Li Congzhou, Li Binghua, Bi Erping
MOE Key Laboratory of Groundwater Circulation and Environmental Evolution, Beijing Key Laboratory of Water Resources and Environmental Engineering, and School of Water Resources and Environment, China University of Geosciences (Beijing), Beijing 100083, PR China.
Department of Water Resources, Beijing Water Science and Technology Institute, Beijing 100048, PR China.
Sci Total Environ. 2019 Jun 10;668:1030-1037. doi: 10.1016/j.scitotenv.2019.02.375. Epub 2019 Feb 26.
Due to the quality difference between reclaimed water and natural groundwater, managed aquifer recharge (MAR) with reclaimed water may pose environmental risks. A river infiltration of reclaimed water for groundwater recharge in north China has been in operation for over 10 years. To investigate the actual impact on native groundwater under long-term MAR, 10-year monitoring data of recharge water and groundwater were analyzed. Due to the effect of recharge, the hydrochemical type of groundwater rapidly changed from Ca-Mg-HCO into Na-HCO which was the type of recharge water. Cl was used as a conservative tracer in a physical mixing model, and the mixing was concluded to be dominant in the groundwater hydrochemical change under long-term MAR. The hydraulic travel time to the 30 m depth was determined to be about 6.5 months by obtaining the best-fit linear cross correlation between the concentrations of Cl in recharge water and those in groundwater. In application of this method, the monitoring wells should be located downstream and as close as possible to the recharge site (e.g., <50 m). Based on the travel time, behaviors of total nitrogen (TN), NO-N, NO-N, and NH-N were determined by attenuation factor (A). As the main nitrogen compound, NO-N was well attenuated under high hydraulic load, resulting in the A > 1, with an attenuation rate of 99.6%. The A < 1 of NH-N indicated the additional input of NH-N in groundwater. Fluctuations of NH-N in recharge water exceeded 4 mg/L changes sorption equilibrium, resulting in the sorption/desorption of NH-N in soil-groundwater system. The concentration of NH-N in groundwater increased in the later period of monitoring. The overall attenuation rate of NH-N was 26.3%. These findings contributed to improving the environmental benefits of this MAR site and provided guidance for other similar projects.
由于再生水与天然地下水之间存在质量差异,利用再生水进行含水层人工补给(MAR)可能会带来环境风险。中国北方一条用于地下水补给的再生水河流渗滤工程已运行超过10年。为调查长期MAR对原生地下水的实际影响,分析了10年的补给水源水和地下水监测数据。由于补给作用,地下水的水化学类型迅速从Ca-Mg-HCO型转变为补给水源水的Na-HCO型。在物理混合模型中,Cl被用作保守示踪剂,得出在长期MAR作用下,混合作用在地下水水化学变化中占主导地位。通过获取补给水中Cl浓度与地下水中Cl浓度之间的最佳拟合线性互相关,确定到达30米深度的水力运移时间约为6.5个月。在应用该方法时,监测井应位于下游且尽可能靠近补给地点(例如,<50米)。基于运移时间,通过衰减因子(A)确定了总氮(TN)、NO-N、NO-N和NH-N的行为。作为主要的氮化合物,NO-N在高水力负荷下得到了很好的衰减,导致A>1,衰减率为99.6%。NH-N的A<1表明地下水中有NH-N的额外输入。补给水中NH-N的波动超过4mg/L会改变吸附平衡,导致土壤-地下水系统中NH-N的吸附/解吸。监测后期地下水中NH-N的浓度增加。NH-N的总体衰减率为26.3%。这些研究结果有助于提高该MAR场地的环境效益,并为其他类似项目提供指导。