电动力学技术强化原位生物修复研究进展

介绍了利用电动力学技术强化土壤及地下水原位生物修复的原理和最新进展。电动力学强化的基本原理是利用电渗析、电迁移和电泳等电动力学效应加速污染环境中有机污染物和微生物运动,注入营养物、电子受体或活性微生物,或者利用电极反应和电流热效应为地下生物降解创造有利条件。研究表明．电动力学技术能有效地强化原位生物修复,而且该技术不破环生态环境．安装和操作简单,成本低廉．有广泛的应用前景。     

农药污染土壤的生物修复技术

本文综述了土壤农药有机污染的生物修复技术,重点分析了植物、微生物对土壤农药污染的修复机制以及影响因子,介绍了几种生物修复技术。     

农药污染土壤的生物修复技术

本文综述了土壤农药有机污染的生物修复技术 ,重点分析了植物、微生物对土壤农药污染的修复机制以及影响因子 ,介绍了几种生物修复技术     

基于嗜盐微生物的高盐废水生物强化处理研究进展

针对传统活性污泥法在高盐废水的处理过程中具有周期长、抗冲击能力差以及盐分耐受效果不好等缺点,引入嗜盐微生物,用来强化废水的生物法处理效果。介绍了嗜盐微生物的污染物去除机理和驯化方法,概括了影响嗜盐微生物处理的关键因素;结合嗜盐微生物在好氧和厌氧反应器内的实际应用,总结了其在实际处理高盐废水中相较于普通生物法的强化效果,并从反应器的区别上分析原因。在高盐废水的处理实例中,好氧嗜盐微生物的应用较多,而厌氧嗜盐微生物的应用较少,未来需要对厌氧嗜盐微生物的自然界提取、驯化培养以及在厌氧反应器中的应用拓展进行研究和讨论。     

挥发性有机污染物与恶臭的生物处理技术及其工艺选择

本文介绍了生物滤池、生物洗涤塔和生物滴滤池处理挥发性有机污染物及恶臭的特性、近期发展状况及其应用。阐述了亨利系在选择生物处理技术中的应用,以及生物反应器内填料、微生物的选择。     

挥发性有机污染物与恶臭的生物处理技术及其工艺选择

本文介绍了生物滤池、生物洗涤塔和生物滴滤池处理挥发性有机污染物及恶臭的特性、近期发展状况及其应用。阐述了亨利系数在选择生物处理技术中的作用 ,以及生物反应器内填料、微生物的选择     

生物强化系统微生物分子诊断技术的应用及新发展

现代分子生物技术的飞速发展及其在环境研究领域的应用，为生物强化技术的研究和发展提供了新方法和新思路。本文从生物强化系统特异微生物检测及定量化技术、生物强化系统微生物群落结构组成及动态演替规律研究、生物强化作用机制的分子生物学解析、生物强化菌的基因工程构建、生物强化系统微生物的安全释放及控制技术几方面，对生物强化系统微生物分子诊断技术的应用和发展作了较为全面的综述。     

印染废水生物强化处理技术研究进展

印染废水是国内外公认的难处理的工业废水之一 ,活性污泥法是目前最常用的处理方法 ,但还存在诸多问题。在分析中 ,主要从生物强化技术、固定化微生物技术和微生物活性增加技术等方面 ,总结了废水生物处理技术强化研究进展 ,并讨论了今后的研究方向。     

生物强化系统微生物分子诊断技术的应用及新发展

现代分子生物技术的飞速发展及其在环境研究领域的应用,为生物强化技术的研究和发展提供了新方法和新思路.本文从生物强化系统特异微生物检测及定量化技术、生物强化系统微生物群落结构组成及动态演替规律研究、生物强化作用机制的分子生物学解析、生物强化菌的基因工程构建、生物强化系统微生物的安全释放及控制技术几方面,对生物强化系统微生物分子诊断技术的应用和发展作了较为全面的综述.     

