Olivares Christopher I, Abrell Leif, Khatiwada Raju, Chorover Jon, Sierra-Alvarez Reyes, Field Jim A
Department of Chemical and Environmental Engineering, University of Arizona, P.O. Box 210011, Tucson, AZ 85721, USA.
Department of Soil, Water & Environmental Science, University of Arizona, P.O. Box 210011, Tucson, AZ 85721, USA; Department of Chemistry & Biochemistry, University of Arizona, P.O. Box 210011, Tucson, AZ 85721, USA.
J Hazard Mater. 2016 Mar 5;304:214-21. doi: 10.1016/j.jhazmat.2015.10.059. Epub 2015 Oct 30.
Recent studies have begun to assess the environmental fate and toxicity of 2,4-dinitroanisole (DNAN), an insensitive munition compound of interest to defense agencies. Aerobic and anaerobic DNAN biotransformation in soils was evaluated in this study. Under aerobic conditions, there was little evidence of transformation; most observed removal was attributed to adsorption and subsequent slow chemical reactions. Under anaerobic conditions, DNAN was reductively (bio)transformed and the rate of the transformation was positively correlated with soil organic carbon (OC) up to a threshold of 2.07% OC. H2 addition enhanced the nitroreduction rate compared to endogenous treatments lacking H2. Heat-killed treatments provided rates similar to the endogenous treatment, suggesting that abiotic factors play a role in DNAN reduction. Ten (bio)transformation products were detected by high-resolution mass spectrometry. The proposed transformation pathway involves reduction of DNAN to aromatic amines, with putative reactive nitroso-intermediates coupling with the amines to form azo dimers. Secondary reactions include N-alkyl substitution, O-demethylation (sometimes followed by dehydroxylation), and removal of an N-containing group. Globally, our results suggest that the main reaction DNAN undergoes in anaerobic soils is nitroreduction to 2-methoxy-5-nitroaniline (MENA) and 2,4-diaminoanisole (DAAN), followed by anaerobic coupling reactions yielding azo-dimers. The dimers were subsequently subject to further (bio)transformations.
近期研究已开始评估2,4-二硝基苯甲醚(DNAN)的环境归宿和毒性,DNAN是一种国防机构感兴趣的钝感弹药化合物。本研究评估了土壤中DNAN的好氧和厌氧生物转化。在好氧条件下,几乎没有转化的证据;观察到的大部分去除归因于吸附和随后的缓慢化学反应。在厌氧条件下,DNAN发生还原(生物)转化,转化率与土壤有机碳(OC)呈正相关,直至OC阈值为2.07%。与缺乏氢气的内源处理相比,添加氢气提高了硝基还原速率。热灭活处理的速率与内源处理相似,表明非生物因素在DNAN还原中起作用。通过高分辨率质谱检测到十种(生物)转化产物。提出的转化途径包括将DNAN还原为芳香胺,假定的活性亚硝基中间体与胺偶联形成偶氮二聚体。二级反应包括N-烷基取代、O-去甲基化(有时随后是脱羟基化)和去除含氮基团。在全球范围内,我们的结果表明,DNAN在厌氧土壤中发生的主要反应是硝基还原为2-甲氧基-5-硝基苯胺(MENA)和2,4-二氨基苯甲醚(DAAN),随后发生厌氧偶联反应生成偶氮二聚体。这些二聚体随后进行进一步的(生物)转化。