石油污染土壤的生物修复技术

1　前　言在石油生产、贮运、炼制加工及使用过程中 ,由于事故 ,不正常操作及检修等原因 ,都会有石油烃类的溢出和排放。例如 ,油田开发过程中的井喷事故 ;输油管线和贮油罐的泄漏事故 ;油槽车和油轮的泄漏事故 ;油井清蜡和油田地面设备检修 ;炼油和石油化工生产装置检修等。石油烃类大量溢出 ,应当尽可能予以回收 ,但有的情况下回收很困难 ,即使尽力回收 ,仍会残留一部分 ,对环境 (土壤、地面和地下水 )造成污染。其进入土壤后 ,会破坏土壤结构 ,分散土粒 ,使土壤的透水性降低。其富含的反应基能与无机氮、磷结合并限制硝化作用和脱磷酸作…     

生物反应器法处理油泥污染土壤的研究

采油过程产生的油泥是整个石油烃污染源的重点。在陆地生态环境中 ,烃类的大量存在往往对植物的生物学质量产生不利影响 ,更重要的是石油中的一些多环芳烃是致癌和致突变物质 ,这些致癌和致突变的有机污染物进入农田生态系统后 ,在动植物体内逐渐富集 ,进而威胁人类的生存和健康[1 ,1 1 ] 。大量的废弃油泥 ,不仅污染农田 ,同时也给石油行业带来巨大的经济损失。污染土壤的治理主要有物理、化学和生物 (生物修复 )方法 ,生物修复方法被认为最有生命力。污染土壤生物修复技术主要有 3种 ,即原位处理、挖掘堆置处理和反应器处理。反应器处理是…     

石油污染土壤生物降解生态条件研究

生物治理是石油污染土壤主要的有效的治理方法。微生物、污染物及环境等方面的因素都影响着生物降解效率。通过最佳生物降解条件的研究,提出了提高生物降解效率的措施。     

Biodegradation of Hopane Prevents Use as Conservative Biomarker During Bioremediation of PAHs in Petroleum Contaminated Soils

The pentacyclic triterpane C₃₀ 17α (H), 21β (H)-hopane, a biomarker commonly used in hydrocarbon bioremediation laboratory experiments and field studies, was found to be completely removed without the formation of the demethylated intermediate nor-hopane in a crude oil-contaminated soil undergoing slurry biotreatment, while PAHs such as benzo(e)pyrene were recalcitrant. The partial or complete biodegradation of hopane has also been previously reported in a few bioremediation studies and has been explored by petroleum geochemists in an effort to characterize crude oil deposits. It is currently not clear what conditions induce hopane biodegradation or biotransformation, although the use of microbial enrichment cultures appears to speed up the process. Considering that hopane is not necessarily conserved during a bioremediation study, the uncritical normalization of hydrocarbon concentrations using this biomarker can lead to incorrect estimates of biodegradation rates and extents. If hopane is found to be unstable in a particular case, other potential biomarkers such as pentahopane, oleanane, or vanadium may be used instead.     

An Investigation of the Ability of a 14C-Labeled Hydrocarbon Mineralization Test to Predict Bioremediation of Soils Contaminated with Petroleum Hydrocarbons

Bioremediation is a widely accepted technology for the remediation of hydrocarbon-contaminated soil. Treatability studies are usually carried out to assess the biodegradation potential of the contaminants and to design optimal treatments. Laboratory studies measuring soil respiration are often used. One method consists of monitoring the mineralization of a ¹⁴C-labeled hydrocarbon surrogate added to the contaminated soil. This study investigates the ability of this method to properly predict the removal of the hydrocarbon contaminants initially found in soils. Mineralization of ¹⁴C-labeled hexadecane was monitored in seven soils contaminated with various hydrocarbon mixtures, both fresh and weathered, in microcosm experiments. Reduction of total petroleum hydrocarbon (TPH) concentrations was measured simultaneously in separate microcosms. Both types of microcosms were subjected to the same amendment regimes. For all soils, poor correlation was observed between the mineralization and TPH reduction data sets. Mineralization data supported contaminants removal data in only one soil. Findings indicate that the radioactive surrogate method does not reliably predict the extent of, and the effect of amendments on, the removal of the hydrocarbons initially present in soil, and may therefore predict suboptimal treatment regimes. Recommendations for soil treatability protocols are provided.     

