生物修复石油污染土壤研究现状

石油污染土壤的生物修复方法具有操作简便、费用低、对周围环境污染小、修复效率高等优点,应用前景广阔。从石油污染土壤生物修复过程中修复生物的选择、修复条件的优化、修复效果的评价等方面对近年来生物修复技术的研究进展进行了综述。为推动该方法的广泛应用,还应深入探究降解微生物之间的拮抗和协同机制、进一步降低修复成本、进一步完善修复评价标准,加强重石油污染土壤和特殊环境下石油污染土壤的治理研究,开展复合污染(如石油污染和重金属污染)土壤的修复研究。     

石油污染土壤修复技术研究进展

概述了目前国内外石油污染土壤常用的修复技术及其研究进展,综述了物理修复、化学修复,特别是生物修复技术的优越性,并针对国内外石油污染土壤修复技术研发和实际应用过程中存在的问题,提出加强研发污染土壤综合修复技术、完善修复工程设计、加大新型功能材料的开发和应用力度、加强分子生态学技术在污染土壤修复中的应用4项建议。     

菌剂-菌根联合修复石油污染土壤的实验研究

植物根际是一个能降解土壤中污染物的生物活跃区。本文应用菌根修复技术对某污灌区石油烃污染土壤进行了处理。在污染土壤中种植玉米和黄豆,通过施加不同的菌剂,采取菌剂和菌根强化修复措施,在运行一个生长季节后,土壤中石油类污染物降解率可达53%~78%。本研究为该地区石油污染土壤的治理提供了有力的技术保证。     

通气对石油污染土壤生物修复的影响

为了探讨石油污染土壤的生物修复的有效方法,本研究就通气对石油污染土壤生物降解的影响,在自制反应器中进行了为期50天的堆腐试验。结果表明,通气可为石油烃污染土壤中的微生物提供充足的电子受体,可保持土壤pH稳定,从而促进了微生物的生物活性,强化了它们对石油污染物的氧化降解作用。通过在反应器中,调控通气量使污染土壤中石油烃的降解率进一步提高,为石油污染土壤生物修复技术的应用奠定了科学基础。     

生物修复石油污染土壤

本文概述了石油污染土壤的生物降解机制,分析了生物修复土壤污染技术及其影响因子,提出了强化生物修复的措施及其在我国的应用前景。     

石油污染土壤的生物修复研究进展

生物修复技术是解决环境污染、恢复被人类活动破坏的生态系统、实现人类社会可持续发展的重要手段之一,它具有速度快、消耗低、效率高、成本低、反应条件温和以及无二次污染等显著优点.本文主要介绍了生物修复的原理和特点,石油污染土壤的各种生物修复技术:微生物修复技术、植物修复技术和菌根根际生物修复技术的研究和应用进展.     

植物对污染土壤修复作用的研究进展

利用植物修复污染土壤是一种被人们认为安全可靠的方法.植物修复技术不仅能修复被石油污染的土壤,而且对更多品种污染的土壤修复有效,植物降解高分子有毒化合物的基础是根际环境及根际微生物,与无植物土壤不同.对根际区微生物降解和转化有机化合物的研究,更多的集中于植物对杀虫剂和除草剂的降解.事实证明,生物修复污染土壤是一项实用性和有效性很强的技术.     

土壤气相抽提技术修复柴油污染场地示范研究

土壤气相抽提(SVE)是一种广泛应用于石油类污染土壤修复工程中的原位修复技术,在广东某柴油污染场地开展SVE技术修复示范工程,探讨SVE技术对此类污染场地的修复效果。结果表明:经过3个多月的修复,土壤中总石油烃的最高去除率达64.88%,在试验进行50d后高浓度的挥发性有机物基本被去除,中低浓度污染物仍然存在,土壤中有效磷和速效氮含量与污染物的生物降解作用相关。为缩短修复时间、降低成本,应将SVE与生物通风技术相结合,并采用相应的强化措施(如添加菌剂和营养物质等),以期获得更高的修复效果。     

