Exposure Assessment Applications, LLC, 6045 N. 27th St., Arlington, VA 22207, USA.
Division of Environmental Health Sciences, University of Minnesota School of Public Health, 420 Delaware St. SE, Minneapolis, MN 55455, USA.
Ann Work Expo Health. 2022 Apr 7;66(Suppl 1):i202-i217. doi: 10.1093/annweh/wxab056.
The Deepwater Horizon (DWH) drilling unit explosion above the Macondo oil well on 20 April 2010 caused the release of approximately 4.9 million barrels (779 million L) of oil into the Gulf of Mexico. As part of a larger spill response and clean-up effort, approximately 1.84 million gallons (6.81 million L) of chemical dispersants COREXIT™ EC9500A and COREXIT™ EC9527A were applied to the resultant oil slicks through spraying on the water surface by plane and by vessel and through injection at the release source near the seabed. The GuLF STUDY is investigating the health effects of workers involved in the oil spill response and clean-up after the DWH explosion, and estimates of possible exposure to chemical dispersants were needed. Exposures were estimated to the volatile components of COREXIT™ EC9500A [petroleum distillates, hydrotreated light, and propylene glycol (PG)] and of COREXIT™ EC9527A [2-butoxyethanol (2-BE) and PG] using two of AIHA IHMOD2.0© mathematical modeling tools along with the dispersants' chemical and physical properties. Monte Carlo simulations were used to reflect uncertainty in input parameters with both the two-box, constant emission model and the near and mid field plume model for indoor and outdoor activities, respectively. Possible exposure scenarios considered various evaporation rates, sizes of the dispersant pool, wind speeds, and ventilation rates. For the two-box model, mean near field exposure estimates to 2-BE ranged from 0.9 to 5.7 ppm, while mean far field estimated exposures ranged from 0.3 to 3.5 ppm. Estimates of mean near field plume model exposures ranged from 0.01 to 3.7 ppm at 2.5 ft from the source, and <0.01 to 0.3 ppm at 10 ft from the source. Estimated exposures to PG were approximately 10% of the calculated 2-BE exposures and exposures to petroleum distillates about 40% higher than the 2-BE estimates. Results indicate that compared with current occupational exposure guidelines, overexposure to petroleum distillates and PG probably did not occur in our study, but under some conditions, for short periods, exposure to 2-BE may have exceeded the limits for peak exposures. These estimates were developed for use in job-exposure matrices to estimate exposures of workers having contact with dispersant vapors for the GuLF STUDY.
2010 年 4 月 20 日,深水地平线(DWH)钻井平台在马孔多油井上方发生爆炸,导致约 490 万桶(77.9 亿升)石油流入墨西哥湾。作为大规模溢油应急和清理工作的一部分,大约有 184 万加仑(6.81 亿升)的化学分散剂 COREXIT™ EC9500A 和 COREXIT™ EC9527A 被应用于由此产生的浮油,方法是通过飞机和船只在水面上喷洒,以及通过在靠近海底的泄漏源进行注入。GuLF STUDY 正在调查深水地平线爆炸后参与溢油应急和清理工作的工人的健康影响,并需要对可能接触化学分散剂的情况进行估计。使用 AIHA IHMOD2.0© 中的两种数学建模工具以及分散剂的化学和物理特性,对 COREXIT™ EC9500A 的挥发性成分(石油馏分、加氢轻质馏分和丙二醇(PG))和 COREXIT™ EC9527A 的成分(2-丁氧基乙醇(2-BE)和 PG)进行了暴露估计。蒙特卡罗模拟用于反映输入参数的不确定性,对于室内和室外活动,分别使用两个盒式、恒排放模型和近场和中场羽流模型。考虑了各种蒸发率、分散剂池的大小、风速和通风率等可能的暴露场景。对于两个盒式模型,2-BE 的近场估计暴露平均值范围为 0.9 至 5.7 ppm,而远场估计暴露平均值范围为 0.3 至 3.5 ppm。在距离源 2.5 英尺处,近场羽流模型暴露的估计平均值范围为 0.01 至 3.7 ppm,而在距离源 10 英尺处,暴露的估计值<0.01 至 0.3 ppm。PG 的估计暴露量约为 2-BE 计算暴露量的 10%,而石油馏分的暴露量比 2-BE 估计值高出约 40%。结果表明,与当前职业接触限值相比,在我们的研究中,石油馏分和 PG 的过度暴露可能没有发生,但在某些条件下,短时间内,2-BE 的暴露可能超过了峰值暴露限值。这些估计值是为了在 GuLF STUDY 中使用作业暴露矩阵来估计接触分散剂蒸气的工人的暴露情况而开发的。