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首页> 外文期刊>Journal of Shellfish Research >EFFECTS OF MACONDO CANYON 252 OIL (NATURALLY AND CHEMICALLY DISPERSED) ON LARVAL CRASSOSTREA VIRGINICA (GMELIN, 1791)
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EFFECTS OF MACONDO CANYON 252 OIL (NATURALLY AND CHEMICALLY DISPERSED) ON LARVAL CRASSOSTREA VIRGINICA (GMELIN, 1791)

机译:Macondo Canyon 252油(天然的和化学分散的)对幼虫菜豆(弗吉尼亚州,1791年)的影响

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摘要

A series of acute and sublethal experiments were conducted to examine the potential effects of exposure to water-accommodated fractions (WAFs) of Macondo Canyon 252 crude oil and chemically enhanced (Corexit 9500A dispersant) water-accommodated fractions (CEWAFs) on embryogenesis, larval development, growth, and survival of the eastern oyster, Crassostrea virginica. Nominal exposure concentrations for acute experiments were 0, 100, 200, 400, 800 and 1,200 mg/L for WAFs, and 0, 6.25, 12.5, 25, 50, 100, and 200 mg/L for CEWAFs. Calculated total polycyclic aromatic hydrocarbon (TPAH) values were 0, 22.5, 45, 90, 181, and 271 mu g/L for WAFs, and 0, 4.5, 8.9, 17.8, 35.7, 71, and 142 mu g/L for CEWAFs. The exposure concentration for sublethal experiments was 16 mg/L CEWAF. Total polycyclic aromatic hydrocarbon concentrations represent moderate to high levels of TPAH reported during the Deepwater Horizon (DWH) event. Exposure to acute concentrations of 1 or both of these contaminants was shown to decrease fertilization success (>= 100 mg/L CEWAF), hinder trochophore (>= 100 mg/L WAF, 12.5 mg/L CEWAF) and D-stage(>= 200 mg/L WAF, >= 25 mg/L CEWAF) development, increase the risk of D-stage developmental abnormalities (>= 100 mg/L WAF, >= 100 mg/L CEWAF), and decrease survival of D-stage (1,092 to 261.8 mg/L WAF, 24-96 h LC50; 177.6 to 24.8 mg/L CEWAF, 24-96 h LC50) and eyed (81.9 to 14.5 mg/L CEWAF; 24-96 h LC50) larvae. Exposure to CEWAFs, in general, resulted in increased toxicity over WAFs, likely as a result of the increased bioavailability of hydrocarbons. In contrast to acute exposures, short-term (24-h) sublethal exposure of D-stage larvae to CEWAFs (16 mg/L) had no impact on survival or growth. Although concentrations used represent possible TPAH exposure levels based on maximum reported values, these findings do not imply that oyster larvae were exposed to similar concentrations during or after the DWH event.
机译:进行了一系列急性和亚致死实验,以检验暴露于Macondo Canyon 252原油的水合馏分(WAF)和化学增强的(Corexit 9500A分散剂)水合馏分(CEWAF)对胚胎发生,幼体发育的潜在影响。东部牡蛎Crassostrea virginica的生长,生长和生存。对于WAF,急性实验的名义暴露浓度为0、100、200、400、800和1200 mg / L,对于CEWAF,名义暴露浓度为0、6.25、12.5、25、50、100和200 mg / L。 WAF的总多环芳烃(TPAH)计算值分别为0、22.5、45、90、181和271μg / L,CEWAF的计算值分别为0、4.5、8.9、17.8、35.7、71和142μg / L 。亚致死实验的暴露浓度为16 mg / L CEWAF。在深水地平线(DWH)事件中,多环芳烃的总浓度代表中等至高水平的TPAH。暴露于一种或两种以上污染物的急性浓度显示降低了受精成功率(> = 100 mg / L CEWAF),阻碍了滋养体(> = 100 mg / L WAF,12.5 mg / L CEWAF)和D期= 200 mg / L WAF,> = 25 mg / L CEWAF)发展,增加D期发育异常(> = 100 mg / L WAF,> = 100 mg / L CEWAF)的风险,并降低D-阶段(1,092至261.8 mg / L WAF,24-96 h LC50; 177.6至24.8 mg / L CEWAF,24-96 h LC50)和有眼(81.9至14.5 mg / L CEWAF; 24-96 h LC50)幼虫。通常,暴露于CEWAF会导致毒性超过WAF,这可能是由于碳氢化合物的生物利用度增加所致。与急性暴露相反,D期幼虫短期(24小时)亚致死暴露于CEWAF(16 mg / L)对存活或生长没有影响。尽管所使用的浓度表示基于最大报告值的可能的TPAH暴露水平,但这些发现并不意味着牡蛎幼虫在DWH事件期间或之后也暴露于相似的浓度。

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