石油污染土壤中芳烃降解菌及邻苯二酚2,3双加氧酶的克隆

石油污染土壤中的芳烃降解菌是进行土壤修复的主要生物资源,本研究对某炼油厂附近土壤中的芳烃降解菌及邻苯二酚2,3双加氧酶基因进行了研究。结果表明,部分石油烃污染土壤中存在着大量的芳烃降解菌;对其中一个土壤样本中的邻苯二酚2,3双加氧酶基因进行克隆,获得了7个不同的邻苯二酚双加氧酶基因序列,序列分析表明这些基因可能来源于土壤中的假单胞菌,且该基因在土壤中的丰度与污染水平及芳烃降解菌的数量相关。可见,土壤中芳烃降解菌数量及降解基因的丰度和多样性,可以对石油污染土壤的生物修复进行监控并为生物修复提供丰富的微生物资源。     

农药污染土壤的生物强化修复技术研究进展

生物强化作为一种新型、高效的生物修复技术在污染环境治理中具有独特优势。针对目前土壤农药污染现状,本文介绍了土壤微生物修复方法中的生物强化技术的概念及内涵,探讨了在污染土壤环境中影响生物强化修复效率的生物及非生物因素,重点阐述了生物强化技术在4大类农药(有机氯类、有机磷类、拟除虫菊酯类杀虫剂和三嗪类除草剂)污染土壤修复中的研究进展及应用实例,并提出生物强化技术面临的问题和未来研究方向。     

玉米草（Zea Mexicana）与海藻寡糖联合修复石油烃污染土壤的研究

采用玉米草及海藻寡糖联合修复技术研究了石油污染土壤的修复效果,对修复过程中酶活性变化进行了测定,并采用变性梯度凝胶电泳（DGGE）技术测定了土壤中微生物群落的变化。结果表明,种植玉米草可以有效提高土壤中石油烃的降解,与对照相比石油烃降解率增加了11%;加入不同浓度海藻寡糖进一步增加了石油烃的降解效果,降解率最高达到28.6%。种植植物及加入海藻寡糖可以有效提高多酚氧化酶、脱氢酶及尿酶的活性。PCR-DGGE结果表明植物种植及海藻寡糖的加入增加了土壤中微生物数量,其微生物群落结构与未种植植物及修复前土壤相比发生了较大的变化。     

Kinetics of Indigenous Isolated Bacteria used for Ex-Situ Bioremediation of Petroleum Contaminated Soil

The bioremediation of petroleum contaminated soil was investigated using a laboratory scale aerated reactor. The Indigenous bacteria, Stenotrophomonas multophilia, were isolated from the contaminated sites near to Jordan Petroleum Refinery and used further in the bioremediation experiments. First order kinetic equation has been proven to satisfactorily describe the biodegradation of petroleum contained in soil in the presence of the isolated bacteria. The results also showed that the first order kinetic constants for the different bioreactors vary between 0.041 and 0.0071/day. The overall kinetic constant k′ was determined based on food-to-microorganisms ratio and found to be 0.02/day.     

A Comparison of Five Bioassays to Monitor Toxicity During Bioremediation of Pentachlorophenol-Contaminated Soil

Five bioassays were used to measure toxicity during bioremediation of a soil contaminated with pentachlorophenol (PCP; 335 ppm), polycyclic aromatic hydrocarbons (PAHs; 1225 ppm) and petroleum hydrocarbons (19 125 ppm). Different bioremediation treatments were tested in soil microcosms including amendment with phosphorus and/or PCP-degrading Pseudomonas sp. UG30, either as free cells or encapsulated in κ-carrageenan. Soil toxicity was monitored using the solid-phase Microtox test, SOS-chromotest, lettuce seed germination, earthworm survival and sheep red blood cell (RBC) haemolysis assays. PCP levels were reduced in all treatments after 210 days. The RBC lysis assay, Microtox test and SOS-chromotest indicated reduced toxicity in most of the microcosms by day 210. Trends depicted by lettuce seed germination and earthworm survival LC50 values varied with each treatment. For example, in soil amended with phosphorus, both the seed germination and earthworm survival LC50 data suggested increased soil toxicity. However, for soil treated with encapsulated Pseudomonas sp. UG30 cells, the earthworm survival LC50 data indicated reduced toxicity while seed germination LC50 values showed little change from values obtained prior to bioremediation. Our results show that toxicity trends in a contaminated soil during bioremediation differ according to the assay used.     

