Papadopoulos Apostolos, Paton Graeme I, Reid Brian J, Semple Kirk T
Department of Environmental Science, Faculty of Science and Technology, Lancaster University, Lancaster, UK LA1 4YQ.
J Environ Monit. 2007 Jun;9(6):516-22. doi: 10.1039/b700720e. Epub 2007 May 11.
Biodegradation has been identified as a major loss process for organic contaminants in soils and, as a result, microbial strategies have been developed for the remediation of contaminated land. Prediction of the biodegradable fraction would be important for determining bioremediation end-points in the clean-up of contaminated land. The aim of this study was to investigate the ability of a cyclodextrin extraction to predict the extent to which polycyclic aromatic hydrocarbons (PAHs) would be degraded microbiologically in field contaminated soils; further testing the robustness and reproducibility of this extraction in chemically complex systems. Dichloromethane and hydroxypropyl-beta-cyclodextrin (HPCD) extractable fractions were measured together with the PAH biodegradable fraction in each of the six field contaminated soils. The amounts of PAHs degraded by the catabolic activity of the indigenous microflora in each of the soils were correlated with HPCD-extractable PAH concentrations. The regressions showed that the amounts of lower molecular weight PAHs extracted by the HPCD were not significantly (P > 0.05) different to the amounts that were degraded. However, higher molecular weight PAHs that were extracted by HPCD did differ significantly (P < 0.05) from the amounts degraded. Although the HPCD extraction did overestimate the microbially degradable fraction of the higher molecular weight PAHs, overall the correlations between the HPCD extractable fraction and the microbially degradable fraction were very close, with mean values of the slope of line for the six soils equalling 1. This study further describes the robust and reproducible nature of the aqueous-based soil extraction technique reliably measuring the extent to which PAHs will be microbially degraded in soil.
生物降解已被确定为土壤中有机污染物的主要损失过程,因此,已开发出微生物策略用于污染土地的修复。预测可生物降解部分对于确定污染土地清理中的生物修复终点非常重要。本研究的目的是调查环糊精萃取预测多环芳烃(PAHs)在现场污染土壤中微生物降解程度的能力;进一步测试这种萃取在化学复杂系统中的稳健性和可重复性。在六种现场污染土壤中,分别测量了二氯甲烷和羟丙基-β-环糊精(HPCD)可萃取部分以及PAH可生物降解部分。每种土壤中本地微生物群落的分解代谢活性降解的PAHs量与HPCD可萃取的PAH浓度相关。回归分析表明,HPCD萃取的低分子量PAHs量与降解量没有显著差异(P>0.05)。然而,HPCD萃取的高分子量PAHs量与降解量有显著差异(P<0.05)。尽管HPCD萃取确实高估了高分子量PAHs的微生物可降解部分,但总体而言,HPCD可萃取部分与微生物可降解部分之间的相关性非常密切,六种土壤的直线斜率平均值等于1。本研究进一步描述了基于水的土壤萃取技术可靠测量PAHs在土壤中微生物降解程度的稳健性和可重复性。