Department of Civil and Environmental Engineering, Northwestern University, Evanston, IL 60208, USA.
Department of Earth and Planetary Sciences, Northwestern University, Evanston, IL 60208, USA.
J Contam Hydrol. 2024 May;264:104338. doi: 10.1016/j.jconhyd.2024.104338. Epub 2024 Apr 10.
Performance evaluation of in situ bioremediation processes in the field is difficult due to uncertainty created by matrix and contaminant heterogeneity, inaccessibility to direct observation, expense of sampling, and limitations of some measurements. The goal of this research was to develop a strategy for evaluating in situ bioremediation of light nonaqueous-phase liquid (LNAPL) contamination and demonstrating the occurrence of bioenhanced LNAPL dissolution by: (1) integrating a suite of analyses into a rational evaluation strategy; and (2) demonstrating the strategy's application in intermediate-scale flow-cell (ISFC) experiments simulating an aquifer contaminated with a pool of LNAPL (naphthalene dissolved in dodecane). Two ISFCs were operated to evaluate how the monitored parameters changed between a "no bioremediation" scenario and an "intrinsic in situ bioremediation" scenario. Key was incorporating different measures of microbial activity and contaminant degradation relevant to bioremediation: contaminant loss; consumption of electron acceptors; and changes in total alkalinity, pH, dissolved total inorganic carbon, carbon-stable isotopes, microorganisms, and intermediate metabolites. These measurements were integrated via mass-flux modeling and mass-balance analyses to document that in situ biodegradation of naphthalene was strongly accelerated in the "intrinsic in situ bioremediation" scenario versus "no bioremediation." Furthermore, the integrated strategy provided consistent evidence of bioenhancement of LNAPL dissolution through intrinsic bioremediation by a factor of approximately 2 due to the biodegradation of the naphthalene near the pool/water interface.
由于基质和污染物异质性、直接观察的不可及性、采样费用以及某些测量的局限性所带来的不确定性,现场原位生物修复过程的性能评估较为困难。本研究的目的是开发一种用于评估轻非水相液体(LNAPL)污染的原位生物修复的策略,并通过以下方式证明生物增强 LNAPL 溶解的发生:(1)将一系列分析整合到一个合理的评估策略中;(2)通过模拟含水层中 LNAPL 池(溶于十二烷的萘)污染的中间规模流动池(ISFC)实验证明该策略的应用。运行了两个 ISFC 来评估在“无生物修复”情景和“原位生物修复”情景之间监测参数如何变化。关键是要结合与生物修复相关的微生物活性和污染物降解的不同测量方法:污染物损失;电子受体的消耗;总碱度、pH 值、溶解总无机碳、碳稳定同位素、微生物和中间代谢物的变化。通过质量通量模型和质量平衡分析对这些测量值进行整合,以证明与“无生物修复”相比,“原位生物修复”中萘的原位生物降解得到了极大的加速。此外,综合策略通过原位生物降解提供了 LNAPL 溶解的生物增强的一致证据,其增强倍数约为 2,这是由于靠近池/水界面处萘的生物降解所致。