Kinetic Modeling for a Novel Permeable Reactive Biobarrier for In Situ Remediation of PAH-Contaminated Groundwater

被引:1
|
作者
Liu, Cuicui [1 ,2 ]
Ma, Yue [2 ]
Banwart, Steven A. [3 ,4 ]
Chen, Xiaohui [2 ]
Du, Wenchao [5 ]
Yin, Ying [1 ]
Guo, Hongyan [1 ]
机构
[1] Nanjing Univ, State Key Lab Pollut Control & Resource Reuse, Sch Environm, Nanjing 210023, Peoples R China
[2] Univ Leeds, Sch Civil Engn, Leeds LS2 9JT, W Yorkshire, England
[3] Univ Leeds, Sch Earth & Environm, Leeds LS2 9JT, W Yorkshire, England
[4] Univ Leeds, Global Food & Environm Inst, Leeds LS2 9JT, W Yorkshire, England
[5] Nanjing Normal Univ, Sch Environm, Nanjing 210023, Peoples R China
基金
国家重点研发计划;
关键词
Phenanthrene; PHREEQC; Kinetics; Permeable reactive barrier; Groundwater remediation; WHEAT-STRAW; BIODEGRADATION; BIOREMEDIATION; PHENANTHRENE; REMOVAL; BARRIER; HYDROCARBON; TRANSPORT; COLUMN; CARBON;
D O I
10.1061/(ASCE)GT.1943-5606.0002779
中图分类号
P5 [地质学];
学科分类号
0709 ; 081803 ;
摘要
Y Permeable reactive barriers (PRBs) are an environmentally friendly and cost-effective in situ remediation technology that have been used to restore polycyclic aromatic hydrocarbon (PAH)-contaminated groundwater. However, the understanding of removal mechanisms of the pollutant from groundwater remains a challenge due to the complex interactions between microbial evolution, organic carbon kinetics, and multiple chemical reactions. In this study, a one-dimensional reactive transport model was developed to study 450-day column experiments for removal of phenanthrene from groundwater using new PRB materials A (including wheat straw) and B (including coconut shell biochar). The modeling results provided a deeper understanding of the removal process for phenanthrene, and showed that Material B had a higher removal efficiency than Material A over 34 days. The removal efficiency of phenanthrene in both Materials A and B was close to 100% in the PRB system. This was because (1) Material B had a higher adsorption capacity for phenanthrene than Material A, and adsorption played an important role in the short term (e.g., 20 days), whereas biodegradation controlled longer-term removal processes; (2) the biomass in Column B was higher (p < 0.05) than that in Column A; and (3) Column B had a higher microbial yield coefficient that could favor longer-term microbial growth and biodegradation activity. Material B might have greater potential than Material A for longer-term remediation performance. The simulated results generally were in agreement with the experimental results and support the development of field-scale pilot testing of these materials for groundwater remediation. (C) 2022 American Society of Civil Engineers.
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页数:9
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