西北黄土区石油污染土壤原位微生物生态修复试验研究

通过对西北黄土石油开采区石油污染土壤生物强化原位微生物生态修复方法的试验研究, 充分利用强化原位微生物菌群辅以物理和化学方法与土壤环境相结合的微生物生态技术, 进行了土壤中石油的降解与修复试验研究, 试验结果显示, 土壤中平均石油含量在2754 mg/kg时, 经过11 d~32 d强化原位微生物生态修复技术的修复, 土壤中石油含量降解可达40.92%~80.37%, 验证了微生物生态修复技术在西北黄土区土壤石油污染修复的有效性, 探索了推广应用的可行性。     

基于芽胞的混凝土微生物原位修复技术研究进展

混凝土是最广泛使用的现代建筑材料,在应力作用下易于开裂,使混凝土结构具有渗透性,影响其耐用性和完整性,进而缩短使用寿命。混凝土微生物原位修复技术是一种廉价、有效、绿色的方式,因其具有良好的生物相容性、延长混凝土服役寿命、减少经济损失与环境污染等特点,已成为研究热点。其中,芽胞杆菌因良好的生物矿化能力且其芽胞具有极强的环境耐受能力和长期存活能力而备受关注。为推动微生物原位修复混凝土的研究开发及规模化应用,文中综述了基于芽胞的混凝土原位修复机理、芽胞在混凝土中的生存情况、芽胞与外添加物对混凝土机械性能的影响、修复剂的开发和修复效果等方面的进展,并指出了将来的研究重点,如提高芽胞在混凝土内部恶劣环境下的存活能力、降低外添加物对混凝土机械性能的影响和强化实际现场应用的修复效果等。     

中原石油污染土壤原位微生物生态修复技术的应用

利用优化原位土著微生物菌群辅以物理和化学相结合的生态修复技术, 进行了河南中原油田石油残留污染土壤的野外修复应用研究。修复结果显示, 土壤中残留石油含量平均在2 898.25 mg/kg时, 经过99 d微生物生态修复技术的实施, 土壤中石油含量降解可达99%以上, 为油田区土壤石油残留污染的修复提供了技术方法和推广应用的可行性研究。     

西北黄土区石油污染土壤原位微生物生态修复试验研究

通过对西北黄土石油开采区石油污染土壤生物强化原位微生物生态修复方法的试验研究,充分利用强化原位微生物菌群辅以物理和化学方法与土壤环境相结合的微生物生态技术,进行了土壤中石油的降解与修复试验研究,试验结果显示,土壤中平均石油含量在2754mg/kg时,经过lld～32d强化原位微生物生态修复技术的修复,土壤中石油含量降解可达40.92%～80.37%,验证了微生物生态修复技术在西北黄土区土壤石油污染修复的有效性,探索了推广应用的可行性.     

低温微生物修复石油烃类污染土壤研究进展

耐冷菌、嗜冷菌等低温微生物广泛存在于极地、高山以及高纬度等土壤环境中,是石油烃类污染物在低温条件下降解与转化的重要微生物资源.利用低温微生物的独特优势,石油污染土壤的低温生物修复技术的研究成为当前热点领域.本文系统综述了低温石油烃降解菌的分类及冷适机制,低温微生物对不同类型石油烃组分的降解特征和降解机理,低温环境中接种降解菌、添加营养物质和表面活性剂等强化技术在石油污染土壤中生物修复的应用.以及微生物分子生物学技术在低温微生物降解石油烃的研究现状,为拓展我国石油污染土壤生物修复技术提供参考.     

海洋石油降解微生物及其降解机理

微生物修复作为一种新型环保的生物修复技术,已成为海洋石油污染生物修复的核心技术。对海洋石油降解微生物的种类即细菌、蓝藻、真菌以及藻类进行了总结,对微生物对石油烃的降解途径与降解机理进行了综述。微生物降解烷烃的过程包括末端氧化、烷基氢过氧化物以及环己烷降解3种形式。微生物对芳香烃的降解是通过芳香烃被氧化酶氧化导致苯环开环来实现的。微生物对多环芳烃的降解是在单加氧酶或双加氧酶的催化作用下被最终降解为二氧化碳和水而被分解。并对影响石油烃降解微生物的因素包括温度、营养物质等因素进行了分析。     