重金属废水的生物处理技术

介绍了重金属废水生物处理技术的一般原理，主要分析了微生物絮凝法、生物吸附法和植物修复技术的研究现状及应用前景。指出了利用生物化学方法处理重金属废水是一种长期、高效、经济、可靠的方法。     

Bioremediation and reclamation of soil contaminated with petroleum oil hydrocarbons by exogenously seeded bacterial consortium: a pilot-scale study

Purpose  

Spillage of petroleum hydrocarbons causes significant environmental pollution. Bioremediation is an effective process to remediate petroleum oil contaminant from the ecosystem. The aim of the present study was to reclaim a petroleum oil-contaminated soil which was unsuitable for the cultivation of crop plants by using petroleum oil hydrocarbon-degrading microbial consortium.     

Bioavailability and biodegradation of prosulfocarb in soil

Active microbial degraders of the herbicide prosulfocarb (PSC) were isolated to evaluate their performance in soil with a view to their use for bioremediation. The isolated cultures (a microbial consortium and a Pseudomonas sp. strain) were active when tested in mineral medium with PSC as the only carbon source, but had an adverse effect on the soil indigenous microflora. Biodegradation in the inoculated soils was thus lower than in the uninoculated soil when only the indigenous microflora was present. Further tests showed that the strong affinity of PSC for soil organic matter affected its bioavailability and hence its biodegradation by the inocula. Bioremediation of PSC contaminated soils could thus be undertaken by biostimulation of indigenous microflora.     

石油污染土壤的植物与微生物修复技术

石油污染土壤的生物修复技术具有成本低、简便高效、对环境影响小等优点,正逐步成为石油污染治理研究的热点领域,具有广阔的发展前景.介绍了我国的石油污染概况及生物修复技术在石油污染治理中的应用,重点对石油污染土壤的微生物修复、植物修复、植物一微生物联合修复技术的研究进展及各自的优点、局限性进行了综述,并提出了石油污染土壤生物修复技术研究的重点领域.     

Bioremediation of HCH-contaminated soil: elimination of inhibitory effects of the insecticide on radish and green gram seed germination

The effects of technical grade hexachlorocyclohexane (tech-HCH) on the germination of different seeds were tested. Two types of seeds, radish and green gram showed marked reduction in germination percentage and seeding vigour index. The abnormalities and reduction in germination increased with increasing concentration of tech-HCH. At 100 microg HCH level the germination of radish and green gram seeds was inhibited almost completely on moist filter paper and soil. Protease and amylase activities were reduced in seeds grown in soil spiked with tech-HCH. Bioremediation of HCH-spiked soils with a HCH-degrading microbial consortium helped in eliminating the toxic effects of tech-HCH towards seed germination. The degradation of 25 microg tech-HCH g(-1) soil was complete by 120 h. The seed germination and the activities of the assayed enzymes, amylase and protease, were same as before or better in bioremediated soils.     

Assessment of the toxic potential of hydrocarbon containing sludges

A short-time period microbial toxicity test-battery was used for the investigation of acute toxicity and genotoxicity of five hydrocarbon containing sludges. Four sludges were obtained from a petrochemical industry and the fifth from a petroleum refinery. Some of the sludges had been stored for long periods. Bioremediation potential assays for soils polluted with each of the sludges were also considered. The sludges did not show acute toxicity in any of the microbial tests performed. However, when the diethylether soluble fractions of these sludges were analyzed some of them showed acute toxicity, for which the clearest results were obtained with the resazurin reduction method. The greatest toxicity detected with the Resazurin based method was found in the diethylether extracts of the freshly collected (not stored) sludges. On the other hand, the diethylether soluble fraction of those sludges that had been stored showed genotoxicity when analyzed with the Salmonella/microsome assay. After the incorporation of the sludges into the soil, increased bacterial counts were noted and substantial hydrocarbon elimination was achieved in 30 days, showing that bioremediation may be a possible technology for cleaning soils polluted with these sludges.     

