Guerin Turlough F
Telstra Corporation Limited, L33/242 Exhibition Street, Melbourne 3000, Australia.
J Hazard Mater. 2008 Jun 15;154(1-3):9-20. doi: 10.1016/j.jhazmat.2007.09.094. Epub 2007 Sep 29.
Chlorinated benzenes, including chlorobenzene (CB) and 1,2-dichlorobenzene (DCB) are widely used as chemical intermediates and solvents across industry. Soil contaminated with these compounds was treated in a pilot-scale trial in 6 m3 cells. Air was drawn through each cell and exhausted via an activated carbon (GAC) filter system. The trial objective was to stimulate native microflora with nutrients and varying levels of organic amendments (0%, 12% and 35%). Initial soil DCB concentrations varied from <1 to 6 mg/kg in the three cells with an average of 2 mg/kg. Approximately 90% of the DCB mass present in the soil was removed over a period of 2-3 weeks. Up to 100-fold increases in total heterotrophs (THP), CB+ and DCB+ degraders were observed. Residual concentrations of chlorinated benzenes were generally below detection limits (0.2 mg/kg). Adding organic matter did not enhance the removal of CB and DCB under the trial conditions, which were set up to minimize losses from volatilization. Biodegradation estimation calculations indicated that <5% of the chlorinated benzenes were removed by volatilization and 90% removed by biodegradation. Laboratory shake flask trials confirmed that the soils in the pilot-scale treatment contained a microbial consortium capable of mineralizing CB and DCB. This consortium was capable of mineralizing both CB and DCB with up to 50% of carbon added as chlorinated benzene substrate being recovered as CO2 and up to 44% of organic chlorine being released as chloride ion in mineralization tests, further confirming these chlorinated benzenes were biodegraded. The study confirms that vented ex-situ biotreatment processes for chlorinated benzenes can be achieved without excessive losses from volatilization and that naturally occurring microflora can be readily stimulated with aeration and nutrients.
包括氯苯(CB)和1,2 - 二氯苯(DCB)在内的氯化苯在整个工业中被广泛用作化学中间体和溶剂。在一个中试规模的试验中,对受这些化合物污染的土壤在6立方米的试验单元中进行了处理。空气被抽入每个试验单元,并通过活性炭(GAC)过滤系统排出。试验目的是用营养物质和不同水平的有机改良剂(0%、12%和35%)刺激本地微生物群落。三个试验单元中土壤的初始DCB浓度在<1至6毫克/千克之间变化,平均为2毫克/千克。在2至3周的时间内,土壤中存在的DCB质量约90%被去除。观察到总异养菌(THP)、CB+和DCB+降解菌的数量增加了高达100倍。氯化苯的残留浓度通常低于检测限(0.2毫克/千克)。在为尽量减少挥发损失而设定的试验条件下,添加有机物并没有增强CB和DCB的去除效果。生物降解估算计算表明,<5%的氯化苯通过挥发去除,90%通过生物降解去除。实验室摇瓶试验证实,中试规模处理中的土壤含有能够使CB和DCB矿化的微生物群落。在矿化试验中,这个群落能够使CB和DCB都矿化,添加的作为氯化苯底物的碳中高达50%以二氧化碳形式回收,高达44%的有机氯以氯离子形式在矿化过程中释放,进一步证实了这些氯化苯被生物降解。该研究证实,对于氯化苯的通风异位生物处理过程可以在不过度挥发损失的情况下实现,并且通过曝气和营养物质可以很容易地刺激天然存在的微生物群落。