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.     

植物修复重金属污染土壤的强化措施

植物修复技术作为一种新兴的绿色环保技术,有着高效、经济和生态协调等特点而成为当前研究的热点领域,而且由于其修复的彻底性和环境友好性而在治理污染土壤实地过程得到广泛应用.概述了当前植物修复研究的基本类型和修复机理,并着重从生物技术、农艺措施和物理化学等强化手段上阐述了利用超富集植物修复污染土壤,以进一步提高超富集植物的修复效率,为大规模治理重金属污染土壤和商业化应用提供技术途径和科学依据.     

植物修复技术在地表水污染控制中的应用

介绍了一项新兴的地表水污染治理技术--植物修复技术.该项技术与传统的物理方法和化学方法相比,具有成本低、处理效果好（去除率可达99%以上）、对环境扰动小、操作简便、在处理设备和处理规模上没有限制等优点.这些优点决定了植物修复技术在地表水污染治理中具有很好的应用前景.综述了国内外植物修复技术的研究进展,并对该项技术的发展趋势进行了探讨.     

植物修复及重金属在植物体内形态分析综述

植物修复是重金属污染土壤治理的重要方法,因其具有高效、经济及生态协调性等优势而广受关注。当前相关研究主要包括超积累植物体内重金属的迁移转化与形态分析方法,土壤修复后植物的减量化、无害化和资源化利用等方面。实验研究及修复工程中存在的问题主要体现为:(1)基础研究方面,目前对植物超积累重金属的分子机制、调控原理等方面的研究不够完善;(2)应用技术方面,修复植物的规模化种植、适用的栽培技术、收获物安全处置及资源化利用方面仍是植物修复技术发展的瓶颈。因此,目前需要深入研究超积累植物吸收、运输和积累重金属的生理机制,利于植物生长的农业措施以及用于修复的植物收获后的相应处理技术。同时,应结合重金属在植物体内的形态,对修复后的植物进行合理的减量化、无害化、资源化处理,以便于更加科学合理地选择土壤重金属修复植物,大规模推广植物修复技术的应用。     

重金属污染土壤植物修复及进展

土壤污染是当今面临的一个重要环境问题。常规的土壤污染物理化学治理技术 ,如客土换土法、冲洗法、热处理、固化、玻璃化、动电修复法等 ,由于其技术要求高或经济成本高昂 ,对土壤结构的扰动破坏较严重 ,因而 ,大规模推广应用存在较大问题。重金属超累积植物的不断发现 ,使人们认识到有可能利用植物于土壤污染的治理修复。自 2 0世纪 90年代起 ,植物修复成为环境污染治理研究领域的一个前沿性课题。研究表明 ,通过植物的吸收、挥发、根滤、稳定等作用 ,可以净化土壤或水体中金属污染物 ,达到净化环境的目的。近 10年来 ,在超累积植物的找寻培育、植物根际微生物共存体系研究、植物对重金属的耐忍性、超量吸收及其解毒机制以及植物修复的工艺技术方面已有不少研究 ,并取得长足的进展 ,现代分子生物学的发展以及基因工程技术的应用有可能使植物修复技术取得根本性的突破。     

重金属污染土壤的植物修复技术与其他技术联用的进展与前景

随着工业和经济的发展,土壤重金属污染越来越严重,因此重金属污染土壤的修复迫在眉睫。植物修复技术因其经济、环保等优点已经成为国内外研究的热点,但存在修复植物稀少的问题。将其他技术与植物修复技术联用可能是突破植物修复这一局限性的关键举措之一。介绍了基因工程技术与植物修复技术联用的研究进展;总结了微生物技术与植物修复技术联用中植物根际促生细菌、菌根真菌的作用;概述了材料化学技术联合植物修复的应用现状,着重介绍了土壤改良剂和螯合剂的实际应用。最后对基因工程、微生物、材料化学等技术联合植物修复技术在研究和应用中的未来方向进行了前景展望,旨在为植物修复技术发展提供更多新的思路和参考。     

