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。     

化学氧化技术对微生物修复石油污染土壤的强化作用研究

微生物修复技术由于其经济性和环境友好性在石油污染修复领域得到广泛应用，利用化学氧化技术可有效提高微生物修复效率。本研究以油泥污染土壤为研究对象，利用化学氧化—微生物联合技术开展修复研究，对比分析单一修复方法和联合修复法的修复效果。研究结果表明，利用化学氧化—微生物联合法去除石油烃的效率要优于化学氧化法和微生物法，最高去除率为48.82%，反应时间越长时，联合修复技术的优势越明显。研究结果可为联合修复技术在石油污染土壤治理方面的推广应用提供参考依据。     

浅析生物修复技术在石油污染治理中的应用

生物修复技术是目前人们比较关注的一种新型石油污染治理技术。文章简要介绍了生物修复技术在石油污染的土壤、河流、湖泊、地下水、海洋领域的应用,阐述了该技术的研究将大力推进生物高科技的发展,对环保科技的发展具有重大意义。     

石油污染土壤修复技术研究进展

研究高效、环保、低成本的石油污染土壤修复技术对石油开发场地修复具有重要的现实应用意义。从工艺和原理两个方面介绍和总结了焚烧法、洗涤法、气相抽提法、化学氧化法、微生物和植物法修复的研究现状及发展趋势。对上述工艺进行比较,总结出各类工艺的优缺点及使用范围。由于污染场地的地质结构、气候条件和污染程度等情况复杂,仅靠单一工艺很难达到预期目标,有必要对已有技术进行完善并开发组合土壤修复技术及设备,满足实际工程的需求。     

石油污染土壤生物修复技术的研究进展

本文综述了30多年来国内外石油污染土壤的生物修复的进展，并介绍了国内外在修复石油污染土壤方面的生物修复工艺：原位生物修复和异位生物修复。原位修复有原位地耕法和土壤气相抽提；异位修复有土壤耕作发、堆放法、堆肥法和反应器法。文章还就今后的研究方向作了阐述，指出生物修复方法作为一种费用低、效果好、对环境影响低、无二次污染的方法，是今后治理石油对土壤污染的最可行的方法。     

石油污染土壤生物修复技术的研究进展

目前对石油污染环境的治理方法有物理法、化学法和生物修复三种类型。文章综合论述了国内外对石油污染土壤的几种微生物修复方法,分别介绍了利用植物、动物及微生物进行治理的修复技术。在我国,对于石油污染的治理应更多地采用低成本、无污染、高效率的生物治理技术。     

表面活性剂强化技术修复石油类污染土壤

介绍了表面活性剂强化修复技术(SER)的原理,并开展SER修复饱和带石油类污染土壤室内研究。经过20d的SER修复,模拟受石油类污染的饱和带土壤,已接近修复终点,土壤中总石油烃(TPH)平均浓度,由初始的13.25g/kg降至4.30g/kg,去除率达到67.54%。表面活性剂强化修复技术对砂土层中石油污染物去除有显著效果。     

石油污染对土壤生态的影响及修复技术分析

土壤修复现已逐渐成为环保领域新的热点。石油类污染物在土壤中迁移转化,使土壤的pH、有机质、含水率、生物群落结构等发生了改变。研究土壤理化性质、非生物因子和生物因子的动态关系是选择最佳修复技术的依据。介绍了目前主要的石油污染土壤修复技术及其优缺点和适用范围,提出理化一生物联用的原位修复技术是未来发展方向;石油污染物复杂多样,可通过构建复合高效菌群提高其生物修复效率。     

石油污染的修复与处理技术

随着工业化进程的不断发展，石油及其制品的污染问题也日趋严重。由于各种原因导致的石油及其制品的泄漏，对土壤和水体造成严重危害，并最终威胁到人类的健康。本文主要介绍了受石油污染环境的几种修复技术及处理方法，比较与分析了各种方法的优点及存在的问题，同时指出了石油污染治理方面的最新研究进展以及发展方向。     

污染土壤淋洗修复技术研究进展

本文介绍了淋洗修复技术和淋洗装置在污染土壤修复技术中的应用,对有机物、重金属及放射性核素污染土壤淋洗修复技术的应用现状进行了总结和评价,还探讨了淋洗修复技术的发展方向及其应用前景。     

