Crocker Fiona H, Indest Karl J, Jung Carina M, Hancock Dawn E, Fuller Mark E, Hatzinger Paul B, Vainberg Simon, Istok Jonathan D, Wilson Edward, Michalsen Mandy M
U.S. Army Engineer Research and Development Center, 3909 Halls Ferry Road, Vicksburg, MS, 39180, USA.
CB&I Federal Services, 17 Princess Road, Lawrenceville, NJ, 08648, USA.
Biodegradation. 2015 Nov;26(6):443-51. doi: 10.1007/s10532-015-9746-1. Epub 2015 Oct 5.
In situ bioaugmentation with aerobic hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX)-degrading bacteria is being considered for treatment of explosives-contaminated groundwater at Umatilla Chemical Depot, Oregon (UMCD). Two forced-gradient bacterial transport tests of site groundwater containing chloride or bromide tracer and either a mixed culture of Gordonia sp. KTR9 (xplA (+)Km(R)), Rhodococcus jostii RHA1 (pGKT2 transconjugant; xplA (+)Km(R)) and Pseudomonas fluorescens I-C (xenB (+)), or a single culture of Gordonia sp. KTR9 (xplA (+); i.e. wild-type) were conducted at UMCD. Groundwater monitoring evaluated cell viability and migration in the injection well and downgradient monitoring wells. Enhanced degradation of RDX was not evaluated in these demonstrations. Quantitative PCR analysis of xplA, the kanamycin resistance gene (aph), and xenB indicated that the mixed culture was transported at least 3 m within 2 h of injection. During a subsequent field injection of bioaugmented groundwater, strain KTR9 (wild-type) migrated up to 23-m downgradient of the injection well within 3 days. Thus, the three RDX-degrading strains were effectively introduced and transported within the UMCD aquifer. This demonstration represents an innovative application of bioaugmentation to potentially enhance RDX biodegradation in aerobic aquifers.
俄勒冈州尤马蒂拉化学武器库(UMCD)正在考虑采用原位生物强化技术,利用好氧降解六氢-1,3,5-三硝基-1,3,5-三嗪(RDX)的细菌来处理受炸药污染的地下水。进行了两项强制梯度细菌运移试验,试验对象为含有氯化物或溴化物示踪剂的场地地下水,以及戈氏菌属KTR9(xplA(+)Km(R))、约氏红球菌RHA1(pGKT2接合子;xplA(+)Km(R))和荧光假单胞菌I-C(xenB(+))的混合培养物,或者戈氏菌属KTR9的单一培养物(xplA(+);即野生型)。地下水监测评估了注入井和下游监测井中的细胞活力和迁移情况。在这些试验中未评估RDX的强化降解情况。对xplA、卡那霉素抗性基因(aph)和xenB进行的定量PCR分析表明,混合培养物在注入后2小时内至少迁移了3米。在随后一次生物强化地下水的现场注入过程中,菌株KTR9(野生型)在3天内迁移到了注入井下游23米处。因此,这三种降解RDX的菌株被有效地引入并在UMCD含水层中运移。该试验代表了生物强化技术在潜在增强好氧含水层中RDX生物降解方面的创新性应用。