Bioremediation of petroleum-contaminated soils using Streptomyces sp. Hlh1

Purpose

Bioremediation using microorganisms is a promising strategy to remediate soil with petroleum hydrocarbons. Streptomyces sp. Hlh1, an endophytic strain, has previously demonstrated the ability to degrade crude petroleum in liquid culture. To apply this strain at field scale, it is necessary to test its ability to colonize the soil, compete with native microbiota, and remove the petroleum hydrocarbons under unfavorable conditions. Herein, a study was conducted to evaluate the performance of Streptomyces sp. Hlh1 to remove crude petroleum from contaminated sterilized and non-sterilized soils.

Materials and methods

Soils samples, contaminated with 2%, 5%, and 10% of petroleum, were inoculated with Streptomyces sp. Hlh1, and incubated at 30 °C for 4 weeks. At the end of bioremediation assays, the pollutant concentrations were determined by Gas chromatography flame ionization detector and the degradation rates were also calculated. The survival of the strain in the soil was estimated and the toxicity of metabolites was evaluated on Lactuca sativa.

Results and discussion

Streptomyces sp. Hlh1 was able to grow and remove total petroleum hydrocarbons (TPH), n-alkanes, and aromatic hydrocarbons found in soil samples. In sterilized soil samples, Streptomyces sp. Hlh1 removed up to 40% of TPH at an initial concentration of 10%. Whereas, the maximum TPH removal reached was 55% in non-sterilized soil at an initial concentration of 2%. In addition, it was observed that the degradation of aromatic hydrocarbons was more active than n-alkanes. The strain grew well and produced high biomass in contaminated soil. Lettuce seedling was found to be the adequate bioindicator to assess the toxicity of petroleum end products. Streptomyces sp. Hlh1 performed a successful bioremediation, which was confirmed through the phytotoxicity test.

Conclusions

The study shows the first insight of the contribution of free endophytic actinobacterial strain in the bioremediation of petroleum-contaminated soil; therefore, it suggests that Streptomyces sp. Hl1 can be usefully exploited at field scale.

     

采用通气堆沤对石油烃污染土壤进行生物修复

Laboratory simulation studies and a composting pilot study were conducted to evaluate the capacity of three strains of fungi, indigenous fungus Fusarium sp. and Phanerochaete chrysosporium and Coriolus Versicolor, to remediate petroleum-contaminated soils. In laboratory, the fungi were inoculated into a liquidculture medium and the petroleum-contaminated soil samples for incubation of 40 and 50 days 5 respectively. In the 200-day pilot study, nutrient contents and moisture were adjusted and maintained under aerobiccondition in composting units using concrete container (118.5 cm × 65.5 cm × 12.5 cm) designed specially for this study. The laboratory simulation results showed that all the three fungi were effective in degrading petroleum in the liquid culture medium and in the soil. At the end of both the laboratory incubations, the degradation rates by Phanerochaete chrysosporium were the highest, reaching 66% after incubation in liquid culture for 50 days. This was further demonstrated in the composting pilot study where the degradation rate by P. chrysosporium reached 79% within 200 days, higher than those of the other two fungi (53.1% and 46.1%), indicating that P. chrysosporium was the best fungus for bioremediation of soil contaminated with petroleum. Further research is required to increase degradation rate.     

Changes in Hydrocarbon Composition and Autochthonous Microorganism Growth of Contaminated Mining Soil During Bioremediation

The goal of this study was to evaluate the effect of high Tween 80 concentrations on hydrocarbon contaminants and hydrocarbonoclastic microorganisms present in contaminated mining soil during a bioremediation process. The independent variables included Tween 80 concentration and process time. The elected response variables included concentration of total petroleum hydrocarbons (TPH), the chemical composition of contaminants, viable microbial count, and CO₂ production. These were measured at various time points during the bioremediation process, which was conducted at room temperature. Higher removal of pollutants occurred at low Tween 80 concentrations. An analysis of the normalized variables shows that the rate of TPH degradation depended on microbial growth rate, which depended on Tween 80 concentration. The addition of Tween 80 changed the concentration and type of the residual hydrocarbon contaminants present, as well as the count and genus of the hydrocarbonoclastic microorganisms that grew during the bioremediation process. Higher concentrations of Tween 80 increased the levels of the chemical compounds present in the bioremediated soil while reducing the viable count and microbial diversity during the bioremediation process. Conversely, low Tween 80 concentrations produced only monoethylhexyl phthalate, which is not a petroleum hydrocarbon derivative. Overall, these results prove that the removal of TPH is dependent on the count and genus of active indigenous hydrocarbonoclastic microorganisms in soil, and these conditions may be controlled by modulating the concentration of Tween 80 that is applied.     