The roles of biological interactions and pollutant contamination in shaping microbial benthic community structure

Biological interactions between metazoans and the microbial community play a major role in structuring food webs in aquatic sediments. Pollutants can also strongly affect the structure of meiofauna and microbial communities. This study aims investigating, in a non-contaminated sediment, the impact of meiofauna on bacteria facing contamination by a mixture of three PAHs (fluoranthene, phenanthrene and pyrene). Sediment microcosms were incubated in the presence or absence of meiofauna during 30 days. Bioremediation treatments, nutrient amendment and addition of a hydrocarbon-degrading bacterium, were also tested to enhance PAH biodegradation. Results clearly show the important role of meiofauna as structuring factor for bacterial communities with significant changes observed in the molecular fingerprints. However, these structural changes were not concomitant with changes in biomass or function. PAH contamination had a severe impact on total meiofaunal abundance with a strong decrease of nematodes and the complete disappearance of polychaetes and copepods. In contrast, correspondence analysis, based on T-RFLP fingerprints, showed that contamination by PAH resulted in small shifts in microbial composition, with or without meiofauna, suggesting a relative tolerance of bacteria to the PAH cocktail. The PAH bioremediation treatments were highly efficient with more than 95% biodegradation. No significant difference was observed in presence or absence of meiofauna. Nutrient addition strongly enhanced bacterial and meiofaunal abundances as compared to control and contaminated microcosms, as well as inducing important changes in the bacterial community structure. Nutrients thus were the main structural factor in shaping bacterial community composition, while the role of meiofauna was less evident.     

Bioremediation process on Brazil shoreline

GOAL, SCOPE AND BACKGROUND: Bioremediation technique can be considered a promising alternative to clean oil spills using microbial processes to reduce the concentration and/or the toxicity of pollutants. To understand the importance of this work we must know that there is only little research performed to date using bioremediation techniques to clean oil spills in tropical countries. So, the main objective of this work is to analyze the behavior of a laboratory's bioremediation test using nutrients on coastal sediments. METHODS: The bioremediation process is followed through geochemical analysis during the tests. This organic material is analyzed by medium pressure liquid chromatography (MPLC), gas chromatography/flame ionization detection (GC/FID) and gas chromatography/ mass spectrometry. By microbial counting, the number of total bacteria and degrading bacteria is determined during the experiments, in order to confirm the effectiveness of the bioremediation process. The seawater obtained throughout the bioremediation process is analyzed for nutrients grade (phosphate and ammonium ions) and also for its toxicity (Microtox tests) due the presence of hydrocarbons and fertilizer. RESULTS: The results from the geochemical analyses of the oil show a relative decrease in the saturated hydrocarbon fraction that is compensated by a relative enrichment on polar compounds. It's confirmed by the fingerprint evaluation where it is possible to see a complete reduction of the normal alkanes followed by isoprenoids. Seawater analysis done by toxicity and nutrients analysis, such as microbial counting (total and degrading bacteria), confirm the fertilizer effectiveness during the bioremediation process. DISCUSSION: Results from simulating test using NPK, a low-price plant fertilizer, suggest that it's able to stimulate the degradation process. Results from medium pressure liquid chromatography (MPLC), done at two different depths (surface and subsurface), show different behavior during the biodegradation process where the later is seen to be more susceptible to microbial attack. Data from bioremediation unit shows a bigger reduction of the saturated fraction, followed by some smaller reduction of aromatic fractions, compensated by a relative increase from polar compounds (NSO). n-C17/pristane, n-C18/ fitane and pristane/fitane rates show constant values for the unity control, different from bioremediation samples which have a significant reduction, especially on subsurface areas, where a strong fall in the rates, seen to be reduced to zero over twenty days, had occurred during the first ten days. However, sample surfaces are reduced to zero in thirty days of experiments, proving that biodegradation is better on subsurfaces. Gaseous chromatography/mass spectrometry (CG/MS) analysis shows constant values to cyclic biomarker rates and aromatic compounds, suggesting that the biodegradation process is not strong enough to reduce these composites. Microbial analysis shows a reduction on heterotrophic (total bacteria) number from control unit, probably because the bacteria uses the spill oil like carbon source and energy. However, the number increases on bioremediation unit, because it uses NPK like a biostimulator. The hydrocarbonoclastic number isn't enough on the first moment, but it's detected after 30 days and quantified in all units, showing big values especially in bioremediation. Toxicity tests confirm that NPK fertilizer does not intoxicate the shoreline during the application of the bioremediation technique. Some nutrient concentration shows high values of ammonium and phosphate per bioremediation unit, reducing by the end of the experiment. CONCLUSIONS: Results reached the goal, finding a proper nutrient (NPK fertilizer) to stimulate the biodegradation process, growing bacteria responsible for reducing impact-contaminated coast ambient by oil spills. Chemical analysis of oil shows a reduction in the saturated fraction with a relative enrichment in polar composites (NSO) and the aromatic fraction from oil remaining constant. Subsurface samples show more biodegradation than surface samples, probably because the first one has higher humidity. Linear alcanes are more biodegraded than isoprenoids, confirming the biodegradation susceptibility order. Saturated cyclic biomarkers and aromatic compounds show constant behavior maybe because the nutrients or time was not enough for microorganismic attack. Fertilizer does not demonstrate any toxic effects in local biota so that it does not compromise the technique applicability and the environment is not saturated by nutrients during the simulation, especially since the coastal environment is an open system affected daily by tides. Therefore, bioremediation tests can be classified as moderate, reaching level 5 in the classification scale by Peters & Moldowan (1993). RECOMMENDATIONS AND PERSPECTIVES: The use of marine environment by the petroleum industry on exploration, production and transportation operation, transform this oil to become the most important pollutant in the oceans. Bioremediation is an important technique used to clean spilled oil impacting on shorelines, accelerating the biodegradation process by using fertilizer growing the microorganisms responsible for decontaminating the environment. We recommend confirming the efficiency of NPK nutrient used on bioremediation simulating experiments on beaches, while monitoring the chemical changes long-term. NPK fertilizer can be used to stimulate the biodegradation process on shoreline impacted by spilled oil.     