2020污染土壤的生物修复专刊序言

生物修复技术,作为可持续发展的重要方向,因其环境友好、高效且无二次污染并能从根本上解决土壤污染问题而受到关注,已经在土壤污染治理中得到了广泛的应用。为了梳理和凝练生物修复技术的发展状况,本专刊收录了该研究领域的16篇论文,分别从植物修复、微生物修复、联合修复、重金属吸收积累的相关分子机制、资源化再利用等方面,详细阐述生物修复技术的发展动态,展望未来的发展趋势,为促进生物修复技术的发展提供参考。     

植物-微生物联合修复化学农药污染土壤的研究进展

化学农药的高毒性、生物积累性和扩散性极易对环境及人类健康造成危害,环境中化学农药的去除尤为重要。植物-微生物联合修复技术因其高效、环境友好和修复成本低等优点受到越来越多的关注,植物-微生物联合修复化学农药污染土壤是一种很有前景的方法。植物为根际和内生细菌提供养分,而细菌通过化学农药的降解和解毒来支持植物生长。本文综述了影响化学农药在植物体内吸收和转运的因素以及植物-微生物修复技术的原理,并讨论了植物与微生物在化学农药污染土壤修复中的协同效应,并对植物-微生物联合修复法在化学农药污染土壤修复中的应用前景进行了展望。     

石油污染土壤的微生物修复技术

该文介绍了微生物修复技术的最新研究内容和方法、重点对石油污染土壤的微生物原位修复、异位修复研究进展及各自的优点、局限性进行了综述,并就石油对微生物修复的影响因素进行探讨,最后讨论了该技术在我国的研究趋势和前景.     

海洋石油污染及其微生物修复研究进展

海洋石油污染严重影响了海洋生态系统平衡和人类健康,海洋石油污染的微生物修复技术因其自身的优势越来越受到人们的重视。介绍了海洋石油污染的现状和治理方法,并着重介绍了海洋中石油污染微生物修复中降解微生物的种类、降解机理和生物修复的研究进展,并指出了生物修复存在并需要克服的问题,以期为海洋石油污染环境修复研究提供参考。     

石油污染土壤的生物降解研究

石油工业迅速的发展带来了许多环境问题。在原油生产与输送过程中[1] ,井喷、泄露及沉降排放等引起的原油进入土壤造成的土壤污染 ,很难治理。原油在环境中残留时间长 ,对土壤微生物和土壤 植物生态系统 ,甚至地下水都产生危害 ,影响土壤肥力 ,破坏土壤生产力 ,严重影响当地的粮食产量及产品质量。当前 ,治理土壤石油污染的方法主要有物理法、化学法和生物治理技术[2 ] 。污染土壤生物清洁技术就是利用微生物将土壤中有害有机污染物降解为无害无机物 (ＣＯ2 和Ｈ2 Ｏ)的过程。降解过程可以由改变土壤理化条件 (包括土壤ｐＨ ,温度、湿度、…     

Responses and roles of roots,microbes, and degrading genes in rhizosphere during phytoremediation of petroleum hydrocarbons contaminated soil

Abstract

Rhizodegradation performed by plant roots and the associated bacteria is one of the major mechanisms that contribute to removal of petroleum hydrocarbons (PHCs) during phytoremediation. In this study, the pot-culture experiment using wild ornamental Hylotelephium spectabile (Boreau) H. Ohba was designed to explore responses and roles of roots, microbes, and degrading genes in the rhizodegradation process. Results showed that PHCs degradation rate by phytoremediation was up to 37.6–53.3% while phytoaccumulation accounted for a low proportion, just at 0.3–13.3%. A total of 37 phyla were classified through the high throughput sequencing, among which Proteobacteria, Actinobacteria, and Acidobacteria were the three most dominant phyla, accounting for >60% of the phylum frequency. The selective enrichment of PHC degraders with high salt-tolerance, including Alcanivorax and Bacteroidetes, was induced. Generally, relative abundance of the PHC degrading genes increased significantly with an increase in PHCs concentrations, and the gene copy number in the phytoremediation group was 1.46–14.44 times as much as that in the unplanted controls. Overall, the presence of PHCs and plant roots showed a stimulating effect on the development of specific degraders containing PHC degrading genes, and correspondingly, a biodegradation-beneficial community structure had been constructed to contribute to PHCs degradation in the rhizosphere.     

