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城市污染河道沉积物AVS与重金属生物毒性研究
引用本文:利锋,温琰茂,朱娉婷.城市污染河道沉积物AVS与重金属生物毒性研究[J].环境科学,2007,28(8):1810-1815.
作者姓名:利锋  温琰茂  朱娉婷
作者单位:1. 中山大学环境科学与工程学院环境污染控制与修复广东省重点实验室,广州,510275;嘉应学院环境工程研究所,梅州,514015
2. 中山大学环境科学与工程学院环境污染控制与修复广东省重点实验室,广州,510275
基金项目:国家自然科学基金项目(40071074);广东省科技计划项目(2006B13501008)
摘    要:采集珠江三角洲典型城市污染河道佛山水道表层沉积物和上覆水样品,测定了沉积物AVS,Eh,SEMPb,SEMCd,SEMCu,SEMZn,SEMNi,SEMCr,及上覆水Eh,DO.同步进行了底栖动物调查,结合调查结果分析了城市污染河道沉积物AVS与重金属生物毒性的关系.主要研究SEM-AVS判据在判断城市重污染河道重金属生物有效性方面的作用.所测AVS最大值为69.579 μmol/g,最小值为0.339 μmol/g,均值为20.283 μmol/g;各采样站位∑SEM5(SEMPb,SEMCd,SEMCu,SEMZn,SEMNi之和)最大值为23.067 μmol/g,最小值为1.062 μmol/g;底栖动物种类和数量均较少,且基本为耐污种,优势种为水丝蚓.13个采样站位中,∑SEM5-AVS<0的有9个,MDS分析结果显示:这9个站位中的7个底栖动物群落结构相似程度高.这表明重污染河道沉积物重金属的生物毒性与SEM-AVS的值关系密切,SEM-AVS判据在判断重污染区域重金属的生物毒性方面具有较大作用;同时说明重污染河流重金属生物毒性比较复杂,不能完全由SEM-AVS解释.

关 键 词:城市污染河道  酸挥发性硫化物  同步提取金属  生物毒性
文章编号:0250-3301(2007)08-1810-06
收稿时间:2007/1/25 0:00:00
修稿时间:2007-01-25

Acid Volatile Sulfide and Heavy Metals Biotoxicity in a Municipal Polluted River
LI Feng,WEN Yan-mao and ZHU Ping-ting.Acid Volatile Sulfide and Heavy Metals Biotoxicity in a Municipal Polluted River[J].Chinese Journal of Environmental Science,2007,28(8):1810-1815.
Authors:LI Feng  WEN Yan-mao and ZHU Ping-ting
Institution:1. Key Laboratory of Environmental Pollution and Remediation Technology of Guangdong Province, School of Environmental Science and Engineering, Sun Yat-sen University, Guangzhou 510275, China; 2. The Research Institute of Environmental Engineering, Jiaying College, Meizhou 514015, China
Abstract:The surface layer of sediment and overlying water samples of Foshan Waterway, a typical municipal polluted river in Pearl River Delta, have been sampled and analyzed. The analytical items of sediment and overlying water include AVS, Eh, SEM(Pb), SEM(Cd), SEM(Cu), SEM(Zn), SEM(Ni), SEM(Cr), and Eh, DO, respectively. The benthic macroinvertebrate investigation has been done at the same time in the same place. Combing the results above, the relationship between AVS and heavy metals biotoxicity in Foshan waterway has been discussed. The main object is to examine if the SEM-AVS criterion is valid in judging the biotoxicity of heavy metals in the heavily polluted river. The range of AVS is from 0.339 micromol/g to 69.579 micromol/g, with the average of 20.283 micromol/g. The maximum sigmaSEM5 (Sum of SEM(PB), SEM(Cd), SEM(Cu), SEM(Zn), SEM(Ni)) is 23.067 micromol/g, while the minimum is 1.062 micromol/g. Both the species and quantity of benthic macroinvertebrate are little, and most of them belong to pollution bearable species, with Limnodrilus sp. as dominative species. There are 9 sampling stations where the sigmaSEM5-AVS are below zero, and the analytical results of Non-matric multi-dimentional scaling (MDS) indicate the benthic community structure of 7 sampling stations among them are similar. It means that the heavy metals biotoxicity in the heavily polluted river has close relationship with the value of SEM-AVS. It also proves that heavy metals biotoxicity in sediment is complicated, which can't be explained by SEM-AVS completely.
Keywords:municipal polluted river  acid volatile sulfide(AVS)  simultaneously extracted metals(SEM)  biotoxicity
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