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Toxicological assessment of crude oil, oil spill dispersant, and dispersed oil.

机译:原油,溢油分散剂和分散油的毒理学评估。

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The toxicities of crude oil and crude oil plus dispersant Water Accommodated Fractions (WAFs) were evaluated in three toxicity testing systems: spiked and continuous exposures to Mysidopsis bahia were tested in flow-through and static testing systems respectively; microbial toxicity was tested with Microbics Microtox{dollar}spcircler{dollar}. Flourometry and HPLC were used to quantitate WAF concentrations of PAHs and BTEX respectively. The mechanically dispersed WAFs spiked exposure test resulted in a median lethal crude oil loading (LL50) = 3914 mg/L compared to a LL50 = 2766 mg/L for the continuous exposure assay. This data suggest that spiked exposures require higher WAF concentrations to achieve toxic responses similar to those due to continuous exposures. PAH data showed some correlation to aquatic toxicity data, while BTEX data showed no correlation. Microtox{dollar}spcircler{dollar} and fluorescence data revealed that chemically dispersed WAF EC50s were 2 to 29 greater than the mechanically dispersed WAF EC50s. This suggests that the chemically dispersed WAFs have a lower percentage of toxic components per unit concentration that the mechanically dispersed WAFs. No significant toxicity variance was observed between the two aquatic test systems and the microbial assay.
机译:在三个毒性测试系统中评估了原油和原油加分散剂水适应级分(WAF)的毒性:分别在流通式和静态测试系统中测试了加标和连续暴露于Mysidopsis bahia的毒性;用Microbics Microtox {dollar} spcircler {dollar}测试了微生物毒性。荧光法和HPLC分别定量了PAHs和BTEX的WAF浓度。机械分散的WAF加标暴露测试得出的致死原油中位数(LL50)= 3914 mg / L,而连续暴露测定的LL50 = 2766 mg / L。该数据表明加标的暴露需要更高的WAF浓度才能达到与连续暴露相似的毒性反应。 PAH数据显示与水生毒性数据相关,而BTEX数据显示不相关。 Microtox {dollar} spcircler {dollar}和荧光数据表明,化学分散的WAF EC50比机械分散的WAF EC50大2至29。这表明化学分散的WAF与机械分散的WAF相比,每单位浓度的毒性成分所占的百分比更低。在两个水生测试系统和微生物测定之间未观察到明显的毒性变化。

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