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澳大利亚新南威尔士州麦夸里湖河口温带海草生态系统中硒、铜、镉、锌、砷和铅的生物转移与生物放大作用。

Biotransference and biomagnification of selenium copper, cadmium, zinc, arsenic and lead in a temperate seagrass ecosystem from Lake Macquarie Estuary, NSW, Australia.

作者信息

Barwick M, Maher W

机构信息

Ecochemistry Laboratory, Applied Ecology Group, University of Canberra, ACT 2601, Bruce, Australia.

出版信息

Mar Environ Res. 2003 Oct;56(4):471-502. doi: 10.1016/S0141-1136(03)00028-X.

DOI:10.1016/S0141-1136(03)00028-X
PMID:12860434
Abstract

In this study the biotransference of selenium copper, cadmium, zinc, arsenic and lead was measured in a contaminated seagrass ecosystem in Lake Macquarie, NSW, Australia, to determine if biomagnification of these trace metals is occurring and if they reach concentrations that pose a threat to the resident organisms or human consumers. Selenium was found to biomagnify, exceeding maximum permitted concentrations for human consumption within carnivorous fish tissue, the highest trophic level examined. Selenium concentrations measured within carnivorous fish were also above those shown to elicit sub-lethal effects in freshwater fish. As comparisons are made to selenium concentrations known to effect freshwater fish, inferences must be made with caution. There was no evidence of copper, cadmium, zinc or lead biomagnification within the food web examined. Copper, cadmium, zinc and lead concentrations were below concentrations shown to elicit adverse responses in biota. Copper concentrations within crustaceans M. bennettae and P. palagicus were found to exceed maximum permitted concentrations for human consumption. It is likely that copper concentrations within these species were accumulated due to the essential nature of this trace metal for many species of molluscs and crustaceans. Arsenic showed some evidence of biomagnification. Total arsenic concentrations are similar to those found in other uncontaminated marine ecosystems, thus arsenic concentrations are unlikely to cause adverse effects to aquatic organisms. Inorganic arsenic concentrations are below maximum permitted concentrations for human consumption.

摘要

在本研究中,对澳大利亚新南威尔士州麦夸里湖一个受污染的海草生态系统中硒、铜、镉、锌、砷和铅的生物转移进行了测量,以确定这些痕量金属是否正在发生生物放大作用,以及它们是否达到对当地生物或人类消费者构成威胁的浓度。研究发现,硒会发生生物放大作用,在肉食性鱼类组织(所检测的最高营养级)中超过了人类消费的最大允许浓度。肉食性鱼类体内测得的硒浓度也高于对淡水鱼产生亚致死效应的浓度。由于是与已知对淡水鱼有影响的硒浓度进行比较,因此必须谨慎推断。在所研究的食物网中,没有证据表明铜、镉、锌或铅会发生生物放大作用。铜、镉、锌和铅的浓度低于对生物群产生不良反应的浓度。发现甲壳类的贝氏沼虾和九齿扇虾体内的铜浓度超过了人类消费的最大允许浓度。这些物种体内的铜浓度可能是由于这种痕量金属对许多软体动物和甲壳类物种的必需性而积累起来的。砷显示出一些生物放大的迹象。总砷浓度与其他未受污染的海洋生态系统中的浓度相似,因此砷浓度不太可能对水生生物造成不利影响。无机砷浓度低于人类消费的最大允许浓度。

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