污染场地修复技术的种类

本文旨在归纳总结目前国内外对污染场地的修复的各种技术。认为场地修复通常包括污染土修复和含水层净化等2个方面。污染土常见的处理技术目前大致可归纳为6类，即微生物修复技术、化学处理技术、物理分离技术、固化／安定化技术、高温处理技术、植物修复技术等。而污染地下水的修复方法主要有5项：注气法、原位微生物修复技术、两相蒸气提取法、原位氧化法、原位反应墙技术等。     

Phytoremediation of aged petroleum sludge: effect of irrigation techniques and scheduling

The use of higher plants to accelerate the remediation of petroleum contaminants in soil is limited by, among other factors, rooting depth and the delivery of nutrients to the microsites at which remediation occurs. The objective of this study was to test methods of enhancing root growth and remediation in the subsurface of a contaminated petroleum sludge. The phytoremediation of highly contaminated petroleum sludge (total petroleum hydrocarbons >35 g kg(-1) was tested in the greenhouse as a function of the frequency and the depth of irrigation and fertilization. Water and dissolved plant nutrients were added to the soil surface or at a depth of 30 cm, either daily or weekly. Equivalent quantities of water and nutrients were added in all cases. Daily irrigation at a depth of 30 cm invoked greater root growth and enhanced contaminant degradation relative to all other treatments. In the absence of plants, residual concentrations of petroleum hydrocarbons after 7 mo were higher than with plants. The presence of plant roots clearly improved the physical structure of the soil and increased microbial populations. Thus, the plant roots in conjunction with daily additions of soluble N and P appeared to enhance oxygen transport to greater depths in the soil, stimulate petroleum-degrading microorganisms, and provide microbial access to soil micropores. Subsurface irrigation with frequent, small amounts of water and nutrients could significantly accelerate phytoremediation of field soils contaminated with petroleum hydrocarbons.     

黄土高原地区石油类非点源污染试验研究

石油类非点源污染基本特征为污染源分散、污染源作用周期长、暴雨时易于形成高含沙水流以及由此引发的高强度石油类污染。试验结果表明,随土壤石油污染强度的提高,径流量增大,产沙量降低,但水、固两相中的污染物径流污染强度均增大。试验条件下,径流过程释放于水相中的石油类浓度可高达4～7 mg/L。     

Isolation of a novel yeast strain Candida digboiensis TERI ASN6 capable of degrading petroleum hydrocarbons in acidic conditions

A novel yeast species Candida digboiensis TERI ASN6 was isolated from soil samples contaminated with acidic oily sludge (pH 1–3) from the Digboi refinery (Northeast India). The strain TERI ASN6 could degrade 73% of the total petroleum hydrocarbons present in the medium at pH 3 in a week. This strain presents a dimorphic behaviour and showed mycelia morphology when grown under stressed conditions such as low pH and in a medium containing petroleum hydrocarbons. The C. digboiensis strain could efficiently degrade the aliphatic and aromatic fractions of the acidic oily sludge at pH 3 as confirmed by gas chromatography. During the growth of TERI ASN6 in dibenzothiophene (DBT), DBT-sulfone and biphenyl-2-ol were detected. An active cytochrome P450 system, implicated in hydrocarbon oxidation, was also detected in this yeast using degenerated primers based on its conserved regions. This yeast is a potential candidate for petroleum bioremediation treatment of hydrocarbon contaminated acidic soils. Its physiological behaviour allows the strain to work efficiently where other hydrocarbon-degrading bacteria may not survive.     

应用植物重金属超富集机理修复土壤复合污染的研究现状与展望

超积累植物在修复土壤重金属污染中起着重要的作用，但由于重金属复合污染的存在，许多植物并未能完全适用于实际修复中。本文通过阐述土壤重金属复合污染，参考近年来国际上对超积累植物富集机理的研究，从土壤重金属复合污染自身的交互作用，超积累植物根系活化机理，吸收和运输通道机制，金属配位体的运输与解毒作用，以及细胞分室化现象等各个阶段探讨与展望土壤重金属复合污染修复研究问题。     

Annexing Marginal Soils for Agricultural Cultivation Using an Organic Source of Fertilizer as a Bioremediation Treatment Option

