Zhou Quanlin, McCraven Sally, Garcia Julio, Gasca Monica, Johnson Theodore A, Motzer William E
Earth Sciences Division, Lawrence Berkeley National Laboratory, University of California, One Cyclotron Road, MS90-1116, Berkeley, CA 94720, United States.
Water Res. 2009 Feb;43(3):793-805. doi: 10.1016/j.watres.2008.11.011. Epub 2008 Nov 21.
Biodegradation of N-Nitrosodimethylamine (NDMA) has been found through laboratory incubation in unsaturated and saturated soil samples under both aerobic and anaerobic conditions. However, direct field evidence of in situ biodegradation in groundwater is very limited. This research aimed to evaluate biodegradation of NDMA in a large-scale groundwater system receiving recycled water as incidental and active recharge. NDMA concentrations in 32 monitoring and production wells with different screen intervals were monitored over a period of seven years. Groundwater monitoring was used to characterize changes in the magnitude and extent of NDMA in groundwater in response to seasonal hydrogeologic conditions and, more importantly, to significant concentration variations in effluent from water reclamation plants (associated with treatment-process changes). Extensive monitoring of NDMA concentrations and flow rates at effluent discharge locations and surface-water stations was also conducted to reasonably estimate mass loading through unlined river reaches to underlying groundwater. Monitoring results indicate that significant biodegradation of NDMA occurred in groundwater, accounting for an estimated 90% mass reduction over the seven-year monitoring period. In addition, a discrete effluent-discharge and groundwater-extraction event was extensively monitored in a well-characterized, localized groundwater subsystem for 626 days. Analysis of the associated NDMA fate and transport in the subsystem indicated that an estimated 80% of the recharged mass was biodegraded. The observed field evidence of NDMA biodegradation is supported by groundwater transport modeling accounting for various dilution mechanisms and first-order decay for biodegradation, and by a previous laboratory study on soil samples collected from the study site [Bradley, P.M., Carr, S.A., Baird, R.B., Chapelle, F.H., 2005. Biodegradation of N-Nitrosodimethylamine in soil from a water reclamation facility. Bioremediat. J. 9 (2), 115-120.].
通过在有氧和厌氧条件下对不饱和及饱和土壤样品进行实验室培养,已发现N-亚硝基二甲胺(NDMA)具有生物降解性。然而,地下水中原位生物降解的直接现场证据非常有限。本研究旨在评估在一个大规模地下水系统中,作为偶然和主动补给水源的再生水对NDMA的生物降解情况。在七年时间里,对32口不同筛管间隔的监测井和生产井中的NDMA浓度进行了监测。利用地下水监测来描述地下水中NDMA的含量和范围随季节性水文地质条件的变化,更重要的是,描述其对水回收厂出水显著浓度变化(与处理工艺变化相关)的响应。还对废水排放地点和地表水监测站的NDMA浓度和流量进行了广泛监测,以合理估算通过无衬砌河段进入下层地下水的质量负荷。监测结果表明,地下水中NDMA发生了显著的生物降解,在七年的监测期内估计质量减少了90%。此外,在一个特征明确的局部地下水子系统中,对一次离散的废水排放和地下水抽取事件进行了为期626天的广泛监测。对子系统中相关的NDMA归宿和运移分析表明,估计80%的补给质量被生物降解。考虑到各种稀释机制和生物降解的一级衰减的地下水运移模型,以及之前对从研究地点采集的土壤样品进行的实验室研究[布拉德利,P.M.,卡尔,S.A.,贝尔德,R.B.,查佩尔,F.H.,2005年。水回收设施土壤中N-亚硝基二甲胺的生物降解。生物修复杂志。9(2),115 - 120。],支持了所观察到的NDMA生物降解的现场证据。