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通过河流沉积物不同粒径级分中的金属形态评估沉积物毒性。

Assessment of sediment toxicity by metal speciation in different particle-size fractions of river sediment.

作者信息

Lin J G, Chen S Y, Su C R

机构信息

Institute of Environmental Engineering, National Chiao Tung University, 75 Po-Ai Street, Hsinchu, Chinese Taiwan.

出版信息

Water Sci Technol. 2003;47(7-8):233-41.

Abstract

Mobility and toxicity of metals associated with sediments are generally affected by metal speciation and granular compositions. Due to the various speciation patterns of heavy metals in sediments, it is not reliable to assess the potential toxicity of heavy metals on the aquatic environment with the total concentrations of heavy metals in sediments. The purposes of this study were to investigate the distribution of metal speciation in different particle-size fractions of sediments collected from two rivers (the Ke-Ya River and Ell-Ren River) in Taiwan, and to assess their potential toxicity to the aquatic ecosystem. Metals in the exchangeable, carbonate-bound and Fe/Mn oxide-bound forms obtained by sequential extraction were considered to be mobile and related with anthropogenic pollution. The degree of metal pollution and potential toxicity of sediments were higher in the lower reaches of both rivers. The metal speciation in sediments had a bimodal distribution over particle-size fractions. Heavy metals were subject to accumulation in the silt/clay fraction (< 25 microm) and coarse sand (420-2,000 microm). By normalizing the sum of the exchangeable, carbonate-bound, and Fe/Mn oxide-bound metals, it suggested that the potential toxicity to the aquatic ecosystem was caused by the fine sediments as well as coarse sediments.

摘要

与沉积物相关的金属的迁移性和毒性通常受金属形态和颗粒组成的影响。由于沉积物中重金属存在多种形态模式,仅依据沉积物中重金属的总浓度来评估其对水生环境的潜在毒性是不可靠的。本研究的目的是调查从台湾两条河流(柯雅河和二仁河)采集的沉积物不同粒径组分中金属形态的分布,并评估它们对水生生态系统的潜在毒性。通过连续萃取得到的可交换态、碳酸盐结合态和铁/锰氧化物结合态的金属被认为具有迁移性且与人为污染有关。两条河流下游沉积物的金属污染程度和潜在毒性均较高。沉积物中的金属形态在粒径组分上呈双峰分布。重金属在粉砂/黏土组分(<25微米)和粗砂(420 - 2000微米)中易于积累。通过对可交换态、碳酸盐结合态和铁/锰氧化物结合态金属的总和进行归一化处理,结果表明对水生生态系统的潜在毒性是由细颗粒沉积物以及粗颗粒沉积物共同造成的。

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