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景观土壤中N-亚硝基二甲胺(NDMA)的降解

Degradation of N-nitrosodimethylamine (NDMA) in landscape soils.

作者信息

Yang W C, Gan J, Liu W P, Green R

机构信息

Department of Environmental Sciences, University of California, Riverside, CA 92521, USA.

出版信息

J Environ Qual. 2005 Jan-Feb;34(1):336-41. doi: 10.2134/jeq2005.0336.

Abstract

N-nitrosodimethylamine (NDMA), a potential carcinogen, was commonly found in treated wastewater as a by-product of chlorination. As treated water is increasingly used for landscape irrigation, there is an imperative need to understand the leaching risk for NDMA in landscape soils. In this study, adsorption and incubation experiments were conducted using landscape soils planted with turfgrass, ground cover, and trees. Adsorption of NDMA was negligibly weak (K(d) < 1) in all soils, indicating that NDMA has a high potential for moving with percolating water in these soils. Degradation of NDMA occurred at different rates among these soils. At 21 degrees C, the half-life (t(1/2)) of NDMA was 4.1 d for the ground cover soil, 5.6 d for the turfgrass soil, and 22.5 d for the tree soil. The persistence was substantially prolonged after autoclaving or when incubated at 10 degrees C. The rate of degradation was not significantly affected by the initial NDMA concentration or addition of organic and inorganic nutrient sources. The relative persistence was inversely correlated with soil organic matter content, soil microbial biomass, and soil dehydrogenase activity, suggesting the importance of microorganisms in NDMA degradation in these soils. These results suggest that the behavior of NDMA depends closely on the vegetation cover in a landscape system, and prolonged persistence and increased leaching may be expected in soils with sparse vegetation due to low organic matter content and limited microbial activity.

摘要

N-亚硝基二甲胺(NDMA)是一种潜在致癌物,通常作为氯化副产物存在于经处理的废水中。随着经处理的水越来越多地用于景观灌溉,迫切需要了解景观土壤中NDMA的淋溶风险。在本研究中,使用种植了草坪草、地被植物和树木的景观土壤进行了吸附和培养实验。在所有土壤中,NDMA的吸附作用都非常微弱(分配系数K(d) < 1),这表明NDMA在这些土壤中很有可能随渗漏水移动。NDMA在这些土壤中的降解速率各不相同。在21摄氏度下,地被植物土壤中NDMA的半衰期(t(1/2))为4.1天,草坪草土壤中为5.6天,树木土壤中为22.5天。经过高压灭菌或在10摄氏度下培养后,其持久性显著延长。降解速率不受初始NDMA浓度或有机和无机养分添加的显著影响。相对持久性与土壤有机质含量、土壤微生物生物量和土壤脱氢酶活性呈负相关,这表明微生物在这些土壤中NDMA降解过程中起着重要作用。这些结果表明,NDMA的行为在景观系统中与植被覆盖密切相关,由于有机质含量低和微生物活动有限,植被稀疏的土壤中可能会出现持久性延长和淋溶增加的情况。

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