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非饱和带中控制DNT生物降解因素的土柱评估

Soil column evaluation of factors controlling biodegradation of DNT in the vadose zone.

作者信息

Fortner John D, Zhang Chunlong, Spain Jim C, Hughes Joseph B

机构信息

Department of Civil and Environmental Engineering, Rice University, 6100 Main Street, Houston, Texas 77005, USA.

出版信息

Environ Sci Technol. 2003 Aug 1;37(15):3382-91. doi: 10.1021/es021066s.

DOI:10.1021/es021066s
PMID:12966985
Abstract

High concentrations of 2,4-dinitrotoluene (2,4-DNT) and 2,6-dinitrotoluene (2,6-DNT) are present in vadose zone soils at many facilities where explosives manufacturing has taken place. Both DNT isomers can be biodegraded under aerobic conditions, but rates of intrinsic biodegradation observed in vadose zone soils are not appreciable. Studies presented herein demonstrate that nutrient limitations control the onset of rapid 2,4-DNT biodegradation in such soils. In column studies conducted at field capacity, high levels of 2,4-DNT biodegradation were rapidly stimulated by the addition of a complete mineral medium but not by bicarbonate-buffered distilled deionized water or by phosphate-amended tap water. Biodegradation of 2,6-DNT was not observed under any conditions. Microcosm studies using a DNT-degrading culture from column effluent suggest that, after the onset of 2,4-DNT degradation, nitrite evolution will eventually control the extent of degradation achieved by two mechanisms. First, high levels of nitrite (40 mM) were found to strongly inhibit 2,4-DNT degradation. Second, nitrite production reduces the solution pH, and at pH levels below 6.0, 2,4-DNT degradation slows rapidly. Under conditions evaluated in laboratory-scale studies, 2,4-DNT biodegradation enhanced the rate of contaminant loss from the vadose zone by a factor of 10 when compared to the washout due to leaching.

摘要

在许多曾经进行过炸药制造的场所,渗流带土壤中存在高浓度的2,4-二硝基甲苯(2,4-DNT)和2,6-二硝基甲苯(2,6-DNT)。两种DNT异构体在有氧条件下均可生物降解,但在渗流带土壤中观察到的固有生物降解速率并不显著。本文所展示的研究表明,养分限制控制了此类土壤中2,4-DNT快速生物降解的起始。在田间持水量下进行的柱实验中,添加完全矿物培养基能迅速刺激高水平的2,4-DNT生物降解,而碳酸氢盐缓冲的去离子蒸馏水或添加磷酸盐的自来水则不能。在任何条件下均未观察到2,6-DNT的生物降解。使用柱流出物中的DNT降解培养物进行的微观实验表明,在2,4-DNT降解开始后,亚硝酸盐生成最终将通过两种机制控制降解程度。首先,发现高水平的亚硝酸盐(40 mM)会强烈抑制2,4-DNT降解。其次,亚硝酸盐的产生会降低溶液pH值,在pH值低于6.0时,2,4-DNT降解迅速减缓。在实验室规模研究评估的条件下,与因淋溶导致的污染物流失相比,2,4-DNT生物降解使渗流带中污染物的流失速率提高了10倍。

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