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来自清洁湖泊和受金属污染湖泊的野生黄鲈(黄斑鲈)鳃中镉和铜的结合以及肠道对镉的吸收

Branchial cadmium and copper binding and intestinal cadmium uptake in wild yellow perch (Perca flavescens) from clean and metal-contaminated lakes.

作者信息

Klinck J S, Green W W, Mirza R S, Nadella S R, Chowdhury M J, Wood C M, Pyle G G

机构信息

Department of Biology, McMaster University, Hamilton, Ont. L8S 4K1, Canada.

出版信息

Aquat Toxicol. 2007 Aug 30;84(2):198-207. doi: 10.1016/j.aquatox.2007.03.024. Epub 2007 Jun 16.

Abstract

Branchial binding kinetics and gastro-intestinal uptake of copper and cadmium where examined in yellow perch (Perca flavescens) from a metal-contaminated lake (Hannah Lake, Sudbury, Ontario, Canada) and an uncontaminated lake (James Lake, North Bay, Ontario, Canada). An in vivo approach was taken for gill binding comparisons while an in vitro gut binding assay was employed for gastro-intestinal tract (GIT) uptake analysis. By investigating metal uptake at the gill and the gut we cover the two main routes of metal entry into fish. Comparisons of water and sediment chemistries, metal burdens in benthic invertebrate, and metal burdens in the livers of perch from the two study lakes clearly show that yellow perch from Hannah L. are chronically exposed to a highly metal-contaminated environment compared to a reference lake. We found that metal-contaminated yellow perch showed no significant difference in gill Cd binding compared to reference fish, but they did show significant decreases in new Cd binding and absorption in their GITs. The results show that gill Cd binding may involve low-capacity, high-affinity binding sites, while gastro-intestinal Cd uptake involves binding sites that are high-capacity, low-affinity. From this we infer that Cd may be more critically controlled at the gut rather than gills. Significant differences in branchial Cu binding (increased binding) were observed in metal-contaminated yellow perch. We suggest that chronic waterborne exposure to Cu (and/or other metals) may be the dominant influence in gill Cu binding rather than chronic exposure to high Cu diets. We give supporting evidence that Cd is taken up in the GIT, at least in part, by a similar pathway as Ca(2+), principally that elevated dietary Ca(2+) reduces Cd binding and uptake. Overall our study reveals that metal pre-exposure via water and diet can alter uptake kinetics of Cu and Cd at the gill and/or the gut.

摘要

研究了来自受金属污染湖泊(加拿大安大略省萨德伯里的汉娜湖)和未受污染湖泊(加拿大安大略省北湾的詹姆斯湖)的黄鲈(Perca flavescens)鳃对铜和镉的结合动力学以及胃肠道对它们的吸收情况。采用体内方法进行鳃结合比较,同时采用体外肠道结合试验进行胃肠道(GIT)吸收分析。通过研究鳃和肠道对金属的吸收,我们涵盖了金属进入鱼类的两条主要途径。对两个研究湖泊的水和沉积物化学、底栖无脊椎动物中的金属负荷以及鲈鱼肝脏中的金属负荷进行比较,结果清楚地表明,与参考湖泊相比,汉娜湖的黄鲈长期暴露于高度金属污染的环境中。我们发现,与参考鱼类相比,受金属污染的黄鲈鳃对镉的结合没有显著差异,但它们胃肠道中新镉的结合和吸收却显著下降。结果表明,鳃对镉的结合可能涉及低容量、高亲和力的结合位点,而胃肠道对镉的吸收涉及高容量、低亲和力的结合位点。由此我们推断,镉在肠道而非鳃处可能受到更严格的控制。在受金属污染的黄鲈中观察到鳃对铜的结合存在显著差异(结合增加)。我们认为,长期通过水体接触铜(和/或其他金属)可能是鳃对铜结合的主要影响因素,而非长期接触高铜饮食。我们提供了支持性证据,表明镉至少部分地通过与钙(Ca2+)相似的途径在胃肠道中被吸收,主要是饮食中钙(Ca2+)升高会降低镉的结合和吸收。总体而言,我们的研究表明,通过水和饮食预先接触金属可以改变鳃和/或肠道对铜和镉的吸收动力学。

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