三油酸酯-半渗透膜采样装置对有机氯农药的富集作用

在实验室流水条件下研究了林丹、艾氏剂、环氧七氯、4 ,4′ 滴滴涕及六氯苯在三油酸酯 半渗透膜采样器 (SP MDs)中的富集。所研究的 5种有机氯农药在SPMDs中富集迅速 ,动力学过程可以用线性关系描述 ,2 0d后富集系数达到 15 0 0— 180 0 0。当暴露于接近天然水体浓度时 (2 μg/L) ,富集量能够达到对生物标记物研究制样量的要求 ,富集量大小顺序为六氯苯 >4 ,4’ 滴滴涕 >七氯环氧 >艾氏剂 >林丹 ,与有机氯化合物的脂 /水分配系数成正相关。初步研究结果表明SPMDs可以用来作为生物标记物测试的样品前处理手段 ,或替代水体生物进行微量或痕量有毒有机污染物的生物毒性监测。     

Modeling of DNAPL-Dissolution, Rate-Limited Sorption and Biodegradation Reactions in Groundwater Systems

This article presents an approach for modeling the dissolution process of single component dense non-aqueous phase liquids (DNAPL), such as tetrachloroethene and trichloroethene, in a biologically reactive porous medium. In the proposed approach, the overall transport processes are conceptualized as three distinct reactions. Firstly, the dissolution (or dissolving) process of a residual DNAPL source zone is conceptualized as a mass-transfer limited reaction. Secondly, the contaminants dissolved from the DNAPL source are allowed to partition between sediment and water phases through a rate-limited sorption reaction. Finally, the contaminants in the solid and liquid phases are allowed to degrade by a set of kinetic-limited biological reactions. Although all of these three reaction processes have been researched in the past, little progress has been made towards understanding the combined effects of these processes. This work provides a rigorous mathematical model for describing the coupled effects of these three fundamental reactive transport mechanisms. The model equations are then solved using the general-purpose reactive transport code RT3D (Clement, 1997).     

Biotransformation of Trichloroethylene Using Butane-Oxidizing Bacteria

Mixed butane-utilizing cultures were obtained through sequential batch enrichment under 6% (vol/vol) butane in air using one sediment and four different soil samples with varying histories of contamination as inocula. Subsamples of each environmental sample were subjected to one of three pretreatments prior to inoculation: saturation with 30% ethanol, a 15-min exposure to 60°C, or no treatment. Thirteen of the 14 mixed cultures that were obtained appeared to cometabolize trichloroethylene (TCE) while growing at the expense of butane. All 13 caused a loss of at least one-third of TCE from initial aqueous levels between 4 and 25?µg/ml during 6 days of growth on butane provided at initial aqueous concentrations between 90 and 160?µg/ml. Two cultures cometabolized essentially all the available TCE during this test. One culture, which was obtained from an ethanol-pretreated inoculum, vigorously consumed butane while leaving TCE levels essentially unchanged. However, two other mixed cultures originally derived from the same environmental sample as the ineffective culture were moderately active in TCE cometabolism. Thus, TCE-cometabolizing butane oxidizers appeared to be present in all five of the environmental samples used in these studies.     

Comparison of Soil VOCs measured by soil gas,heated headspace,and methanol extraction techniques

Comparisons of soil volatile organic compound (VOC) measurement techniques and soil properties expected to influence these measurements were performed at two dissimilar sites. A total of 41 soil gas, 52 heated headspace, and 51 methanol extraction/purge‐and‐trap measurements were obtained on collocated samples. Contaminants present at both sites included cis‐1,2‐dichloroethene, 1, 1, 1‐trichloroethane, trichloroethene, and tetrachloroethene. Heated headspace offered the highest sensitivity, as indicated by the greatest percentage of detections per number of analyses. The statistical regression between headspace concentrations and methanol extraction concentrations was highly significant (p < 0.001) with r² = 0.53. Headspace concentrations (range, 7 to 4250 ng/g) ran approximately 20 to 30% of the methanol extraction concentrations (range, 260 to 7300 ng/g), indicating that the methanol was able to extract significantly more of the chlorinated hydrocarbons (CHCs) than the headspace extraction, even in soils with relatively low organic carbon contents (< 0.25%). None of the soil properties (gravimetric moisture content, organic carbon content, percent sand, and percent clay) significantly improved the regression fit. The soil gas responses were unlike either headspace or methanol extraction data. CHC measurements by vapor extraction/soil gas could not be used to predict soil CHC concentrations at these sites.     

