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Treatment of RDX using down-flow constructed wetland mesocosms

机译:使用向下流动的湿地中膜处理RDX

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Runoff of organic and inorganic contaminants from live firing ranges is a challenging issue because of the extensive size,the variable nature of runoff,the random occurrence of surface contamination,and general inaccessibility.This is particularly true with energetic compounds such as hexahydro-l,3,5-trinitro-l,3,5-triazine (RDX).One potentially promising technology for addressing runoff in a passive,sustainable,and low-cost manner is the use of constructed wetlands to intercept flow.This research effort investigated the ability of down-flow constructed wetlands to remediate RDX-contaminated water at varying loading rates over a period of 2 years.The impact of competing electron acceptors (NO3" and SO42"),the role of plants in the remediation process,and the production of initial daughter products were determined.Significant RDX removal occurred (89-96%) for all loading rates (160-1600 mg/(m2 day)) at a hydraulic retention time of approximately 2 days.RDX degradation occurred in both NO_3~-and SO_4~(2-) dominated electron acceptor zones.RDX and NO_3~-degradation rate constants (k_(RDX) and R_(NO_3~-)) were also determined using a 1D transport model with dispersion.K_(RDX) declined with the increase of influent RDX (6.2-0.8 d~(_1) for planted mesocosms).Changes in degradation rates may be the result of changing bioavailability of carbon released by the peat moss.k_(NO_3~-) followed similar trends but was relatively greater than k_(RDX).Removal of plants is believed to have a small impact on overall RDX removal.RDX concentration in plant tissue was found to be semi-logarithmically related to RDX concentration in the rhizosphere.MNX,DNX,and TNX were observed as transient products generally proportional to RDX loading and low concentrations of MNX and DNX were detected in plant tissue at high RDX loading rates.Cessation of RDX exposure substantially reduced RDX concentrations plants over 6 weeks.These results support the use of constructed wetlands for the remediation of low-level RDX-contaminated water.
机译:活的燃烧范围内的有机和无机污染物的径流是一个具有挑战性的问题,因为径流范围大,径流的性质可变,表面污染的随机发生以及普遍难以接近。对于高能化合物(例如六氢铀, 3,5-trinitro-1,3,5-triazine(RDX)。一种以被动,可持续和低成本的方式解决径流的潜在有前途的技术是使用人工湿地来拦截水流。向下流动的人工湿地在2年内以不同的负荷率修复RDX污染水的能力。竞争性电子受体(NO3“和SO42”)的影响,植物在修复过程中的作用以及生产确定了最初的子产物的数量。在所有水负荷率(160-1600 mg /(m2·天))下,在大约2天的水力停留时间,RDX的去除率显着(89-96%)。以O_3〜和SO_4〜(2-)为主的电子受体区域,还使用一维带分散的传输模型确定了RDX和NO_3〜降解速率常数(k_(RDX)和R_(NO_3〜-))。 )随着进水RDX的增加而下降(种植的中观为6.2-0.8 d〜(_1))。降解率的变化可能是泥炭藓释放的碳的生物利用度变化的结果。据认为去除植物对整体RDX去除的影响很小。发现植物组织中RDX浓度与根际中RDX浓度呈半对数关系.MNX,DNX和观察到TNX是通常与RDX负载成比例的瞬态产物,并且在高RDX负载率下在植物组织中检测到低浓度的MNX和DNX。停止RDX暴露在6周内显着降低了RDX浓度,这些结果支持使用人工湿地用于补救o f低级RDX污染的水。

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