钒污染土壤生物修复研究进展

钒污染土壤对生态环境和人体健康存在危害，已成为土壤修复领域关注的热点之一。选取科学合理的修复方法对钒污染土壤进行精准治理十分必要。生物修复技术是钒污染土壤绿色可持续治理的重要发展方向，具有操作简便、环境友好、成本低廉、修复效率较高等优势。本文从植物、动物、微生物单一及联合修复的角度，综述了近年来钒污染土壤生物修复的研究进展，探讨了影响钒污染土壤生物修复效果的主要因素，总结了现阶段的研究不足，并对未来研究方向进行了展望，以期为钒污染土壤生物修复技术的总结与发展应用提供科学依据与理论参考。     

土壤有机氯污染的生物修复和土壤酶活性的关系

简述了土壤生物修复的意义以及微生物 -酶 -生物修复之间的关系 ,对有机氯污染土壤的生物修复进行了初步探讨。研究结果表明 ,自然土壤中含有过氧化氢酶 ;加入“六六六”后 ,降低自然土壤中过氧化氢酶活性。此外 ,对产生过氧化氢酶的外源细菌进行初步搜集、筛选 ,并测定了其产生过氧化氢酶能力。结果表明 ,在有机氯污染的土壤中 ,加入外源细菌能增加土壤过氧化氢酶活性 ;有机氯能诱导加入土壤的外源微生物分泌过氧化氢酶的能力 ;细菌 B1是较有希望的能消除有机氯污染的菌株     

Bioremediation of oil-contaminated soil by combination of soil conditioner and microorganism

Purpose

Oil hydrocarbons are widespread pollutants in soil which pose serious threats to ecological environment. Thus, this study carried out the bioremediation of oil-contaminated soil by using the efficient petroleum-degrading bacteria and soil conditioner, to investigate the changes of physicochemical properties of contaminated soil during bioremediation, reveal the relationship among the exogenous degradation strains and indigenous microbe, and finally illuminate the effects of soil conditioner and microbe on the bioremediation of oil-contaminated soil.

Materials and methods

A PAH-degrading strain named Stenotrophomonas maltophilia was used in this study, which was isolated from an e-waste dismantling area. The soil conditioner in this present study was developed previously by using agricultural wastes, which was in a powdered form and rich in N, P, and K. The simulated experiments were conducted under the control environmental conditions of greenhouse, to study the effects of inoculation and soil conditioner on bioremediation of oil-contaminated soil. Then, the physicochemical properties of soil and the degradation rates of oil were measured at different set times to evaluate the bioremediation effect.

Results and discussion

Adding 1% soil conditioner could significantly improve the soil conditions and offer microorganism enough N, P, and K, which would promote microbial growth and played a key role on bioremediation of oil-contaminated soil. Although in polluted soil, the microorganism could maintain metabolic activity and use the petroleum as carbon source. The soil indigenous microbe was more easily to adapt to the contaminated surrounding. However, when both of them co-existed in soil, they would restrain each other, and go against the oil decomposition. Thus, making two types of microorganisms work to achieve synergy was the key to gain much better remediation effect. Because the indigenous microbe was good at decomposing low molecular compounds and saturated hydrocarbons, while the oil-degrading strains can effectively decompose high molecular weight aromatics.

Conclusions

The soil nutrient and microorganism, including the exogenous oil-degrading strains and the soil indigenous microbe, had an important effect on degradation of petroleum. The addition of soil conditioner, presence of indigenous microbe, and inoculation of oil-degrading strains all were conducive to bioremediation of oil-contaminated site, but the key was to control the proportion and relationship of the three.

Graphical abstract