Biological decomposition of dichloromethane from a chemical process effluent

The application of specialized microorganisms to treat dichloromethane (DM) containing process effluents was studied. An aerobic fluidized bed reactor with a working volume of 801 filled with sand particles as carriers for the bacteria was used. Oxygen was introduced into the recycle stream by an injector device. DM was monitored semi-continuously. A processor controlled the feed volume according to the DM effluent concentration. Mineralization rates of 12 kg DM/m_bioreactor ³ · d were reached within about three weeks using synthetic wastewater containing 2000 mg/l DM as single carbon compound. DM from process water of a pharmaceutical plant was reduced from about 2000 mg/l in the feed to below 1 mg/l in the effluent at volumetric loading rates of 3 to 4 kg DM/m_bioreactor ³ · d. Degradation of wastewater components like acetone and isopropanol were favoured, thus making the process less attractive for waste streams containing high amounts of DOC other than of DM. DM concentrations of up to 1000 mg/l were tolerated by the immobilized microorganisms and did not influence their DM degradation capacity. The ability to mineralize DM was lost when no DM was fed to the reactor for 10 days.     

Time Varying Optimization for Monitoring Multiple Contaminants under Uncertain Hydrogeology

This study presents a method for identifying cost effective sampling designs for long-term monitoring of remediation of groundwater over multiple monitoring periods under uncertain flow conditions. A contaminant transport model is used to simulate plume migration under many equally likely stochastic hydraulic conductivity fields and provides representative samples of contaminant concentrations. Monitoring costs are minimized under a constraint to meet an acceptable level of error in the estimation of total mass for multiple contaminants simultaneously over many equiprobable realizations of hydraulic conductivity field. A new myopic heuristic algorithm (MS-ER) that combines a new error-reducing search neighborhood is developed to solve the optimization problem. A simulated annealing algorithm using the error-reducing neighborhood (SA-ER) and a genetic algorithm (GA) are also considered for solving the optimization problem. The method is applied to a hypothetical aquifer where enhanced anaerobic bioremediation of four toxic chlorinated ethene species is modeled using a complex contaminant transport model. The MS-ER algorithm consistently performed better in multiple trials of each algorithm when compared to SA-ER and GA. The best design of MS-ER algorithm produced a savings of nearly 25% in project cost over a conservative sampling plan that uses all possible locations and samples.     

Toxicity Assessment of Volatile Organic Compounds in Poplar Trees

A method is described to assess the toxicity of selected volatile organic compounds (VOCs) in poplar trees. The method is illustrated for a specific aqueous mixture of VOCs that contaminates the groundwater at a site for which phytoremediation was being considered. The VOC mixture contained a variety of aromatic compounds, chlorinated aliphatics, and alcohols. Poplar tree cuttings planted in 50-gallon barrels in the greenhouse were watered via subirrigation. The subirrigant contained either a low (42 mg/L), medium (85 mg/L), or high (169 mg/L) dose of the VOC mixture, or water only (experimental control). Phytotoxicity was evaluated by measuring the physiological parameters of stomatal conductance, shoot elongation, and biomass production. Two experiments are briefly described: (1) The poplar tree cuttings were allowed to become established in the barrels and then treated to gradually increasing concentrations of the VOC mixture until the final dose was reached. The objective was to establish a detailed dose-response relationship. (2) The poplar tree cuttings were given the low, medium, or high dose of the VOC mixture immediately after planting. The aim of this experiment was to determine if the VOC mixture would be inhibitory to root development. Phytotoxic effects were not observed in either experiment.     

Estimates of Gibbs free energies of formation of chlorinated aliphatic compounds

The Gibbs free energy of formation of chlorinated aliphatic compounds was estimated with Mavrovouniotis' group contribution method. The group contribution of chlorine was estimated from the scarce data available on chlorinated aliphatics in the literature, and found to vary somewhat according to the position of chlorine in the molecule. The resulting estimates of the Gibbs free energy of formation of chlorinated aliphatic compounds indicate that both reductive dechlorination and aerobic mineralization of these compounds can yield sufficient energy to sustain microbial growth.     

Reaction of the soil microflora after contamination with chlorinated aromatic compounds and HCH

Abstract The effect of the pollution of an industrial land site with chlorinated benzenes, chlorinated phenols, hexachlorocyclohexane-isomers (HCH) on the soil microflora was investigated. Cell counts (microscopic and by plate count) as well as respiration rated did not correlate negatively with the concentration of the contaminants. Soil microorganisms grew in the presence of up to 750 μmol 1⁻¹ pf chlorinated compounds in liquid culture. Only 150 μmol l⁻¹ 2,4,5-trichlorophenol (2,4,5-TCP) inhibited growth totally. In enrichment cultures, bacteria used α- and γ-HCH, 3-chlorophenol (3-CP), 2,3-dichlorophenol (2,3-DCP), 2,6-DCP, 2,4,5-TCP, and 1,2,4,5-tetrachlorobenzene (1,2,4,5-TeCB) as a sole source of carbon and energy under aerobic conditions. No growth was observed with β-HCH. Under anaerobic conditions no growth was observed with any of the substances tested