Landfarming Process Effects on Biochemical Properties of Petroleum-Contaminated Soils

The presence of petroleum contaminants in soil may be toxic to humans, plants, and soil microorganisms. Therefore, remediation of these compounds from the environment is vital. In this study, bioremediation of two petroleum-contaminated soils (S₁ and S₂) using a landfarming technique was evaluated. Investigation of the effect of this technique on biological and chemical properties of contaminated soil was also part of the goal. The results showed that about 50 and 57% of hydrocarbon contents were eliminated from soils S₁ and S₂ at the end of the experiment, respectively. Landfarming processes enhanced microbial respiration rate in both soils S₁ and S₂. Microbial biomass-nitrogen values in the landfarming plots were significantly (P < 0.05) higher than in the control plots (without landfarming operations). Urease activity increased by 21, 45, 26, and 23% in the landfarming plots as compared to the control plots for soil S₂ at the end of first to the 4th month of the experiment, respectively. There was also significant difference (P < 0.05) in soil pH values between the landfarming treatment and control. Soil electrical conductivity in the landfarming plots was lower than in the controls. Total organic matter and total nitrogen contents in the landfarming plots were significantly lower in comparison to the control plots. It appears that improving soil aeration and exposing new layers of soil to sunlight and air as a result of landfarming operations facilitated the degradation of petroleum hydrocarbons.     

A microbial consortium isolated from a crude oil sample that uses asphaltenes as a carbon and energy source

A microbial consortium capable of mineralizing asphaltenes was obtained from the Maya crude oil. The enrichment system was built with a glass column reactor containing mineral medium supplied with asphaltenes as energy and carbon source. The consortium growth was evaluated in Casoy agar during 40 weeks. The steady-state phase of the enriched bacterial community was observed after 10 weeks when the culture reach 10(5) to 10(6) CFU ml(-1). The isolates belong to bacterial genus reported for degradation of other hydrocarbons and they were identified as Corynebacterium sp., Bacillus sp., Brevibacillus sp. and Staphylococcus sp. The bacterial consortium growth was evaluated by a viable counts during 14 days exposed to different aeration, temperature, salinity, and pH conditions. The ability of the consortium to mineralize asphaltenes was evaluated using the method of ISO 9439 in glass column reactors of 20 x 3.2 cm during 13 days. Temperatures of 55 degrees C and salinity of 1.8% were growth limiting. The respiration of the microbial consortium using asphaltenes as a sole carbon source (800 micromoles CO2 in 13 days) was significantly higher than those of the samples containing only the microbial consortium (200 micromoles CO2) or only asphaltenes (300 micromoles CO2). These results indicated the existence of asphaltenes-degradating microbes in the crude oil and confirmed that the consortium could mineralize asphaltenes in conditions of room temperature, salinity of 100 ppm, aeration of 1 l min(-1) and pH of 7.4.     

石油污染土壤植物-微生物修复研究进展

依据国内外近10年来有关石油污染土壤生物修复研究的成果,综合阐述了石油污染土壤的植物修复、微生物修复及植物-微生物联合修复方法研究,重点讨论植物-微生物联合作用,主要包括植物根际微生物、根分泌物以及菌根对石油污染物降解的影响,提出了污染土壤原位修复中需要重视的问题.     

Degradation of Polycyclic Aromatic Hydrocarbons in the Rhizosphere of Festuca arundinacea and Associated Microbial Community Changes

A phytoremediation growth chamber study was conducted to evaluate the contribution of soil microbial diversity to the contaminant degradation. Target contaminant removal from soil was assessed by monitoring concentrations of polycyclic aromatic hydrocarbons (PAHs), along with changes in the bacterial community structure over a time period of 10 months in the presence of tall fescue (Festuca arundinacea). Enhanced degradation of PAHs was observed in rhizosphere soil, with a maximum reduction in pyrene at a rate 36% higher than that noted for the unvegetated control. The dissipation of < 4-ring PAHs, 4-ring PAHs, and > 4-ring PAHs in unvegetated soil was 70%, 54%, and 49% respectively, whereas a higher dissipation rate was observed in tall fescue treated soil of 78%, 68%, and 61% at the end of the study. Microbial enumeration results showed greater total bacterial numbers and PAH-degrading bacteria in rhizosphere soil when compared to unvegetated soil. The results from the terminal restriction fragment length polymorphism (T-RFLP) analysis indicated that there was a shift in the rhizosphere bacterial community during the phytoremediation process.     