Remediation of Copper from Copper Mine Wastes and Contaminated Soils Using (S,S)-Ethylenediaminedisuccinic Acid and Acidophilic Bacteria

The biodegradable chelating agent (S,S)-Ehylenediaminedisuccinic acid (EDDS), autochthonous acidophilic bacteria, and a combination of the two means were investigated for the removal of pseudo-total and ethylenediaminetetraacetic acid (EDTA)-available content of Cu from surface layers of three soil categories in the Bor copper mining area. Their efficiencies were compared at mine overburden, flotation tailings, and agricultural land sites in order to determine the potential role of these approaches in the soil remediation process. The most effective removal of Cu was achieved on flotation tailings, where combined treatment showed significant reduction of pseudo-total and EDTA-available concentrations of Cu (40.5?±?27.3% and 99.6?±?0.2%, respectively). Acidophilic bacteria treatment showed high efficiency on flotation tailings, removing 94.1?±?1.2% of EDTA-available Cu. EDDS treatment showed discernible results in the removal of EDTA-available Cu from agricultural land soil (44.4?±?13.9%). In the case of overburden soil material, selected agents did not have statistically significant results in the removal of pseudo-total or EDTA-available fraction of Cu. Chosen remediation approaches showed diverse efficiency for soil categories on investigated sites. Combined approach showed synergistic results in the case of EDTA-available Cu removal from flotation tailings soils, suggesting that this combination deserves further attention as a potentially promising environmentally friendly remediation option.     

生物技术在放射性污染土壤修复中的研究进展

综述了植物提取和植物稳定等植物修复技术和微生物修复技术等生物技术在放射性重金属污染土壤修复中的研究进展,并对其研究中存在的问题及今后的应用前景进行了讨论。     

Prediction of Petroleum Hydrocarbon Bioavailability in Contaminated Soils and Sediments

Recently, several laboratory methods have been developed for the prediction of contaminant bioavailability. So far, none of these methods has been extensively tested for petroleum hydrocarbons. In the present study we investigated solid-phase extraction and persulfate oxidation for the prediction of total petroleum hydrocarbon (TPH) bioavailability. One sediment and two soil samples were subjected to solid-phase extraction, persulfate oxidation, and biodegradation, after which hydrocarbon removal was compared. It was demonstrated that a short solid-phase extraction (168?h) provided a good method for the prediction of the extent of TPH degradation in an optimized slurry reactor (84?d). Solid-phase extraction slightly underestimated the degradation of readily biodegradable hydrocarbons, whereas it slightly overestimated the degradation of poorly biodegradable hydrocarbons. Persulfate oxidation appeared to be unfit for the prediction of TPH bioavailability as persulfate was unable to oxidize hydrocarbons with a high ionization potential. Hydrocarbons that were affected were likely to be transformed rather than completely oxidized. Nevertheless, persulfate oxidation provided a good method for the prediction of polycyclic aromatic hydrocarbon (PAH) bioavailability.     

Current Risk Assessment Approaches to Address Petroleum Hydrocarbon Mixtures in Soils

Products that exist as complex chemical mixtures, such as petroleum products, are used widely in commerce, and accidental releases of these products into the environment have led to thousands of contaminated sites nationwide. Developing sound estimates of potential health risks posed by these sites is challenging because of the composition of these products, their behavior in the environment, and the paucity of toxicological information available for many of the component compounds. In developing risk based cleanup goals for petroleum products and other complex commercial mixtures, the simplest approach is to assume that the entire mixture is comprised of the most toxic constituent, particularly when standards are unavailable for each of the components of the mixture. This approach often results in excessively conservative regulatory goals; thus, methods are needed which more accurately reflect the actual composition and aggregate toxicity of the mixture. Three approaches for the development of risk based soil cleanup goals for petroleum hydrocarbon mixtures are identified and illustrated using mineral spirits as an example. For the examples presented, estimates of the proportions of components in mineral spirits were based on virgin, unused product; however, detailed component analysis of weathered samples may permit the calculation of more precise, site specific cleanup goals.     

