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蓝藻毒素对底栖动物的毒理学研究进展
引用本文:薛庆举,苏小妹,谢丽强.蓝藻毒素对底栖动物的毒理学研究进展[J].生态学报,2015,35(14):4570-4578.
作者姓名:薛庆举  苏小妹  谢丽强
作者单位:中国科学院南京地理与湖泊研究所湖泊与环境国家重点实验室, 南京 210008;中国科学院大学, 北京 100049,中国科学院南京地理与湖泊研究所湖泊与环境国家重点实验室, 南京 210008;中国科学院大学, 北京 100049,中国科学院南京地理与湖泊研究所湖泊与环境国家重点实验室, 南京 210008
基金项目:中国科学院百人计划(y3bro11050); 南京地理与湖泊研究所一三五项目(NIGLAS2012135015)
摘    要:近年,由于人类活动加剧,大量氮磷等营养物质流入湖泊等缓流水体,导致水体富营养化。而由此引起有害蓝藻水华的频繁爆发,使生态环境和人类健康受到严重威胁。相关研究表明,蓝藻水华的爆发不仅能够使水体水质恶化,其中一些产毒藻类还会产生大量蓝藻毒素,对水生生物产生重要影响。底栖动物作为水体生态系统的重要组成部分,在食物网中有重要作用,同时其中的许多种类又与人类息息相关,因此关于水华蓝藻毒素对淡水底栖动物的毒理学研究具有重要意义。在介绍蓝藻毒素概况的基础上,综述了蓝藻毒素的致毒机理和对底栖动物的影响,展望了研究方向。

关 键 词:底栖动物  蓝藻毒素  食物网  环境毒理学
收稿时间:2013/8/26 0:00:00
修稿时间:2015/5/12 0:00:00

Advances on cyanotoxin toxicology of zoobenthos
XUE Qingju,SU Xiaomei and XIE Liqiang.Advances on cyanotoxin toxicology of zoobenthos[J].Acta Ecologica Sinica,2015,35(14):4570-4578.
Authors:XUE Qingju  SU Xiaomei and XIE Liqiang
Institution:State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China;University of Chinese Academy of Sciences, Beijing 100049, China,State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China;University of Chinese Academy of Sciences, Beijing 100049, China and State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China
Abstract:In recent years, owing to the intensified human activities, a large number of nutrients, primarily nitrogen and phosphorus, flow into lakes and other water bodies and result in serious eutrophication. However, the cultural eutrophication is often associated with cyanobacteria blooms which can create significant water quality and human health problems. What''s more, some species of cyanobacteria are capable of producing secondary metabolites named cyanotoxins. Mass populations of toxin-producing cyanobacteria are in natural and controlled water bodies include blooms and scums of planktonic species, and mats and biofilms of benthic species. Toxic cyanobacterial populations have been reported in freshwaters in over 45 countries. These toxins can be classified into five main types according to their mechanism of action in vertebrates: hepatotoxins, cytotoxins, dermatotoxins, neurotoxins and irritant toxins. These toxins (microcystins, nodularins, saxitoxins, anatoxin-a, anatoxin-a(s), cylindrospermopsin) are structurally diverse and their effects range from liver damage, including liver cancer, to neurotoxicity. There are more than 80 microcystin congeners, microcystin-LR (L, L-leucine; R, L-arginine) is the best studied cyanobacterial toxin, whereas information for the other toxins is largely lacking. Many studies on the effects of cyanobacteria and their toxins over a wide range of aquatic organisms, including invertebrates and vertebrates, have reported acute effects (e.g., reduction in survivorship, feeding inhibition, paralysis), chronic effects (e.g., reduction in growth and fecundity), biochemical alterations (e.g., activity of phosphatases, GST, AChE, proteases), and behavioral alterations. Research has also focused on the potential for bioaccumulation and transferring of these toxins through the food chain. In general, the toxins can transfer to human bodies by drinking and very little by entertainment or health care products. In some special circumstances, the toxins can also be transferred into human bodies by dialysis. Be the highest level of the food chain, toxins can also transfer to human beings by eating aquatic products. As an important part of the aquatic ecosystem, zoobenthos plays an important role in the aquatic food web. On the one hand, it plays an important part in the material and energy flow process. It is not only the source of the predacity fish, but also the predator of the phytoplankton, zooplankton or organic detritus. On the other hand, some species of the zoobenthos can also be used in water cleaning and influence the formation of the eutrophication. The most important thing is that many of them are even closely related to human beings (directly or indirectly food sources), especially the people leave around the lakes and other water bodies, so the study of the cyanotoxin toxicology of zoobenthos is of great importance. In this review, we first summarized the mechanism of toxicity of cyanotoxin on zoobenthos on the base of a brief introduction of cyanotoxins, with emphasis on microcystins. Secondly, the effects of cyanotoxins on zoobenthos is discussed in details, including the bioaccumulation and elimination of the cyanotoxin, the effects of cyanotoxin and the food web studies about cyanotoxin (mainly microcystis) in zoobenthos. At last, we prospect the further research directions as well as drawbacks and future needs in this field of research.
Keywords:zoobenthos  cyanotoxin  food web  environmental toxicology
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