Department of Oceanography and Coastal Science, School of Coast and Environment, Louisiana State University, Energy Coast and Environment Building, Baton Rouge, LA 70803, USA.
Chemosphere. 2015 Jan;119:562-567. doi: 10.1016/j.chemosphere.2014.07.050. Epub 2014 Aug 12.
On April 20, 2010, the BP Deepwater Horizon (DWH) offshore oil platform experienced an explosion which triggered the largest marine oil spill in US history. Approximately 7.9 million liters of dispersant, Corexit EC9500A, was used during the spill between May 15th and July 12th. Marsh soil samples were collected from an unimpacted marsh site proximal to coastal areas that suffered light to heavy oiling for a laboratory evaluation to determine the effect of Corexit on the wetland soil microbial biomass as well as N-mineralization and denitrification rates. Microbial biomass nitrogen (N) values were below detection for the 1:10, 1:100 and 1:1000 Corexit:wet soil treatments. The potentially mineralizable N (PMN) rate correlated with microbial biomass with significantly lower rates for the 1:10 and 1:100 Corexit:wet soil additions. Potential denitrification rates for Corexit:wet soil ratios after immediate dispersant exposure were below detection for the 1:10 treatment, while the 1:100 was 7.6±2.7% of the control and the 1:1000 was 33±4.3% of the control. The 1:10000 treatment was not significantly different from the control. Denitrification rates measured after 2 weeks exposure to the surfactant found the 1:10 treatment still below detection limit and the 1:100 ratio was 12±2.6% of the control. Results from this lab study suggest that chemical dispersants have the potential to negatively affect the wetland soil microbial biomass and resultant microbial activity. Consequences of exposure led to reductions in several important microbial-regulated ecosystem services including water quality improvement (denitrification) and ecosystem primary productivity (N-mineralization). Future studies should investigate the longer-term impacts of dispersant exposure on the microbial consortia to determine if microbial activity recovers over time.
2010 年 4 月 20 日,BP 深海地平线(DWH)海上石油平台发生爆炸,引发美国历史上最大的海洋石油泄漏事件。在 5 月 15 日至 7 月 12 日期间,大约使用了 790 万升分散剂 Corexit EC9500A。从靠近遭受轻到重油污的沿海地区的未受影响的沼泽地采集了沼泽土壤样本,以便在实验室中进行评估,以确定 Corexit 对湿地土壤微生物生物量以及氮矿化和反硝化速率的影响。微生物生物量氮(N)值在 1:10、1:100 和 1:1000 Corexit:湿土处理中低于检测值。潜在可矿化氮(PMN)速率与微生物生物量相关,1:10 和 1:100 Corexit:湿土添加物的速率明显较低。立即暴露于分散剂后,Corexit:湿土比例的潜在反硝化速率在 1:10 处理中低于检测值,而 1:100 为对照的 7.6±2.7%,1:1000 为对照的 33±4.3%。1:10000 处理与对照无显著差异。暴露于表面活性剂 2 周后测量的反硝化速率发现,1:10 处理仍低于检测限,而 1:100 比例为对照的 12±2.6%。该实验室研究的结果表明,化学分散剂有可能对湿地土壤微生物生物量和由此产生的微生物活性产生负面影响。暴露的后果导致一些重要的微生物调节的生态系统服务减少,包括水质改善(反硝化)和生态系统初级生产力(氮矿化)。未来的研究应调查分散剂暴露对微生物群落的长期影响,以确定微生物活性是否随时间恢复。