Page 141 - Soil and water contamination, 2nd edition
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128                                                  Soil and Water Contamination

                    a          Lower critical  Upper critical   b            No effect
                               concentration  concentration                 concentration   6642  6642  6642





                     Biomass production









                           Deficiency  Optimum  Luxury  Toxicity       No effect  Toxicity
                      0            Metal concentration           0     Metal concentration
                    Figure 7.1  Typical dose–response curves for a) essential trace metals,  and b) non-essential trace metals . Adapted
                    from Alloway and Ayres (1997).
                    deposits, which are often associated with past or present volcanic activity. This may give rise
                    to anomalously large natural concentrations in soil, groundwater, stream water and stream
                    sediments. Nevertheless, such natural enrichment of metals may still be harmful to living
                    organisms.
                       Enhanced environmental concentrations of heavy metals  are often associated with mining
                    and smelting. These activities cause air pollution and associated atmospheric deposition  of
                    contaminated dust. Most mine tailing ponds and heaps are potentially hazardous, because
                    pyrite  contained in the ores oxidises to form sulphuric acid . As a consequence, drainage
                    waters from mine tailings are often very acid  (pH  less than 3) and carry large amounts of
                    mobilised heavy metals  and aluminium . Moreover, until the 1980s, slag containing high
                    levels of leachable heavy metals was widely used for road metalling, and in this way the
                    metals were dispersed over large areas. Other important potential anthropogenic sources of
                    heavy metals include sewage sludge  (when spread on the land), phosphate  fertilisers , manure ,
                    and atmospheric fallout  (from smelting, or from burning coal and gasoline), leaching



                    Table 7.1  Typical ranges of heavy metal concentrations in major igneous and sedimentary rock types, and fresh
                    water (source: Alloway and Ayres, 1997; Smedley and Kinniburgh, 2001).
                           Igneous rocks               Sedimentary rocks
                           Ultramafic  Mafic  Granitic  Limestone  Sandstone  Shales/Clays  Fresh water
                           mg kg -1  mg kg -1  mg kg -1  mg kg -1  mg kg -1  mg kg -1  µg l -1
                    As     1       1.5      1.5        2.6      4.1     13 (< 900)  0.2–230
                    Cd     0.12    0.13     0.09       0.028    0.05    0.22 (<240)  0.01–3
                    Cr     2980    200      4          11       35      39         0.1–6
                    Cu     42      90       13         5.5      30      39         2–30
                    Hg     0.004   0.01     0.08       0.16     0.29    0.18       0.0001–2.8
                    Ni     2000    150      0.5        7        9       68         0.02–27
                    Pb     14      3        24         5.7      10      23         0.06–120
                    Sn     0.5     1.5      3.5        0.5      0.5     6          0.0004–0.09
                    Zn     58      100      52         20       30      120        0.2–100








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