Petroleum Bioremediation in Seawater Using Guano as the Fertilizer

The biodegradation of hydrocarbon pollutants in open systems, such as oceans, is generally limited by the availability of utilizable nitrogen and phosphorus sources. Here the authors demonstrate the potential of overcoming this problem with guano as the fertilizer. In the first set of experiments, the principle and conditions for growing bacteria on a water insoluble fertilizer was established, using uric acid as the nitrogen source and a pure culture of an isolated hydrocarbon-degrading bacterium, Alcanivorax sp. OK2. Using a simulated open system, it was demonstrated that uric acid (the major nitrogen component of guano) binds to crude oil and is available for the growth of strain OK2 and petroleum degradation. In the second set of experiments, using a simulated open system, it was demonstrated that commercial guano was an effective source of nitrogen and phosphorus for the growth of marine bacteria on crude oil. Bacterial cultures reached over 10⁸ cells per ml and 70% of the crude oil was degraded. Controls using ammonium sulfate and phosphate in place of guano in the simulated open system reached only 10⁶ cells per ml and showed no detectable hydrocarbon degradation. Isolation and characterization of the bacteria in the crude oil/guano cultures indicated that they were primarily strains of Alcanivorax and Alteromonas.     

On-Site Treatment of Contaminated Soils: An Approach to Bioremediation of Weathered Petroleum Compounds

A bench-scale investigation was conducted prior to on-site bioremediation of 52,000 cubic yards of contaminated soil containing weathered, structurally complex petroleum compounds from an inactive oil refinery. Addition of bulking agents was required to improve soil physical properties. A supplemental study was also conducted to evaluate the effectiveness of bio-enhancement products. Loss of n-alkanes was rapid in soil mixtures containing a high nitrogen sludge compost, but very slow in mixtures containing wood products as bulking agents. By completion of the study at day 110, the isoprenoids pristane and phytane had nearly disappeared from mixtures containing sludge compost. Clearly, pristane and phytane are inadequate biomarkers when conditions favor an advanced stage of biodegradation. Nearly half the complex branched and cyclic alkanes in the unresolved complex mixture also degraded. After 70 days, depletion of dibenzo-thiophenes and phenan-threnes was 75 and 90%, respectively. The most stable PAHs within each group were the highly methylated homologues. Because of their complex structures, both steranes and hopanes were stable in all soil mixtures. Data were normalized to hopanes as a conserved internal standard or biomarker. Use of hopane-normalized data successfully eliminated much of the data variability and permitted a more accurate assessment of biodegradation. A relatively slow decline in total hydrocarbons occurred later in the study. This slowing tendency of microbial utilization is caused not only by substrate depletion, but also because remaining hydrocarbons are structurally more complex and persistent. Because of this, it is important to avoid using kinetic data from early stages of bioremediation to predict later hydrocarbon losses, such as the time required to attain a cleanup standard. In the supplemental study, an oleophilic fertilizer product accelerated hydrocarbon degradation when compared with a conventional fertilizer. This product will be tested in combination with organic bulking agents under field conditions to determine its cost effectiveness.     

Enhanced Biodegradation of Petroleum Hydrocarbons in Contaminated Soil

Soil samples taken from a contaminated site in Northern Quebec, Canada, exhibited a low capacity for biodegradation of total petroleum hydrocarbons (TPH), despite a high capacity for the mineralization of aromatic hydrocarbons and a low toxicity of soil leachates as measured by Microtox assay. Toxicity assays directly performed on surface soil, including earthworm mortality and barley seedling emergence, indicated moderate to high levels of toxicity. Soil biostimulation did not improve the removal of petroleum hydrocarbons, while bioaugmentation of soil with a developed enrichment culture increased the efficiency of hydrocarbon removal from 20.4% to 49.2%. A considerable increase in the removal of TPH was obtained in a bioslurry process, enhancing the mass transfer of hydrocarbons from soil to the aqueous phase and increasing the efficiency of hydrocarbon removal to over 70% after 45 days of incubation. The addition of ionic or nonionic surfactants did not have a significant impact on biodegradation of hydrocarbons. The extent of hydrocarbon mineralization during the bioslurry process after 45 days of incubation ranged from 41.3% to 58.9%, indicating that 62.7% to 83.1% of the eliminated TPH were transformed into CO₂ and water.     

