Department of Environmental and Resource Engineering, Technical University of Denmark, Bygningstorvet, Building 115, 2800 Kgs. Lyngby, Denmark.
Centre for Regional Development, Capital Region of Denmark, Kongens Vænge 2, 3400 Hillerød, Denmark.
J Contam Hydrol. 2024 Nov;267:104421. doi: 10.1016/j.jconhyd.2024.104421. Epub 2024 Sep 6.
Microbial reductive dechlorination is a key process in aquifers contaminated with chlorinated ethenes and results in a net mass reduction of organic pollutants. Biodegradation rates in the subsurface are temperature-dependent and may be enhanced by increased groundwater temperatures. This study explores the potential of combining the temperature increase from low-temperature Aquifer Thermal Energy Storage with In Situ Bioremediation (ATES-ISB). The effects of highly dynamic groundwater flow and heat transport on microbial degradation rates were examined in a contaminated aquifer based on a pilot-scale experiment and a comprehensive process-based modeling analysis. The low-temperature ATES-ISB pilot test was carried out in Birkerød (Denmark), in an aquifer contaminated with trichloroethene by implementing a groundwater flow dipole, injecting heated groundwater, biostimulating the system with lactate and bioaugmenting it with a Dehalococcoides containing culture. Solute concentrations were monitored in four observation wells over the course of the test and a non-isothermal reactive transport model, solved in a two-dimensional heterogeneous domain, was developed to quantitatively interpret the experimental observations. The process-based numerical model also allowed evaluating the evolution of chlorinated ethenes concentrations considering different hydraulic, thermal, and operational scenarios. The results demonstrate the beneficial combination of ATES with in situ contaminant bioremediation, showing enhancement of contaminant mass reduction and more complete reductive dechlorination. The developed process-based model can be instrumental for the design and parameterization of pilot and full scale low-temperature ATES-ISB remediation in shallow aquifer systems.
微生物还原脱氯是受氯代乙烯污染含水层中的一个关键过程,可导致有机污染物的净质量减少。地下水中的生物降解速率取决于温度,并且可能会因地下水温度升高而得到增强。本研究探索了将低温含水层热能储存与原位生物修复(ATES-ISB)相结合的潜力。基于一项试点规模实验和全面的基于过程的建模分析,研究了高度动态的地下水流动和热传递对微生物降解速率的影响。在丹麦比克勒罗德的一个受三氯乙烯污染的含水层中进行了低温 ATES-ISB 试点测试,该测试通过实施地下水流动偶极子、注入加热的地下水、用乳酸对系统进行生物刺激以及用含有 Dehalococcoides 的培养物进行生物增强,来实现。在测试过程中,在四个观测井中监测了溶质浓度,并开发了一个非等温反应性传输模型,在二维非均质域中求解,以定量解释实验观测结果。基于过程的数值模型还允许考虑不同水力、热力和操作方案来评估氯化乙烯浓度的演变。结果表明,ATES 与原位污染物生物修复的有益结合可增强污染物的质量减少和更完全的还原脱氯。所开发的基于过程的模型可用于浅层含水层系统中低温 ATES-ISB 修复的设计和参数化。