Anawar H M, Garcia-Sanchez A, Santa Regina I
Department of Environmental Geochemistry, IRNASA-CSIC, Cordel de Merinas 40-52, Aptdo 257, Salamanca 37008, Spain.
Chemosphere. 2008 Feb;70(8):1459-67. doi: 10.1016/j.chemosphere.2007.08.058. Epub 2007 Oct 22.
Elevated levels of bioavailable As in mining soils, agricultural areas and human habitats may cause potential toxicity to human health, plants and microbe. Therefore, it is essential to determine proper soil chemical extraction method in order to estimate plant-available As in mining soils and protect agricultural and environmental ecosystems by evaluation of environmental risk and implementation of remediation measures. In this study, six single soil chemical extraction processes and four-step sequential chemical extraction protocol were used to determine the relative distribution of As in different chemical forms of soils and their correlations with total As in plants grown in mining areas and greenhouse experiments. The strongest relationship between As determined by single soil chemical extraction and As in plant biomass was found for sodium acetate and mixed acid extractant. The mean percent of total As extracted was: ammonium oxalate (41%)>hydroxylamine hydrochloride (32%)>mixed acid (16%)>phosphate (6%)>sodium acetate (1.2%)>water (0.13%). This trend suggests that most of the As in these soils is inside the soil mineral matrix and can only be released when iron oxides and other minerals are dissolved by the stronger chemical extractant. Single soil chemical extraction methods using sodium acetate and mixed acids, that extract As fractions complexed to soil particles or on the surface of mineral matrix of hydrous oxides of Fe, Mn and Al (exchangeable+sorbed forms) can be employed to estimate and predict the bioavailable As fraction for plant uptake in mining affected soils. In sequential chemical extraction methods, ammonium nitrate and hydroxylamine hydrochloride may be used to provide closer estimates of plant-available As in mining soils.
矿区土壤、农业区域和人类栖息地中生物可利用砷含量的升高可能会对人类健康、植物和微生物造成潜在毒性。因此,确定合适的土壤化学提取方法至关重要,以便估算矿区土壤中植物可利用的砷含量,并通过评估环境风险和实施修复措施来保护农业和环境生态系统。在本研究中,采用六种单一土壤化学提取方法和四步连续化学提取方案,来确定土壤中不同化学形态砷的相对分布及其与矿区种植植物和温室实验中植物总砷含量的相关性。对于醋酸钠和混合酸提取剂,发现单一土壤化学提取法测定的砷与植物生物量中的砷之间存在最强的相关性。提取的总砷平均百分比为:草酸铵(41%)>盐酸羟胺(32%)>混合酸(16%)>磷酸盐(6%)>醋酸钠(1.2%)>水(0.13%)。这一趋势表明,这些土壤中的大部分砷存在于土壤矿物基质内部,只有在铁氧化物和其他矿物被更强的化学提取剂溶解时才会释放出来。使用醋酸钠和混合酸的单一土壤化学提取方法,可提取与土壤颗粒络合或存在于铁、锰和铝的水合氧化物矿物基质表面的砷组分(可交换+吸附态),可用于估算和预测受采矿影响土壤中植物吸收的生物可利用砷组分。在连续化学提取方法中,硝酸铵和盐酸羟胺可用于更准确地估算矿区土壤中植物可利用的砷含量。