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首页> 外文期刊>Archives of Environmental Contamination and Toxicology >Biomarkers of Contaminant Exposure in Northern Pike (Esox lucius) from the Yukon River Basin, Alaska
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Biomarkers of Contaminant Exposure in Northern Pike (Esox lucius) from the Yukon River Basin, Alaska

机译:来自阿拉斯加育空河盆地北部派克(Esox lucius)污染物暴露的生物标志物

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摘要

As part of a larger investigation, northern pike (n = 158; Esox lucius) were collected from ten sites in the Yukon River Basin (YRB), Alaska, to document biomarkers and their correlations with organochlorine pesticide (total p,p’-DDT, total chlordane, dieldrin, and toxaphene), total polychlorinated biphenyls (PCBs), and elemental contaminant (arsenic, cadmium, copper, lead, total mercury, selenium, and zinc) concentrations. A suite of biomarkers including somatic indices, hepatic 7-ethoxyresorufin O-deethylase (EROD) activity, vitellogenin concentrations, steroid hormone (17B- ustradiol and 16-kebtestosteront) concentrations, splenic macrophage aggregates (MAs), oocyte atresia, and other microscopic anomalies in various tissues were documented in YRB pike. Mean condition factor (0.50 to 0.68), hepatosomatic index (1.00% to 3.56%), and splenosomatic index (0.09% to 0.18%) were not anomalous at any site nor correlated with any contaminant concentration. Mean EROD activity (0.71 to 17.51 pmol/min/mg protein) was similar to basal activity levels previously measured in pike and was positively correlated with selenium concentrations (r = 0.88, P < 0.01). Vitellogenin concentrations in female (0.09 to 5.32 mg/mL) and male (<0.0005 to 0.097 mg/mL) pike were not correlated with any contaminant, but vitellogenin concentrations >0.01 mg/mL in male pike from multiple sites indicated exposure to estrogenic compounds. Mean steroid hormone concentrations and percent oocyte atresia were not anomalous in pike from any YRB site. Few site differences were significant for mean MA density (1.86 to 6.42 MA/mm2), size (812 to 1481 μm2), and tissue occupied (MA-%; 0.24% to 0.75%). A linear regression between MA-% and total PCBs was significant, although PCB concentrations were generally low in YRB pike (≤63 ng/g), and MA-% values in female pike (0.24% to 0.54%) were lower than in male pike (0.32% to 0.75%) at similar PCB concentrations. Greater numbers of MAs were found as zinc concentrations increased in YRB female pike, but it is unlikely that this is a causative relationship. Histological abnormalities observed in gill, liver, spleen, and kidney tissues were not likely a result of contaminant exposure but provide information on the general health of YRB pike. The most common histologic anomalies were parasitic infestations in various organs and developing nephrons and nephrocalcinosis in posterior kidney tissues. Overall, few biomarker responses in YRB pike were correlated with chemical contaminant concentrations, and YRB pike generally appeared to be healthy with no site having multiple anomalous biomarker responses.
机译:作为较大规模调查的一部分,从阿拉斯加育空河盆地(YRB)的十个地点收集了北派克(n = 158; Esox lucius),以记录生物标志物及其与有机氯农药的关系(总p,p'-DDT ,总氯丹,狄氏剂和毒杀芬),总多氯联苯(PCB)和元素污染物(砷,镉,铜,铅,总汞,硒和锌)的浓度。一系列生物标志物,包括体细胞指标,肝7-乙氧基异色蛋白O-脱乙基酶(EROD)活性,卵黄蛋白原浓度,类固醇激素(17B-超二醇和16-酮睾酮)浓度,脾脏巨噬细胞聚集体(MAs),卵母细胞闭锁和其他微观异常在YRB派克中记录了各种组织中的组织。平均状况因子(0.50至0.68),肝体指数(1.00%至3.56%)和脾体指数(0.09%至0.18%)在任何位置都不异常,也不与任何污染物浓度相关。平均EROD活性(0.71至17.51 pmol / min / mg蛋白质)与以前在梭子鱼中测得的基础活性水平相似,并且与硒浓度呈正相关(r = 0.88,P <0.01)。女性(0.09至5.32 mg / mL)和男性(<0.0005至0.097 mg / mL)派克中的卵黄蛋白原浓度与任何污染物均不相关,但是来自多个部位的雄性派克中的卵黄蛋白原浓度> 0.01 mg / mL表明暴露于雌激素化合物。在任何YRB部位的派克中,平均类固醇激素浓度和卵母细胞闭锁百分比均未异常。对于平均MA密度(1.86至6.42 MA / mm2 ),大小(812至1481μm2)和组织占据(MA%; 0.24%至0.75%),几乎没有明显的部位差异。尽管YRB派克的PCB浓度通常较低(≤63ng / g),而雌性派克的MA-%值(0.24%至0.54%)低于男性,但MA-%与总PCBs之间的线性回归显着。在类似的PCB浓度下产生派克(0.32%至0.75%)随着YRB雌性梭子鱼中锌浓度的增加,MA的数量也增加了,但这不太可能是因果关系。在g,肝脏,脾脏和肾脏组织中观察到的组织学异常可能不是污染物暴露的结果,但提供了有关YRB派克总体健康的信息。最常见的组织学异常是各种器官的寄生虫侵扰,以及肾后组织中不断发展的肾单位和肾钙化病。总体而言,YRB派克中很少有生物标记反应与化学污染物浓度相关,并且YRB派克通常看起来是健康的,没有多个生物标记反应异常的部位。

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    Columbia Environmental Research Center United States Geological Survey 4200 New Haven Road Columbia MO 65201 USA;

    Leetown Science Center United States Geological Survey 11649 Leetown Road Kearneysville WV 24530 USA;

    Center for Environmental and Human Toxicology University of Florida P. O. Box 100185 Gainesville FL 32611 USA;

    Northwest Fisheries Science Center National Oceanic and Atmospheric Administration 2725 Montlake Boulevard Seattle WA 98112 USA;

    Center for Environmental and Human Toxicology University of Florida P. O. Box 100185 Gainesville FL 32611 USA;

    Columbia Environmental Research Center United States Geological Survey 4200 New Haven Road Columbia MO 65201 USA;

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