Enhanced Biodegradation of Petroleum Hydrocarbons in Contaminated Soil

Soil samples taken from a contaminated site in Northern Quebec, Canada, exhibited a low capacity for biodegradation of total petroleum hydrocarbons (TPH), despite a high capacity for the mineralization of aromatic hydrocarbons and a low toxicity of soil leachates as measured by Microtox assay. Toxicity assays directly performed on surface soil, including earthworm mortality and barley seedling emergence, indicated moderate to high levels of toxicity. Soil biostimulation did not improve the removal of petroleum hydrocarbons, while bioaugmentation of soil with a developed enrichment culture increased the efficiency of hydrocarbon removal from 20.4% to 49.2%. A considerable increase in the removal of TPH was obtained in a bioslurry process, enhancing the mass transfer of hydrocarbons from soil to the aqueous phase and increasing the efficiency of hydrocarbon removal to over 70% after 45 days of incubation. The addition of ionic or nonionic surfactants did not have a significant impact on biodegradation of hydrocarbons. The extent of hydrocarbon mineralization during the bioslurry process after 45 days of incubation ranged from 41.3% to 58.9%, indicating that 62.7% to 83.1% of the eliminated TPH were transformed into CO₂ and water.     

污染土壤微生物群落结构分子鉴定技术研究进展

土壤微生物群落结构多样性检测是土壤修复、监测、评估时的一个重要参数。由于绝大多数微生物在实验室条件下是不可培养,因而早期依赖于微生物培养的检测结果代表性不强。20世纪90年代以来,不依赖于微生物培养的分子生物学方法是研究微生物群落结构的重要手段。该文对近年来土壤污染微生物群落结构研究所采用的主要分子生物学方法按照其原理进行了比较、分析、总结。根据不同技术的灵敏度、优缺点分析了其适用范围。指出了目前技术中存在的一些共性问题和缺陷并展望了土壤修复领域分子生物学技术的发展趋势。     

中国水青冈分布,生长和更新特点

中国水青冈分布、生长和更新特点吴刚（中国科学院生态环境研究中心,北京１０００８５）Ｄｉｓｔｒｉｂｕｔｉｏｎ,ＧｒｏｗｔｈａｎｄＲｅｖｅｇｅｔａｔｉｏｎａｌＣｈａｒａｃｔｅｒｉｓｔｉｃｓｏｆＦａｇｕｓｉｎＣｈｉｎａ．ＷｕＧａｎｇ（ＲｅｓｅａｒｃｈＣｅｎ...     

酞酸酯污染农田土壤生物修复研究进展

酞酸酯是目前世界上产量最大、应用面积最广的人工合成有机物,作为塑化剂被广泛应用于塑料制品中。近年来发现酞酸酯是一类典型的环境内分泌干扰物。随着生活中塑料制品日益增多,尤其是农用薄膜和有机肥的大量使用,农田土壤中酞酸酯污染日益加剧,酞酸酯污染土壤的修复逐渐引起国内外学者的广泛关注。生物修复具有价格低廉、效果良好和环境友好等特点,尤其适合于大面积污染农田土壤修复。从植物修复、微生物修复、植物微生物联合修复和动物修复等方面综述了国内外酞酸酯污染土壤生物修复的研究现状,并从高效修复植物筛选及机理探讨、实际污染土壤的降解菌修复研究、高效降解菌群的构建和作用机制等方面对该领域的研究进行了展望,以期为酞酸酯污染土壤的修复研究提供借鉴并拓展新的思路。     

Application of Biosurfactants Produced by Pseudomonas aeruginosa SP4 for Bioremediation of Soils Contaminated by Pyrene

