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Effect of Corexit 9500A on Mississippi Canyon crude oil weathering patterns using artificial and natural seawater

机译:使用人工和天然海水的Corexit 9500A对密西西比峡谷原油风化模式的影响

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摘要

During the 2010 Deepwater Horizon oil well blowout in the Northern Gulf of Mexico (GoM), the application of 6.97 million litres of chemical dispersants was used at the well-head and on the sea surface to promote oil degradation and weathering of the Mississippi Canyon 252 (MC252) crude oil. Chemical dispersants encourage microbial degradation by increasing the surface area of the spilled oil, which also increases its bioavailability. However, the net beneficial effects of using chemical dispersants on spilled oil and their effects on weathering are not completely elucidated in contemporary literature. The use of simulated environmental conditions in replicate laboratory microcosm weathering experiments were employed to study the weathering of oil and the effects of dispersants on oil weathering. Fresh MC252 oil was evaporatively weathered 40% by-weight to approximate the composition of oil seen in surface slicks during the 2010 spill. This surface oil was then well mixed with two types of seawater, autoclaved artificial seawater, the abiotic control, and Gulf of Mexico seawater, the biotic experiment. Four different weathering combinations were tested: 10 mg of oil mixed in 150 ml artificial seawater (OAS) or natural (i.e., GoM) seawater (ON) and 10 mg of oil with dispersant mixed with 150 ml of artificial seawater (OASD) or natural (i.e., GoM) seawater (OND). For the treatments with dispersant (OASD and OND), the dispersant-to-oil ratio (DoR) was 1:20. The experiment was carried out over 28 days with replicates that were sacrificed on Days 0, 0.5, 3, 7, 14, 21 and 28. For the OAS and OASD treatments, abiotic weathering (i.e., evaporation) dominated the weathering process. However, the ON and OND treatments showed a dramatic and rapid decrease in total concentrations of both alkanes and aromatics with biodegradation dominating the weathering process. Further, there were no identifiable differences in the observed weathering patterns between microcosms using oil or oil treated with dispersant. In the biotic weathering microcosms, the relative degree of individual polycyclic aromatic hydrocarbon (PAH) depletion decreases with an increase in rings and within a homolog series (increased alkylation). The n-C17/pristane and n-C18/phytane ratios rapidly decreased compared to the abiotic weathering experiments. The C2-dibenzothiophenes (DBT)/C2-phenanthrenes (D2/P2) and C3-DBTs/C3-phenanthrenes (D3/P3) ratios initially remained constant during the early stages of weathering and then increased with time showing preferential weathering of the sulfur containing compounds compared to similar sized PAH compounds. These ratios in the abiotic microcosms remained constant over 28 days. Additionally, twenty-four quantitative MC252 oil biomarker ratios were evaluated to determine if their usefulness as oil source-fingerprinting tools were compromised after significant weathering and dispersant augmentation.
机译:在2010年墨西哥北部湾(GoM)的Deepwater Horizo​​n油井井喷期间,在井口和海面使用了697万升化学分散剂,以促进密西西比峡谷252的石油降解和风化(MC252)原油。化学分散剂通过增加溢油的表面积来促进微生物降解,这也增加了其生物利用度。然而,在当代文献中尚未完全阐明使用化学分散剂对溢油的净有益效果及其对风化的影响。在重复的实验室微观风化实验中使用模拟的环境条件来研究油的风化以及分散剂对油风化的影响。将新鲜的MC252油按重量计蒸发了40%,以近似于2010年泄漏期间表面浮油中所见的油成分。然后将这种地表油与两种类型的海水充分混合,高压灭菌的人造海水(非生物控制)和墨西哥湾海水(生物实验)。测试了四种不同的耐候性组合:将10 mg油与150 ml人工海水(OAS)或天然(即GoM)海水(ON)混合,将10 mg油与分散剂与150 ml人工海水(OASD)或天然油混合(即GoM)海水(OND)。对于使用分散剂(OASD和OND)的处理,分散剂与油的比例(DoR)为1:20。实验进行了28天,重复实验分别在第0、0.5、3、7、14、21和28天牺牲。对于OAS和OASD处理,非生物风化作用(即蒸发作用)占主导地位。但是,ON和OND处理表明烷烃和芳烃的总浓度急剧而迅速地下降,而生物降解则在风化过程中占主导地位。此外,使用油或用分散剂处理过的油在微观世界之间观察到的风化模式没有可识别的差异。在生物风化缩影中,单个多环芳烃(PAH)的相对耗竭程度随着环数的增加和在同系物序列内(烷基化程度的增加)而降低。与非生物风化实验相比,n-C17 / rist烷和n-C18 /植烷的比值迅速降低。 C2-二苯并噻吩(DBT)/ C2-菲(D2 / P2)和C3-DBTs / C3-菲(D3 / P3)的比率在风化的早期阶段最初保持恒定,然后随着时间的增加而增加,表明硫优先风化与类似尺寸的PAH化合物相比,含有更多的化合物非生物微观世界中的这些比率在28天内保持不变。此外,评估了24种定量的MC252油生物标志物比率,以确定在显着风化和分散剂增加后,它们作为油源指纹识别工具的有效性是否受到损害。

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