Department of Civil and Environmental Engineering, University of Washington , 201 More Hall, Seattle, Washington 98195-2700, United States.
Environ Sci Technol. 2013 Sep 17;47(18):10356-63. doi: 10.1021/es401729c. Epub 2013 Sep 4.
The leaching of RDX (hexahydro-1,3,5-trinitro-1,3,5-triazine) from particulates deposited in live-fire military training range soils contributes to significant pollution of groundwater. In situ microbial degradation has been proposed as a viable method for onsite containment of RDX. However, there is only a single report of RDX degradation in training range soils and the soil microbial communities involved in RDX degradation were not identified. Here we demonstrate aerobic RDX degradation in soils taken from a target area of an Eglin Air Force Base bombing range, C52N Cat's Eye, (Eglin, Florida U.S.A.). RDX-degradation activity was spatially heterogeneous (found in less than 30% of initial target area field samples) and dependent upon the addition of exogenous carbon sources to the soils. Therefore, biostimulation (with exogenous carbon sources) and bioaugmentation may be necessary to sustain timely and effective in situ microbial biodegradation of RDX. High sensitivity stable isotope probing analysis of extracted soils incubated with fully labeled (15)N-RDX revealed several organisms with (15)N-labeled DNA during RDX-degradation, including xplA-bearing organisms. Rhodococcus was the most prominent genus in the RDX-degrading soil slurries and was completely labeled with (15)N-nitrogen from the RDX. Rhodococcus and Williamsia species isolated from these soils were capable of using RDX as a sole nitrogen source and possessed the genes xplB and xplA associated with RDX-degradation, indicating these genes may be suitable genetic biomarkers for assessing RDX degradation potential in soils. Other highly labeled species were primarily Proteobacteria, including: Mesorhizobium sp., Variovorax sp., and Rhizobium sp.
从实弹军事训练场地土壤中沉积的颗粒中浸出的 RDX(六氢-1,3,5-三硝基-1,3,5-三嗪)是地下水受到严重污染的原因之一。原位微生物降解已被提议作为 RDX 现场封存的可行方法。然而,只有一份关于训练场地土壤中 RDX 降解的报告,并且尚未确定参与 RDX 降解的土壤微生物群落。在这里,我们证明了来自埃格林空军基地轰炸场目标区域(佛罗里达州埃格林美国)的土壤中的有氧 RDX 降解。RDX 降解活性具有空间异质性(在初始目标区域现场样本中发现不到 30%),并且取决于向土壤中添加外源碳源。因此,生物刺激(外加外源碳源)和生物增强可能是维持 RDX 及时有效原位微生物生物降解所必需的。用完全标记的(15)N-RDX 孵育提取的土壤的高灵敏度稳定同位素探测分析在 RDX 降解过程中揭示了一些带有(15)N 标记 DNA 的生物体,包括带有 xplA 的生物体。红球菌是 RDX 降解土壤泥浆中最突出的属,并且完全用 RDX 中的(15)N 氮标记。从这些土壤中分离出的 Rhodococcus 和 Williamsia 物种能够将 RDX 用作唯一氮源,并具有与 RDX 降解相关的 xplB 和 xplA 基因,这表明这些基因可能是评估土壤中 RDX 降解潜力的合适遗传生物标志物。其他高度标记的物种主要是变形菌门,包括:Mesorhizobium sp.、Variovorax sp. 和 Rhizobium sp.。