Lee P K, Touray J C, Baillif P, Ildefonse J P
Korea Institute of Geology, Mining and Materials, Yusung, Korea.
Sci Total Environ. 1997 Aug 1;201(1):1-15. doi: 10.1016/s0048-9697(97)84048-x.
A retention pond is a part of a drainage system designed to control water flow during rainstorms and to trap contaminated solid particles washed off by runoff water from a motorway. A series of studies have been carried out concerning the physico-chemical characteristics of the particles which settle down in such a pond in order to evaluate the effectiveness of the pond as a trap for heavy metals such as Pb, Zn and Cd. The highly contaminated roadside soil and the uncontaminated background soil were also studied for comparison. The settling particles had heavy metal concentrations 2-8 times higher than the background Sologne soil, depending on the metals. Heavy metal concentrations in the roadside soil were 7-26 times higher than those in the former. Sequential extractions, using the procedure of Tessier et al. (1979) illustrate that the highly contaminated roadside soil consisted mainly of the readily soluble fractions for all three heavy metals, with a limited proportion of residual metals. In the settling particles, the proportion of the latter is significantly increased, up to one-third of the total. The high concentration differences between the roadside soil and the settling particles indicates that most of the heavy metals are lost to the surroundings even before reaching the retention pond. Cadmium exhibited a specific behavior in that the most soluble fraction (exchangeable), which is negligible for Pb and Zn, occupied as much as one-fourth of the total in the roadside soil. Based on the 'enrichment factor' normalized to Fe introduced by Helz in 1976, the degree of contamination by heavy metals for the roadside soil and the settling particles was evaluated. The level of contamination was very severe in the roadside soil, while it was not so great in the settling particles. Suggestions are made to improve their removal efficiency.
滞留池是排水系统的一部分,旨在控制暴雨期间的水流,并截留高速公路径流冲刷下来的受污染固体颗粒。为了评估该滞留池作为铅、锌和镉等重金属捕集器的有效性,已经对沉淀在该池中颗粒的物理化学特性进行了一系列研究。还对高污染的路边土壤和未受污染的背景土壤进行了研究以作比较。沉淀颗粒中的重金属浓度比索洛涅背景土壤高出2至8倍,具体取决于金属种类。路边土壤中的重金属浓度比前者高出7至26倍。采用Tessier等人(1979年)的方法进行的连续萃取表明,高污染的路边土壤中,所有三种重金属主要以易溶态存在,残留态金属所占比例有限。在沉淀颗粒中,后者的比例显著增加,高达总量的三分之一。路边土壤和沉淀颗粒之间的高浓度差异表明,大多数重金属在到达滞留池之前就已流失到周围环境中。镉表现出一种特殊行为,即对铅和锌可忽略不计的最易溶态(可交换态),在路边土壤中占总量的四分之一之多。根据Helz于1976年引入的以铁为标准的“富集因子”,对路边土壤和沉淀颗粒的重金属污染程度进行了评估。路边土壤的污染程度非常严重,而沉淀颗粒中的污染程度则没那么大。文中还提出了提高其去除效率的建议。