Page 202 - Soil Degradation, Conservation and Remediation
P. 202

6.2   Sources of Soil Pollutants                                191




                   Table 6.5   Some anthropogenic  sources of heavy metals in soil

                 Sources                             Metals

                 Landfill/chemical waste dump          As, Pb, Cr, Cd, Ba, Zn, Mn, Ni

                 Metal finishing/plating/electronics     Cr, Pb, Ni, Zn, Cu, Cd, Fe, As
                  Chemical/pharmaceutical             Pb, Cr, Cd, Hg, As, Cu
                  Mining/ore processing/smelting      Pb, As, Cr, Cd, Cu, Zn, Fe, Ag
                  Battery recycling                   Pb, Cd, Ni, Cu, Zn
                 Wood treating                       Cr, Cu, As
                 Nuclear processing/equipment        Ra, Th, U
                 Pesticides                          As
                 Vehicle                             As
                  Paint                               Pb, Cr, Cd, Hg

            degradation (Kirpichtchikova et al.  2006 ), and their total concentration in soils
            persists for a long time after their introduction (Adriano  2003 ). However, their
            chemical speciation and bioavailability may change in soil. Heavy metal contami-
            nation of soil may pose risks and hazards to humans and the ecosystem through
            direct ingestion or contact with contaminated soil and the food chain, drinking
            of contaminated water, and deterioration of food quality. Some soils are naturally
            metalliferous; their parent materials and rocks contain high concentrations of metals.
            Soils of mining areas are particularly high in heavy metals. A spectacular case was
            reported by Balke et al. ( 1973 ) from the area of Nievenheim in the lower reaches of
            the Rhine River, where a zinc processing plant has infiltrated wastewater onto the

                                                                            −1
            substratum. In the groundwater, the concentrations of arsenic surpassed 50 mg L   ;
                                                                     −1
            maximum concentrations have been measured for cadmium of 600 μg L   , thallium
                                  −1
                   −1
                                                  −1
            800 μg L   , mercury 50 μg L   , and zinc 40 mg L   . The most common anthropogenic
            sources of heavy metals in soil are summarized in Table  6.5 .
                   Natural Metalliferous Soils
                      The most important types of natural metalliferous soils are (1) serpentine soils,
              developed from Fe- and Mg-rich ultramafic rocks, which are signifi cantly

              enriched in Ni, Cr, and Co; (2) the calamine soils, enriched in Pb and Zn,
              which contain elevated Cd also and sometimes carry high concentrations of As
              and/or Cu; (3) Cu- and Co-containing soils such as those of the Shaban Copper
              Arc in the Democratic Republic of Congo, derived from argillites and dolomites
              containing sulfides of these metals, together with important secondary minerals

              (oxides, basic carbonates, silicates); and (4) soils derived from various Se-rich
              rocks. Serpentine soils occur over extensive areas in many countries of the
              world such as Japan, the Philippines, Indonesia, the USA, Turkey, Greece and
              the Balkan lands, parts of the European Alps, central Brazil, Cuba, Puerto Rico,
              and parts of Central America. Notable Se-rich soils have arisen particularly
              from the Cretaceous shales of the Midwestern USA (Mudgal et al.  2010 ).
   197   198   199   200   201   202   203   204   205   206   207