极端环境下的石油烃生物降解及其在生物修复中的应用

文章综合论述了微生物在高温、低温、高盐等极端条件下对石油烃的生物降解过程,研究了生物降解在生物修复中的应用效果。同时,还介绍了对于强酸、强碱及高压条件下石油烃生物降解的研究状况,论述了研究石油烃生物降解对开发和丰富微生物资源的重要性。     

Bacteria Degrading PCBs and CBs Isolated from Long-Term PCB Contaminated Soil

Bacteria able to degrade polychlorinated biphenyls (PCBs) and chlorobenzoic acids (CBs) were isolated from soil that had been contaminated with PCBs for 15–30 years. Contaminated soil in which PCB content ranged between 10–470 mg/kg was naturally vegetated with different plants including ash (Fraxinus excelsior), birch (Betula pendula), black locust (Robinia pseudoacacia), Austrian pine (Pinus nigra) and goat willow (Salix caprea) trees as well as a variety of grasses and forbs. Bacteria able to use biphenyl as a sole source of carbon and energy were found in the root zone of all plants, but occurred in the largest numbers beneath pine and black locust. Bacteria able to degrade chlorobenzoic acids were isolated from the same location contaminated with PCBs. Strains that were taxonomically identified by 16S rDNA as Pandoraea were able to use 2-CB, 3-CB, 2,3-CB, 2,5-CB as sole carbon sources, and the strain Arthrobacter utilised 4-CB.     

Bioremediation of Stranded Oil on an Arctic Shoreline

The application of slow-release and soluble fertilizers proved to be an effective and environmentally benign way of stimulating oil biodegradation on an Arctic shoreline. Fertilizer application to the surface of the beach delivered nutrients to the oiled sediment beneath the beach surface. There was no significant run-off of this fertilizer to either the nearshore water or to unfertilized plots, and there were no adverse toxicological effects of the fertilizer application. The fertilizer application was followed by an increase in oxygen consumption and carbon dioxide evolution from the beach, increased microbial biomass, and significantly greater biodegradation of oil on the plots that had received fertilizer. The rate of oil biodegradation was approximately doubled over the course of a year by fertilizer applications in the first two months after the spill.Simple test kits proved adequate to monitor the fertilizer-application process in the field in a time frame that would allow the application process to be fine-tuned during treatment on a real spill. Simple test kits and portable instrumentation were useful in demonstrating the initial success of the bioremediation strategy.     

土壤中石油污染物微生物降解过程中各石油烃组分的演变规律

设计了一组实验，将7个石油烃生物降解的主要影响因素迫近在预实验中所得的最佳水平上，探索了石油烃中正构烷烃、异构烷烃、环烷烃、烯烃等不同组分在生物修复过程中各自的降解模式和降解速度。研究发现：碳数的多少是影响石油烃组分降解速度的最大因素；C23烷的降解速度近似于石油烃的总体降解速度；碳数越大，降解越难进行；当碳数相同时，不同类石油烃组分的降解速度由其官能团所决定。     

土壤重金属污染的探讨

随着工农业的发展,土壤重金属污染日益严重.文章综述了土壤重金属污染的现状、污染迁移途径以及危害,并阐述了土壤重金属污染的治理方法.提出了在众多治理方法中,土壤重金属污染生物修复方法是绿色技术,是未来的发展趋势.     

生物表面活性剂及其在重金属污染生态修复中的应用

介绍了不同污染体系中重金属的存在形态,生物表面活性剂的种类、优点及生产方法。综述了几种典型的生物表面活性剂(鼠李糖脂、槐糖脂s、urfactin和皂角苷)及其在重金属污染生态修复中的应用。分析了生物表面活性剂去除重金属的作用机制,阐述了生物表面活性剂修复重金属污染的研究方向。     

稳定同位素技术在污染环境生物修复研究中的应用

稳定同位素技术主要应用于地球化学,它是将人工合成的同位素标记特定的化合物,追踪标记物在生命活动中的变化规律,目前该项技术也广泛应用于环境微生物学、生态学、生物医学等领域.生物修复是利用存在于土壤、地下水和海洋等环境中的生物特别是微生物将有毒、有害的污染物降解为二氧化碳和水,或转化为无害物质,从而使污染的生态环境修复为正常生态环境的过程.这些降解微生物都来自于小部份可培养微生物,对于大部份未可培养降解微生物,通常在实验室条件下很难得到.而利用稳定同位素技术,如13C标记底物,收集利用该底物的微生物核酸,就可以得到具有降解作用的功能微生物,为环境污染生物修复提供重要的菌源和功能基因.环境中的许多物质都可以用SIP来标记,这些标记物主要有PLFA-SIP、DNA-SIP、RNA-SIP等,它们都可以用来在复杂样本中进行有特殊代谢功能微生物的鉴定和分析,在利用微生物进行生物修复中具有重要的意义.图2表1参42     

地下水原位生物修复技术

对地下水原位生物修复技术的概念，实施途径和方案等进行了综述，并介绍了此种方法的优点及局限性。     

假单胞菌AEBL3对土壤中呋喃丹的生物降解

从农药污染的农田土壤中分离到一株假单胞菌AEBL3，该菌能够以呋喃丹为唯一的碳源和氮源生长。使用AEBL3作为生物强化剂对模拟呋喃丹污染的土壤环境进行了生物修复试验。结果表明，接种AEBL3能够明显增加土壤中呋喃丹的降解率。降解菌AEBL3在土壤中具有一定的移动性，当从土壤表层加菌时，对0-7cm深土层中的呋喃丹都有很好的降解效果。在各种投加方式的比较中，以投加降解菌原液修复效果最好，缓冲液悬浮的菌细胞次之，砂粒混合物的效果最差。16S rRNA的变性梯度电泳(DGGE)结果揭示了生物修复过程中土壤微生物菌群结构中的动态变化。     

土壤微生物处理石油污染的研究

本文概述了石油污染土壤微生物处理的几种方法、生物降解机制以及这一领域的研究成果、研究现状，讨论了这一技术在我国的应用前景