Alumaa Priit, Kirso Uuve, Petersell Valter, Steinnes Eiliv
National Institute of Chemical Physics and Biophysics, Akadeemia tee 23, Tallinn 12618, Estonia.
Int J Hyg Environ Health. 2002 Feb;204(5-6):375-6. doi: 10.1078/1438-4639-00114.
The surface soil is a major recipient of pollutants, including heavy metals, through atmospheric deposition, agricultural practices, and waste disposal. In the present work the sorption capacity of different types of soils to toxic heavy metals, i.e. chromium, copper, cadmium and lead has been studied. Experimental adsorption data for metals to the soil obtained by the batch method were fitted by linear isotherm. The various soils showed a very different behaviour in sorption of heavy metals. The distribution coefficient Kd, which is an indication of the adsorbing capacity of the substrate, varies within a wide range, from 57 to 53,000 l kg-1. Desorption of metals from the solid phase was found to be small, indicating that the soil matrix is affecting the metal mobility by modifying the bonding of pollutants to the soil system consequently affecting the potential for soil remediation processes.
表层土壤是包括重金属在内的污染物的主要接收者,这些污染物通过大气沉降、农业活动和废物处理进入土壤。在本研究中,研究了不同类型土壤对有毒重金属(即铬、铜、镉和铅)的吸附能力。采用分批法获得的金属在土壤上的实验吸附数据用线性等温线进行拟合。各种土壤在重金属吸附方面表现出非常不同的行为。分配系数Kd是底物吸附能力的一个指标,其变化范围很广,从57到53000 l kg-1。发现金属从固相的解吸量很小,这表明土壤基质通过改变污染物与土壤系统的结合来影响金属的迁移率,从而影响土壤修复过程的潜力。