Influence of biochar and compost on phytoremediation of oil-contaminated soil

The use of pyrolyzed carbon, biochar, as a soil amendment is of potential interest for improving phytoremediation of soil that has been contaminated by petroleum hydrocarbons. To examine this question, the research reported here compared the effects of biochar, plants (mesquite tree seedlings), compost and combinations of these treatments on the rate of biodegradation of oil in a contaminated soil and the population size of oil-degrading bacteria. The presence of mesquite plants significantly enhanced oil degradation in all treatments except when biochar was used as the sole amendment without compost. The greatest extent of oil degradation was achieved in soil planted with mesquite and amended with compost (44% of the light hydrocarbon fraction). Most probable number assays showed that biochar generally reduced the population size of the oil-degrading community. The results of this study suggest that biochar addition to petroleum-contaminated soils does not improve the rate of bioremediation. In contrast, the use of plants and compost additions to soil are confirmed as important bioremediation technologies.     

石油烃生物降解过程的研究进展

石油烃污染物属于难降解混合物,生物修复已经成为石油烃污染环境的主要修复方法。文中简述了微生物对石油烃的间期适应过程和转运过程,并通过对部分典型石油烃成分的微生物降解机理和代谢路径的梳理和综述,阐释了石油烃生物降解过程中的菌株、基因、代谢路径等研究进展。此外,利用基因工程和代谢工程等手段,可对野生型石油烃降解菌进行改造,进一步提升其对石油烃污染环境的生物修复能力。最后,从石油烃降解菌的代谢途径改造、人工混菌体系的设计构建等角度,结合合成生物学和代谢工程的手段,提出了对石油烃降解的研究展望,以期提升对石油烃污染物的生物修复效果。     

石油污染地土壤微生物群落的碳源利用特性

应用Biolog微平板技术,研究了大庆油田开采36年的石油污染土壤不同土层（0～10 cm、10～20 cm、20～30 cm）土壤微生物群落对碳源的利用特性.结果表明: 石油污染明显提高了土壤微生物群落的代谢活性,3个土层的微生物代谢强度均高于无污染土壤（CK）,不同土层之间的微生物代谢强度存在显著差异,其中20～30 cm土层的碳源代谢能力最强,其次为10～20 cm土层,0～10 cm土层最弱.石油污染使10～20 cm和20～30 cm土层土壤微生物群落对底物碳源利用种类增多,代谢功能的多样性增强,而0～10 cm土层则无明显变化.10～20 cm土层土壤微生物对底物碳源的利用由对照土壤的羧酸类居多转为石油污染土壤的碳水化合物最多,而20～30 cm土层土壤微生物对底物碳源的利用以羧酸类居多.说明石油污染土壤的微生物群落具有独特的群落结构和特点.     

Biotransformation and Dissolution of Petroleum Hydrocarbons in Natural Flowing Seawater at Low Temperature

The objective of this study was to establish methods for controlled studies of hydrocarbon depletion from thin oil films in cold natural seawater, and to determine biotransformation in relation to other essential depletion processes. Mineral oil was immobilized on the surface of hydrophobic Fluortex fabrics and used for studies of microbial biodegradation in an experimental seawater flow-through system at low temperatures (5.9-7.4 degrees C) during a test period of 42 days. The seawater was collected from a depth of 90 m, and microbial characterization by epifluorescence microscopy, fluorescence in situ hybridization, and most-probable number analysis showed relatively larger fractions of archaea and oil-degrading microbes than in the corresponding surface water. Chemical analysis of hydrocarbons attached to the fabrics during the test period showed that n-alkanes (C10-C36) were decreased by 98% after 21 days, while naphthalenes were depleted by 99-100% during the same period. At the end of the period 4-5 ring polyaromatic hydrocarbon (PAH) compounds were removed by 82% from the fabrics. Analysis of the recalcitrant pentacyclic triterpane C30 17alpha(H),21beta(H)-hopane showed that the oil remained adsorbed to the fabrics during the test period. Comparison of depletion analysis with calculation of hydrocarbon dissolution in a flow-through system indicated that naphthalenes and smaller PAH compounds (alkylated 2-ring and 3-ring compounds) were removed from the fabrics by dissolution. The data further implied that depletion of n-alkanes and 4-5 ring PAH hydrocarbons were the result of biotransformation processes. PCR amplification of bacterial 16S rRNA genes from microbes adhering on the immobilized oil surfaces showed the dominance of a few bands when analysed in denaturing gradient gel electrophoresis (DGGE). Sequence analysis of DGGE bands revealed phylogenetic affiliation to the alpha- and gamma-subdivisions of proteobacteria and to the Chloroflexus-Flavobacterium-Bacteroides group.