重金属污染土壤植物修复及进展

土壤污染是当今面临的一个重要环境问题。常规的土壤污染物化学治理技术，如客土换土法、冲洗法、热处理、固化、玻璃化、动电修复法等，由于其技术要求高或经济成本高昂，对土壤结构的扰动破碎较严重，因而，大规模推广应用存在较大问题。重金属超累积植物的不断发现，使人们认识到有可能利用植物于土壤污染的治理修复。自20世纪90年代起，植物修复成为环境污染治理研究领域的一个前沿性课题。研究表明，通过植物的吸收、挥发、根滤、稳定等作用，可以净化土壤或水体中金属污染物，达到净化环境的目的。近10年来，在超累积植物的找寻培育、植物根际微生物共存体系研究、植物对重金属的耐忍性、超量吸收及其解毒机制以及植物修复的工艺技术方面已有不少研究，并取得长 的进展，现代分子生物学的发展以及基因工程技术的应用有可能使植物修复技术取得根本性的突破。     

多环芳烃的毒性及其治理技术研究

多环芳烃（PAHs）是一类长久存在于环境中,具有致癌、致畸与致突变等特性的环境优先污染物。文中概括介绍了PAHs的来源、毒性及毒理,重点阐述了目前国内外对PAHs污染采取的处理方法及治理技术,包括微生物修复、植物修复和微生物-植物联合修复等。     

利用植物修复污染土壤研究进展

本文介绍了植物修复技术的概念及其内涵，回顾了植物修复技术的研究历史，对该项技术的国内外研究现状与未来发展方向进行了讨论。同时指出，植物修复技术优点与其局限性。文中还对利用植物修复重金属污染的土壤应该考虑的因素作了简单的讨论     

生物修复高氯酸盐污染的研究进展

生物修复技术是目前高氯酸盐污染环境整治的最具潜力的修复技术之一,具有成本低、无二次污染的特点,是国内外一个新的研究热点,亦是仅见的污染控制及修复的环境友好技术。介绍了环境中高氯酸盐污染的来源与分布,阐述了生物修复(主要包括植物修复和微生物修复)的特点及作用机制,认识到2种类型修复技术各有其优劣势;重点综述了生物修复高氯酸盐污染的国内外研究现状,得出植物根际降解对植物修复高氯酸盐起着十分重要作用,而微生物修复是目前最有希望获得大规模应用的高氯酸盐污染修复技术;最后提出了植物-微生物联合强化修复高氯酸盐污染的技术将更具应用前景。     

Phyto-products may be essential for sustainability and implementation of phytoremediation

Interest in selenium pollution and remediation technology has escalated during the past two decades. Although not known to be essential for plants, selenium is essential but could be toxic for humans and animals, depending on its concentration. A major selenium controversy in the 1980's emerged in California when the general public and scientific community became aware of selenium's potential as an environmental contaminant. After extensive research on several strategies to reduce loads of mobile Se for entering the agricultural ecosystem a plant-based technology, defined as 'phytoremediation' received increasing recognition, as a low-cost environmentally friendly approach for managing soluble Se in the soil and water environment. Successful long-term field remediation of Se by plants is, however, dependent upon acceptance and widespread use by growers, who are also concerned about potential commercial value from using the plant-based technology. Obtaining products with economic value from plants used in the cleanup of soil would certainly be an additional benefit to phytoremediation, which could help sustain its long-term use.     

The potential of the flora from different regions of Pakistan in phytoremediation: a review

Soil and water quality is greatly affected by environmental pollution due to the increasing trend of urbanization and industrialization. In many developing countries, including Pakistan, the situation is more alarming as no preventive measures are still taken to tackle the problem. Although in developed countries, many techniques are used to remediate the environment including phytoremediation. It is the most eco-friendly technique in which plants are used to remove pollutants from the environment. Pakistan has also a great diversity of plants which could be used for the remediation of environmental pollutants. To our knowledge, few studies from Pakistan were reported about the use of flora for phytoremediation. According to recent literature, 50 plant species from Pakistan are studied for remediation purposes. In this review, the potential of different plant species for phytoremediation from Pakistan has been discussed along with their comparison to other countries to relate future perspectives.     

Phytoremediation of contaminated soils and groundwater: lessons from the field

Background, aim, and scope

The use of plants and associated microorganisms to remove, contain, inactivate, or degrade harmful environmental contaminants (generally termed phytoremediation) and to revitalize contaminated sites is gaining more and more attention. In this review, prerequisites for a successful remediation will be discussed. The performance of phytoremediation as an environmental remediation technology indeed depends on several factors including the extent of soil contamination, the availability and accessibility of contaminants for rhizosphere microorganisms and uptake into roots (bioavailability), and the ability of the plant and its associated microorganisms to intercept, absorb, accumulate, and/or degrade the contaminants. The main aim is to provide an overview of existing field experience in Europe concerning the use of plants and their associated microorganisms whether or not combined with amendments for the revitalization or remediation of contaminated soils and undeep groundwater. Contaminations with trace elements (except radionuclides) and organics will be considered. Because remediation with transgenic organisms is largely untested in the field, this topic is not covered in this review. Brief attention will be paid to the economical aspects, use, and processing of the biomass.