Biosurfactants are considered to facilitate PAHs dissolution in soil slurries for bioremediation applications. In this work, the carbon and nitrogen sources, pH, C/N ratio, and salinity, were considered for optimization of biosurfactant production by Pseudomonas aeruginosa SP4 isolate to enhance pyrene removal from the contaminated soil. Analysis of ANOVA indicated that the carbon source was the most effective factor, followed by pH, nitrogen source, C/N ratio, and salinity. Taguchi experimental design proposed the optimum operating conditions of olive oil, NH₄NO₃, C/N ratio of 5, salinity of 0.5%, and pH 7. Applying the conditions determined by Taguchi design led to a production yield of 452 mg L^?1 (13% improvement) at the optimum conditions. The main characteristics of produced biosurfactant included the critical micelle concentration (CMC) of 60 mg L^?1 and liquid medium surface tension of 29.5 mN m^?1. Produced biosurfactant was used for bioremediation of soil artificially contaminated with 500 mg kg^?1 of pyrene. Following the addition of 250 mg L^?1 biosurfactant, the pyrene removal of 84.6% was obtained compared to 59.8% for control sample without any surfactant.     

Site-Specific Limitations of Using Urea as a Nitrogen Source in Biodegradation of Petroleum Wastes in Soil

Nutrient addition is important to achieving the carbon/nitrogen balance and successful biodegradation of petroleum contaminants. Urea has been considered as a preferred nitrogen source in enhancing biodegradation, because of its high nitrogen content and commercial availability. This study investigated urea in the biodegradation of petroleum-contaminated soils collected from an arid and sandy area in Egypt. Ammonium nitrate served as the nitrogen amendment control in this study. Biodegradation of petroleum-contaminated soils from Wyoming was monitored as a comparison. Addition of urea failed to improve the enhancement of biodegradation of petroleum-impacted soil from the Egyptian site; in addition, urea demonstrates an adverse effect on the biodegradation rates. Results indicate that urea or its intermediates may inhibit the microorganisms involved in petroleum degradation. Data from this study suggest that the application of urea in the enhancement of biodegradation of petroleum compounds should consider site specificity, and may not be applicable in geological areas or soils structures similar to those in this study.     

Release of Chemicals from Contaminated Soils

At sites that contain contaminated soils, there can be questions about the magnitude of risk posed by the chemicals in the soils and about the cleanup levels that should be achieved. Knowledge about the rate of release of chemicals is important to answers to such questions. This article: (1) describes a laboratory protocol to obtain rate of release information for chemicals in soils, and (2) provides estimates of the rate of release of individual polyaromatic hydrocarbon (PAH) compounds from several manufactured gas plant (MGP) site soils. The data were analyzed using an empirical two-site model. Different fractions of PAH were released rapidly from these soils. For one soil, this fraction was less than 20%, for others, the fraction ranged from 36 to 85%. The first-order rate constant (k2) of PAH released during the slow phase of chemical release ranged from 0.0001 to 0.01 per hour.     

Human Risk Assessment of Contaminated Soils by Oil Products: Total TPH Content Versus Fraction Approach

Petroleum hydrocarbons may cause risks for humans and the environment that must be properly managed. Some methodologies cluster hundreds of hydrocarbon substances into one single parameter, total petroleum hydrocarbon (TPH) ranged from C10 to C40. Several national policies establish a maximum acceptable concentration in soil to directly consider if a site is seriously contaminated; this scope may be described as a total content approach. Another approach considers TPH division into fractions according to their physico-chemical and toxicological properties, performed in terms of the environmental behavior (aliphatic and aromatic compounds) and the equivalent carbon number (EC). This approach lets us determine the associated risk for human health through the Human Risk Index (HRI). The consequences of application of the total content and fraction approaches is discussed in this study, evaluating the differences in the approach for volatile and semi-volatile hydrocarbons and also in regard to the origin of the contamination. When focusing on volatile substances, the fraction approach is much more restrictive than the total content approach where all oil products are assessed in the same way. When assessing semi-volatile hydrocarbons, their behavior varies depending on the oil product. This work contributes to the implementation of risk-based assessment for petroleum hydrocarbons.