leaves, and
            fruits, including tomato, cherry, grape, and strawberry grown in Manisa region of Turkey,
            ranged from 0.56 to 329.7, 0.01 to 5.67, 0.26 to 30.68, 0.001 to 0.97, and 0 to 0.06 mg kg  −
            1    for Fe, Cu, Zn, Pb, and Cd, respectively (Bagdatlioglu et al.  2010 ). Contamination
            with heavy metals of fruits including orange, mango, almond, lemon, sweet orange,
            grapefruits, chiku, papaya, muskmelon, apple, quince, grape, strawberry, banana,
            pineapple, papaya, carambola, longan, wampee, date palm, and apricot have been
            reported (Davarynejad et al.  2010 ). Concentrations of Cu, Ni, Zn, Fe, Pb, and Hg
            of 15 common spices available at local markets in the Kumasi Metropolis of Ghana
                                                                            − 1
            ranged from 9 to 21, 31 to 50, 59 to 74, 110 to 494, 96 to 115, and 0.001 to 0.025 mg kg   ,
            respectively (Nkansan and Amoako  2010 ). Permissible limits of heavy metals in
            edible parts of plants are shown in Table  6.8 .



            6.2.12.5        Toxicity of Heavy Metals

              Organisms are exposed to soil contaminants by direct contact, handling, absorption,
            or ingestion and food intake. Heavy metals are bioaccumulated by incorporating
            into tissues, and as they are transferred through the food chain, they are biomagnifi ed
            at higher trophic levels.



                  Effect of Heavy Metals on Soil Microorganisms

              Some heavy metals are essential micronutrients (cobalt, chromium, nickel, iron,
            manganese, and zinc) for soil microorganisms (Bruins et al.  2000 ).  They  are
            involved in redox processes, in order to stabilize molecules through electrostatic
            interactions, as catalysts in enzymatic reactions, and regulating the osmotic balance
            (Hussein et al.   2005 ). On the other hand, some other heavy metals (cadmium,
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