This study was carried out to ascertain the practicability of using bioremediated, engine‐oil‐impacted soil for crop cultivation. In this study, bioremediation by land farming and nutrient enhancement was used to treat contaminated soils. In the laboratory, soil samples were homogenized, analyzed, and placed into several reactor vessels including a substrate of poultry droppings and cow dung in various ratios to the contaminated soil. During the first phase of the investigation, contaminated soil without treatment served as a control. The soil matrix was homogenized on a weekly basis, and samples were drawn during the third, fifth, eighth, tenth, and fifteenth weeks for total petroleum hydrocarbon (TPH) reduction and nutrients analysis. The initial concentrations of TPH were diluted upon the addition of the poultry litter and cow dung substrate. Results obtained during the experiment indicate that the amount of nutrients generally decreased as the weeks progressed, and the TPH degradation ranged from 78.27% to 61.84% in the reactor vessels. There was no significant difference (p < .05) in TPH degradation based on the substrate quantities, whereas the TPH reductions in the soil amended with the animal wastes were significantly different from the control sample (soil not amended with animal wastes). In the planting phase, uncontaminated, loamy soil was used as a control (the planting phase control), and the results show that maize planted on the treated soil germinated with no significant difference (p < .05) in the number of leaves and plant heights between the treated samples and the control sample (uncontaminated loamy soil). Analysis of field‐scale animal waste requirements for hypothetical TPH contaminated soil covering a certain area shows that inorganic fertilizer application requires lesser quantities with lower costs than using poultry litter and cow dung to supply nutrients to support bioremediation. The study concludes that bioremediation for agricultural purpose is feasible, but it can be better implemented if the astronomical quantities of substrates required for field‐scale utilization can be surmounted.     

Efficiency of cassava steep liquor for bioremediation of diesel oil-contaminated tropical agricultural soil

Soil artificially contaminated with diesel oil, treated with cassava steep liquor (CSL) and designated EXPS. Similar polluted soil without CSL amendment (CSS1) and uncontaminated soil (CSS2) served as controls. There were dramatic changes in the physico-chemistry of systems EXPS and CSS1 with utilization of the inorganic nutrients to near-depletion in the former than the latter. In contrast, the properties of CSS2 remained relatively stable throughout the investigated period. Similarly, the population densities of microflora in the polluted soils showed an initial decrease between days 0 and 5 before assuming an increasing trend with percent hydrocarbon-utilizers ranging significantly (P < 0.05) from 0.56 to 6.6, 0.1 to 2.46 and 0.56 to 0.26, respectively for EXPS, CSS1, and CSS2. In EXPS, the residual oil decreased from 98,045 to 1,102.3 mg/kg soil at day 35 representing about 98.88% degradation. The corresponding value for CSS1 was 98,106.1 to 52,110 mg/kg soil, amounting to 46.88% oil disappearance. The GC fingerprints of alkane fractions of the recovered oil reduced significantly by day 15 for EXPS with near-similar results of CSS1. However, by day 35, there was complete disappearance of all peaks including the pristane and phytane molecules in the former whereas in CSS1, there were no observable changes. The germination and growth profiles of maize seed plants as evidence of recovery of oil-impacted soils were poor in CSS1 (10%) with pronounced abnormal morphology when compared with the data obtained for EXPS (74%) and CSS2 (80%). These results suggest that CSL could be an indispensable tool in bioremediation of environments contaminated with hydrocarbons. The technology of application is simple, rapid and cost-effective and may be appropriate for use in developing countries to ameliorate the problems of petroleum pollution.     

石油烃污染地下水的修复

地下水受石油烃类污染以其污染普遍、危害性巨大、去除困难以及治理费用昂贵而受到各国环境学者和水文地质学者的关注。概述了石油烃污染地下水处理技术的进展，并对今后研究发展趋势进行了讨论。     

Degradation of polycyclic aromatic hydrocarbons by combined chemical pre-oxidation and bioremediation in creosote contaminated soil

The ability of pre-oxidation to overcome polycyclic aromatic hydrocarbons (PAH) recalcitrance to biodegradation was investigated in creosote contaminated soil. Sand and peat artificially spiked with creosote (quality WEI C) were used as model systems. Ozonation and Fenton-like treatment were proved to be feasible technologies for PAH degradation in soil. The efficiency of ozonation was strongly dependent on the water content of treated soil samples. The removal of PAH by Fenton-like treatment depended on the applied H2O2/soil weight ratio and ferrous ions addition. It was determined that the application of chemical oxidation in sand resulted in a higher PAH removal and required lower oxidant (ozone, hydrogen peroxide) doses. The enhancement of PAH biodegradability by different pre-treatment technologies also depended on the soil matrix. It was ascertained that combined chemical and biological treatment was more efficient in PAH elimination in creosote contaminated soil than either one alone. Thus, the combination of Fenton-like and the subsequent biological treatment resulted in the highest removal of PAH in creosote contaminated sand, and biodegradation with pre-ozonation was found to be the most effective technology for PAH elimination in peat.