不同生育期美人蕉-微生物修复富营养化水体

生物修复水体富营养化,尤其是植物和微生物联合修复为目前水体富营养化治理方面的研究热点。不同生育期植物和微生物联合修复鲜见报道。研究不同生育期美人蕉和固定化微生物对富营养化水体的联合修复作用。结果表明,营养生长期和开花期美人蕉-微生物组处理前3天,富营养化水体中不同形态氮和磷浓度快速下降,用于美人蕉生长发育。从富营养化水体氮去除效果来看,营养生长期美人蕉-微生物联合处理去除效果略好于开花期,对磷的去除效果相反。美人蕉吸收氮元素为营养器官利用,其营养器官全氮增长量与生殖器官（花）形成显著差异（P<0.05）。花是美人蕉全磷含量最高、全磷增长量最高的器官,其全磷含量和全磷增长量与营养器官均形成显著差异（P<0.05）。实验结果表明,不同生育期美人蕉-微生物联合处理对氮和磷的吸收利用存在差异。     

Innovative technologies for contaminated site remediation: focus on bioremediation.

Bioremediation, the process by which hazardous substances are degraded by microorganisms, is at the forefront of a larger group of innovative remediation technologies being applied at hazardous waste sites worldwide. Although the process of bioremediation has been utilized for decades in the field of wastewater engineering, its application to soils and groundwater at hazardous waste sites is fairly new and still undergoing intensive development. This article is intended to provide both an overview of the state of practice of bioremediation in hazardous waste remediation operations, and an inventory of issues to consider when evaluating the use of this technology for a contaminated site. These topics will be the subject matter of a unique Bioremediation Satellite seminar to be broadcast on January 9, 1992. The seminar, a joint venture between the Air and Waste Management Association (A&WMA) and the Hazardous Waste Action Coalition (HWAC), is the first in a series of satellite seminars that will deal with innovative hazardous waste remediation technologies. The intent of these seminars is to design programs which will make hazardous waste practitioners more familiar with innovative remediation technologies so that they will consider using the technologies in future clean-up operations.