Conclusions and perspectives

It is clear that in spite of a growing public and commercial interest and the success of several pilot studies and field scale applications more fundamental research still is needed to better exploit the metabolic diversity of the plants themselves, but also to better understand the complex interactions between contaminants, soil, plant roots, and microorganisms (bacteria and mycorrhiza) in the rhizosphere. Further, more data are still needed to quantify the underlying economics, as a support for public acceptance and last but not least to convince policy makers and stakeholders (who are not very familiar with such techniques).     

Remediation of BTEX and trichloroethene

The widespread use of industrial chemicals in our highly industrialized society has often caused contamination of large terrestrial and marine areas due to the deliberate and accidental release of organic pollutants into the soil and groundwater. In this review, environmental problems arising from the use of chlorinated solvents and BTEX compounds are described, and an overview about active management strategies for remediation with special emphasis on phytoremediation are presented to achieve a reduction of the total mass of chlorinated solvents and BTEX compounds in contaminated areas. Phytoremediation has been proposed as an efficient, low-cost remediation technique to restore areas contaminated with chlorinated solvents and BTEX compounds. The feasibility of phytoremediation as a remediation tool for these compounds is discussed with particular reference to the uptake and metabolism of these compounds, and a future perspective on the use of phytoremediation for the removal of chlorinated solvents and BTEX compounds is given.     

不同处理条件对石油污染土壤植物修复的影响

针对石油烃植物修复过程中的主要影响因素,研究了不同植物种类、不同土壤调理剂和菌剂使用等不同条件对土壤中石油烃植物修复效果的影响.结果表明,不同种类的植物修复可使总石油烃的年降解率达到37.8％ ～ 73.98％,其中大豆和碱蓬具有较好的修复效果;3种不同土壤调理剂对石油烃污染土壤修复的效果为商业添加剂＞牛粪＞蛭石;先微生物修复后种植植物的处理要优于单独的微生物修复及微生物、植物修复同步进行的处理.     

Establishing best practice for microbially aided phytoremediation

The dispersal of industrial and municipal wastes leads to an increase of contaminated soils and is one of the large concerns in many countries throughout Europe regarding environmental issues. This article proposes a sequence of the microbially aided phytoremediation (phytoextraction and phytostabilization) procedure with the following most important steps: (1) risk assessment, (2) site investigation, (3) determination of the remediation strategy, (4) realization of remediation measures, (5) monitoring, and (6) reuse of the remediated site. UMBRELLA's innovative approach is a proposal of methods to evolve a tool-box which supports phytoremediation by means of microbes and enhances the efficiency of the remediation process at low and heterogeneously metal contaminated sites.     

Electrokinetic-enhanced phytoremediation of soils: Status and opportunities

Phytoremediation is a sustainable process in which green plants are used for the removal or elimination of contaminants in soils. Both organic and inorganic contaminants can be removed or degraded by growing plants by several mechanisms, namely phytoaccumulation, phytostabilization, phytodegradation, rhizofiltration and rhizodegradation. Phytoremediation has several advantages: it can be applied in situ over large areas, the cost is low, and the soil does not undergo significant damages. However, the restoration of a contaminated site by phytoremediation requires a long treatment time since the remediation depends on the growth and the biological cycles of the plant. It is only applicable for shallow depths within the reach of the roots, and the remediation efficiency largely depends on the physico-chemical properties of the soil and the bioavailability of the contaminants. The combination of phytoremediation and electrokinetics has been proposed in an attempt to avoid, in part, the limitations of phytoremediation. Basically, the coupled phytoremediation–electrokinetic technology consists of the application of a low intensity electric field to the contaminated soil in the vicinity of growing plants. The electric field may enhance the removal of the contaminants by increasing the bioavailability of the contaminants. Variables that affect the coupled technology are: the use of AC or DC current, voltage level and mode of voltage application (continuous or periodic), soil pH evolution, and the addition of facilitating agents to enhance the mobility and bioavailability of the contaminants. Several technical and practical challenges still remain that must be overcome through future research for successful application of this coupled technology at actual field sites.