Long‐term evaluation of hydrocarbon degradation rates within the source zone under natural and enhanced attenuation for site closure purposes

M. R. Schneider, A.C.C. Bortolassi, Adriana Ururahy Soriano, M. P. M. Baessa, Marcio Luis Busi da Silva, A.J. Giachini
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Abstract

Despite addressing the cleanup of petroleum hydrocarbon contamination plumes in groundwater, challenges with site closure persist due to the ongoing long‐term contaminant release from source zones. Thus, source zone monitoring even in the presence of residual light nonaqueous‐phase liquid (LNAPL) is mandated by many countries' regulatory agencies before site closure. In this study, four independent controlled‐release sites, each containing a particular fraction of ethanol in gasoline, that is, 10%, 24%, 25%, and 85% (v/v), were subjected to monitored natural attenuation (MNA) alone (E24 and E85), and with nitrate (E25) and sulfate (E10) biostimulation at the vicinity of the source zone. To the best of the authors' knowledge, this is the longest controlled gasohol release monitoring study performed to date at the source zone for site closure (nearly 18 years of monitoring). Both natural source zone depletion and biostimulation were found to reduce benzene concentrations to acceptable remediation target levels according to environmental regulatory councils. Benzene biodegradation rates (λs) were one order of magnitude higher than those reported in the literature for diluted concentrations in groundwater plumes. The decay rate of benzene varied between 0.45 and 1.75/year and was strongly influenced by the mass of ethanol. Compared to biostimulation with nitrate (half‐life of 1.52 years), MNA alone resulted in faster benzene removal rates (half‐life of 0.96 years). Anaerobic biostimulation with sulfate had negligible effects on benzene, toluene, ethylbenzene, and xylene (o‐, m‐, and p‐xylene [BTEX]) biodegradation compared to natural attenuation alone. The highest ethanol concentration (E85) led to faster benzene removal (with a half‐life of 0.40 years), which was even higher than MNA under lower ethanol concentrations (E24). Benzene half‐life was 2.2‐fold slower in the site with the lowest ethanol (E10) compared to E85, indicating that the negative effects of ethanol on BTEX biodegradation appeared to be short‐lived and may need to be re‐evaluated over the long term. Benzene decay rates were approximately six times slower in the source zone than the rates obtained for groundwater plumes, emphasizing the importance of targeting the LNAPL after plume retreat. The study's findings can assist practitioners in better predicting the lines of evidence for BTEX bioremediation and remediation cleanup times at a lower cost in the presence of ethanol, as well as providing guidance for determining whether biostimulation is necessary to expedite source zone remediation for site closure.
在自然衰减和强化衰减的情况下,对源区内的碳氢化合物降解率进行长期评估,以达到关闭场址的目的
尽管对地下水中的石油碳氢化合物污染羽流进行了清理,但由于源区污染物的长期释放,场地关闭仍面临挑战。因此,许多国家的监管机构都规定,即使存在残留的轻质非水相液体 (LNAPL),也必须在场地关闭前对源区进行监测。在这项研究中,对四个独立的受控释放场地(每个场地都含有汽油中特定比例的乙醇,即 10%、24%、25% 和 85% (v/v))进行了单独的监测自然衰减 (MNA)(E24 和 E85),并在源区附近进行了硝酸盐 (E25) 和硫酸盐 (E10) 生物刺激。据作者所知,这是迄今为止在污染源区进行的时间最长的受控汽油释放监测研究,目的是关闭污染源(监测时间将近 18 年)。研究发现,源区的自然耗竭和生物刺激都能将苯浓度降低到环境监管委员会可接受的修复目标水平。苯的生物降解率 (λs) 比文献报道的地下水羽流中稀释浓度的生物降解率高一个数量级。苯的衰减率介于 0.45 和 1.75/ 年之间,受乙醇质量的影响很大。与使用硝酸盐(半衰期为 1.52 年)进行生物刺激相比,仅使用 MNA 的苯去除率更快(半衰期为 0.96 年)。与单独的自然衰减相比,硫酸盐厌氧生物刺激对苯、甲苯、乙苯和二甲苯(邻二甲苯、间二甲苯和对二甲苯 [BTEX])生物降解的影响微乎其微。乙醇浓度最高(E85)时,苯的去除速度更快(半衰期为 0.40 年),甚至高于乙醇浓度较低(E24)时的 MNA。在乙醇浓度最低(E10)的地点,苯的半衰期比 E85 慢 2.2 倍,这表明乙醇对 BTEX 生物降解的负面影响似乎是短暂的,可能需要长期重新评估。苯在源区的衰减率比地下水羽流的衰减率慢约六倍,这强调了在羽流消退后以 LNAPL 为目标的重要性。研究结果可以帮助从业人员更好地预测 BTEX 生物修复的证据线,以及在存在乙醇的情况下以较低成本进行修复清理的时间,并为确定是否有必要进行生物刺激以加快源区修复从而关闭场地提供指导。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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