Department of Chemical, Mining and Environmental Engineering, University of Bologna, Via Terracini 28, 40131 Bologna, Italy.
Bioresour Technol. 2013 Jan;128:479-86. doi: 10.1016/j.biortech.2012.10.026. Epub 2012 Oct 17.
A novel aerobic/anaerobic/aerobic treatment was implemented in batch reactors containing aquifer materials from a site contaminated by tetrachloroethylene (PCE), trichloroethylene (TCE), vinyl chloride (VC), 1,1,2-trichloroethane (1,1,2-TCA) and chloroform (CF). Consortia grown aerobically on methane, propane, n-pentane and n-hexane completely biodegraded the chlorinated solvent mixture, via aerobic cometabolism of VC, CF, TCE and 1,1,2-TCA, followed by PCE reductive dechlorination (RD) to 1,2-cis-dichlorothylene (cis-DCE) or TCE, and cis-DCE/TCE cometabolism in a further aerobic phase. n-Hexane was the best substrate. No electron donor was supplied for RD, which likely utilized cellular material produced during the aerobic phase. Chloride release was stoichiometric with chlorinated solvent biodegradation. According to the Lepidium sativum ecotoxicity test, a decreased toxicity was observed with propane, n-pentane and n-hexane, but not methane. A kinetic study of PCE RD allowed to estimate the PCE maximum specific rate (0.57 ± 0.07 mg mg(protein)(-1) day(-1)) and half-saturation constant (6.7 ± 1.5 mg L(-1)).
采用 novel aerobic/anaerobic/aerobic 处理工艺,在含有受四氯乙烯(PCE)、三氯乙烯(TCE)、氯乙烯(VC)、1,1,2-三氯乙烷(1,1,2-TCA)和氯仿(CF)污染的含水层材料的批量反应器中实施处理。采用甲烷、丙烷、正戊烷和正己烷进行好氧培养的生物群落,通过 VC、CF、TCE 和 1,1,2-TCA 的好氧共代谢,随后进行 PCE 的还原脱氯(RD)生成 1,2-顺式-二氯乙烯(cis-DCE)或 TCE,以及在进一步的好氧阶段进行 cis-DCE/TCE 的共代谢,完全降解了氯代溶剂混合物。正己烷是最好的基质。RD 没有提供电子供体,它可能利用了好氧阶段产生的细胞物质。氯离子的释放与氯化溶剂的生物降解呈化学计量关系。根据蕺菜 ecotoxicity 测试,发现丙烷、正戊烷和正己烷的毒性降低,但甲烷没有。对 PCE RD 的动力学研究允许估计 PCE 的最大比速率(0.57 ± 0.07 mg mg(protein)(-1) day(-1))和半饱和常数(6.7 ± 1.5 mg L(-1))。