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三硝基甲苯/代谢物在土柱中的迁移性与降解:土壤有机碳含量的影响

Mobility and degradation of trinitrotoluene/metabolites in soil columns: effect of soil organic carbon content.

作者信息

Singh Neera, Hennecke Dieter, Hoerner Jennifer, Koerdel Werner, Schaeffer Andreas

机构信息

Division of Agricultural Chemicals, Indian Agricultural Research Institute, New Delhi, India.

出版信息

J Environ Sci Health A Tox Hazard Subst Environ Eng. 2008 Jun;43(7):682-93. doi: 10.1080/10934520801959823.

Abstract

There has been increasing interest in enhancing natural attenuation of munitions-contaminated soils. Present study reports the effect of increasing soil organic matter content on fate and mobility of trinitrotoluene (TNT) and metabolites in soil columns. This study was performed using 30-cm-long columns containing a top 5 cm of contaminated soil as a source layer and an uncontaminated soil (25 cm) adjusted to 0.5, 1.0, 1.5 and 3.0% organic carbon (OC) content using compost. Contaminated soil layer was fortified with uniformly ring-labeled (14)C-trinitrotoluene (TNT) or 2,4-dinitrotoluene (DNT); in total there were 8 treatments. Columns were leached with synthetic rain water under unsaturated flow conditions in downside up direction. There was significant increase in the retention of both (14)C-TNT and (14)C-DNT in soils with increasing soil OC content and in 3.0% soil OC content column < 1% TNT/DNT was recovered in the leachate. Further, degradation of TNT and metabolites from contaminated soil was significantly increased and resulted in greater soil-bound residues. Formation of monoamino-dinitrotoluene (ADNTs), diamino-mononitrotoluene (DANTs) and monoamino-mononitrotoluene (ANTs) metabolites was greatly enhanced with increase in OC content of soils. Study suggests that increasing OC content of contaminated soil to 3.0% significantly enhanced the reduction of nitroaromatics to more polar amine metabolites and the formation of soil-bound residues.

摘要

人们对增强弹药污染土壤的自然衰减越来越感兴趣。本研究报告了增加土壤有机质含量对三硝基甲苯(TNT)及其代谢产物在土壤柱中的归宿和迁移性的影响。本研究使用30厘米长的土柱进行,土柱顶部5厘米为受污染土壤作为源层,底部25厘米为未受污染土壤,通过添加堆肥将其有机碳(OC)含量调整为0.5%、1.0%、1.5%和3.0%。受污染土壤层用均匀环状标记的(14)C-三硝基甲苯(TNT)或2,4-二硝基甲苯(DNT)强化;总共有8种处理。在不饱和流动条件下,从下向上用合成雨水淋洗土柱。随着土壤OC含量的增加,(14)C-TNT和(14)C-DNT在土壤中的保留量显著增加,在3.0%土壤OC含量的土柱中,淋滤液中回收的TNT/DNT不到1%。此外,受污染土壤中TNT及其代谢产物的降解显著增加,导致土壤结合残留物增加。随着土壤OC含量的增加,单氨基二硝基甲苯(ADNTs)、二氨基单硝基甲苯(DANTs)和单氨基单硝基甲苯(ANTs)代谢产物的形成大大增强。研究表明,将受污染土壤的OC含量提高到3.0%可显著增强硝基芳烃向极性更强的胺类代谢产物的还原以及土壤结合残留物的形成。

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