Manzano Manuel A, Perales José A, Sales Diego, Quiroga José M
Department of Chemical Engineering and Environmental Technology, Faculty of Sea and Environmental Sciences, Cádiz University, Polígono Río San Pedro s/n, 11510 Puerto Real, Cádiz, Spain.
Environ Toxicol Chem. 2003 Apr;22(4):699-705.
This article reports the results of various biodegradation experiments on polychlorinated biphenyl (PCB)-contaminated sandy soil employing a mixed culture of acclimatized bacteria. Following the optimization of different variables without chemical pretreatment, the elimination rate achieved of Aroclor 1242 in slurry-phase reactors was 61% after four months of treatment, with the presence of biphenyl as cosubstrate being the most important factor affecting PCB biodegradation. The biodegradation occurred as a first-order process, and it proved most effective in respect to dichlorinated biphenyls (100% removal), followed by trichlorinated (92%) and tetrachlorinated biphenyls (24%). The results also showed that the degradability of PCBs in soil may be enhanced by an advanced oxidation pretreatment (Fenton reaction), producing almost 100% elimination of PCBs at the end of the integrated chemical-biological process and 72% mineralization of the intermediates generated during the chemical pretreatment.
本文报道了使用驯化细菌混合培养物对多氯联苯(PCB)污染砂土进行各种生物降解实验的结果。在未进行化学预处理的情况下对不同变量进行优化后,在浆液相反应器中处理四个月后,Aroclor 1242的去除率达到61%,联苯作为共底物的存在是影响PCB生物降解的最重要因素。生物降解以一级过程发生,对二氯联苯最为有效(去除率100%),其次是三氯联苯(92%)和四氯联苯(24%)。结果还表明,通过高级氧化预处理(芬顿反应)可以提高土壤中PCBs的降解能力,在化学-生物联合过程结束时几乎可以100%去除PCBs,并且化学预处理过程中产生的中间体有72%矿化。