CHEMISTRY OF METAL RETENTION BY SOILS - SEVERAL PROCESSES ARE EXPLAINED
CHEMISTRY OF METAL RETENTION BY SOILS - SEVERAL PROCESSES ARE EXPLAINED
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DOI:
10.1021/es00067a001
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发表时间:
1989-09-01
影响因子:
11.4
通讯作者:
EVANS, LJ
中科院分区:
文献类型:
--
作者:
EVANS, LJ
For thousands of years, soil has been the repository of society’s wastes. The excavation of middens, which has provided archaeologists with valuable information on the daily life of past civili-zations, has shown that land disposal has been carried out since antiquity. In recent years, however, the rapid in-crease in the disposal of municipal and industrial wastes in landfill sites, and the application both of leachates from these landfill sites and of sewage sludge to land, is causing much concern about environmental pollution. Moreover, metals also are being addedto soil either directly through agricultural prac-tices or indirectly through the atmo-spheric precipitation of industrial pollutants and automobile emissions. Many metals form stable complexes with biomolecules, and their presence in even small amounts can be detrimental to plants and animals. The relative toxicity of metals to plants and animals, however, can vary greatly (see box); metals that form stable complexes with ligands tendto be the most toxic (1, 2). The possible contamination of groundwater supplies by metals leached from landfill sites, therefore, is a major environmental concern. This concern has led many industrial nations to specify the maximum acceptableconcentra-tions of metals, such as barium, cad-mium, chromium, lead, mercury, and silver in drinking water. The soils and sediments formed or deposited on the land surface can, how-ever, act as vast reservoirs for the con-tainment of these metals. Soils are important particularly because they contain surface-active mineral and hu-mic constituents involved in reactions that affect metal retention. The retention of metals by soil or other surface materials has been a focus of much research in recent years (4). Various mathematical models have been developed to predict the speciation of metals in natural waters, and mecha-nistic modelshave been formulated to quantify the retention of metals by both mineral and organic soil constituents (5, 6).The surfaces of fine-grained soil particles are very active chemically; sur-face sites are negatively or positively charged or they are electrically neutral. Oppositely charged metallic counterions from solutions in soils are attracted to these charged surfaces. The relative proportions of ions attracted to these various sites depends on the degree of acidity or alkalinity of the soil, on its mineralogical composition, and on its