CSIRO Land and Water, Private Bag 5, Wembley, WA 6913, Australia.
Water Res. 2011 Apr;45(8):2550-60. doi: 10.1016/j.watres.2011.02.018. Epub 2011 Feb 19.
The fate of N-nitrosomorpholine (NMOR) was evaluated at microgram and nanogram per litre concentrations. Experiments were undertaken to simulate the passage of groundwater contaminants through a deep anaerobic pyritic aquifer system, as part of a managed aquifer recharge (MAR) strategy. Sorption studies demonstrated the high mobility of NMOR in the Leederville aquifer system, with retardation coefficients between 1.2 and 1.6. Degradation studies from a 351 day column experiment and a 506 day stop-flow column experiment showed an anaerobic biologically induced reductive degradation process which followed first order kinetics. A biological lag-time of less than 3 months and a transient accumulation of morpholine (MOR) were also noted during the degradation. Comparable half-life degradation rates of 40-45 days were observed over three orders of magnitude in concentration (200 ng L(-1) to 650 μg L(-1)). An inhibitory effect on microorganism responsible to the biodegradation of NMOR at 650 μg L(-1) or a threshold effect at 200 ng L(-1) was not observed during these experiments.
在微克和纳克/升浓度下评估了 N-亚硝基吗啉(NMOR)的命运。作为管理含水层补给(MAR)策略的一部分,进行了实验以模拟地下水污染物通过深层厌氧硫铁矿含水层系统的运移。吸附研究表明 NMOR 在利德维尔含水层系统中具有很高的迁移性,阻滞系数在 1.2 到 1.6 之间。来自 351 天柱实验和 506 天停流柱实验的降解研究表明,存在一种遵循一级动力学的厌氧生物诱导还原降解过程。在降解过程中还注意到生物滞后时间小于 3 个月和 morpholine(MOR)的瞬时积累。在浓度为三个数量级(200ng/L 至 650μg/L)的范围内,观察到可比的半衰期降解率为 40-45 天。在这些实验中,没有观察到 650μg/L 时对 NMOR 生物降解负责的微生物的抑制作用或 200ng/L 时的阈值效应。