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Temporal trends and spatial distribution of dioxins and furans in lake trout or lake whitefish from the Canadian Great Lakes

机译:加拿大大湖中的鳟鱼或白鲑湖中二恶英和呋喃的时间趋势和空间分布

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Concentrations of the seventeen 2,3,7,8-substituted, most toxic congeners of polychlorinated dibenzo-p-dioxins (PCDDs) and polychlorinated dibenzofurans (PCDFs) were measured in lake trout (Salvelinus namaycush) or lake whitefish (Coregonus clupeaformis) collected between 1989 and 2003 from the Canadian Great Lakes as a part of the on-going Sport Fish Contaminant Monitoring Program of the Ontario Ministry of the Environment. These monitoring data were used to assess temporal trends and spatial variations of these compounds in the Canadian Great Lakes. Toxic equivalents (TEQs) were calculated using the measured congener concentrations and toxicity equivalency factors (TEFs) published by the World Health Organization in 1998. Five congeners, namely 2,3,7,8-TCDD, 2,3,7,8-TCDF, 1,2,3,7,8-PeCDD, 1,2,3,7,8-PeCDF, and 2,3,4,7,8-PeCDF, were the most dominant congeners among the 17 congeners analyzed. The highest TEQs were found for Lake Ontario lake trout (22-54 pg g~(-1)) while the TEQs for the other Canadian Great Lakes were 60-95% lower. Non-parametric Mann-Kendall and Sen's tests performed on TEQs and PCDD/Fs standardized at a mean lake trout length of 60 cm suggest a linearly decreasing trend for PCDD/Fs in lake trout from Lakes Ontario and Huron. There was no monotonously increasing or decreasing trend found for Lake Superior lake trout. The ratios of 2,3,7,8-TCDD to 2,3,7,8-TCDF concentrations were generally constant during the 1989-2003 period with the values being in the order of Lakes Superior (0.05-0.3) ≤ Huron (0.16-0.25) Ontario (0.56-0.88). These spatial differences observed in the relative abundance of TCDD and TCDF suggest that the sources of dioxins and furans differ between the upper and lower Great Lakes.
机译:在湖鳟(Salvelinus namaycush)或湖白鱼(Coregonus clupeaformis)中测量了17种2,3,7,8-取代的,最有毒的多氯二苯并-对-二恶英(PCDDs)和多氯二苯并呋喃(PCDF)的浓度。在1989年至2003年期间,这是安大略省环境部正在进行的运动鱼污染物监测计划的一部分。这些监测数据用于评估加拿大大湖地区这些化合物的时间趋势和空间变化。使用世界卫生组织于1998年发布的测得的同类物浓度和毒性当量因子(TEF)计算有毒当量(TEQ)。五个同类物,即2,3,7,8-TCDD,2,3,7,8- TCDF,1,2,3,7,8-PeCDD,1,2,3,7,8-PeCDF和2,3,4,7,8-PeCDF是所分析的17个同类物中最主要的同类物。安大略湖鳟鱼的TEQ最高(22-54 pg g〜(-1)),而加拿大其他五大湖的TEQ则低60-95%。对标准的TEQ和PCDD / Fs进行的非参数Mann-Kendall和Sen的测试在平均湖鳟的长度为60 cm的情况下进行了测试,这表明安大略湖和休伦湖鳟的PCDD / Fs呈线性下降的趋势。苏必利尔湖鳟鱼没有单调增加或减少的趋势。 2,3,7,8-TCDD与2,3,7,8-TCDF浓度的比率在1989-2003年期间通常是恒定的,其值在苏必利尔湖(0.05-0.3)≤休伦湖( 0.16-0.25)安大略(0.56-0.88)。在TCDD和TCDF相对丰度中观察到的这些空间差异表明,上,下大湖之间的二恶英和呋喃来源不同。

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