汞污染土壤植物修复技术研究进展

汞是一种全球性污染物,汞污染土壤的修复问题,一直倍受各国科学工作者关注,土壤汞污染的植物修复技术是近年来发展起来的新兴技术.其中,汞污染土壤的植物提取技术是最有发展前途的一种汞污染土壤植物修复技术.本文对国内外有关汞污染土壤的植物修复技术进行了系统分析,对有关汞污染土壤的植物修复应用技术,如植物挥发、固化及提取等修复方法进行了评述,探讨了植物修复技术在汞污染土壤修复中的应用前景.加快对汞超积累植物的筛选和植物体对重金属耐性机制的研究,对今后开展汞污染土壤的植物修复工作具有重要的现实意义.     

土壤汞污染生物修复技术研究进展

汞作为常温下唯一的一种液态金属,在环境中分布十分广泛,极易造成土壤污染。生物修复是一种用于土壤汞污染治理的重要修复技术,该技术因具有修复成本低、绿色环保等优点而受到重视。对现有的土壤汞污染生物修复技术进行了评述,主要涉及植物修复技术、微生物修复技术和动物修复技术的研究和应用情况:植物修复技术主要研究汞在植物体内代谢机理和规律,微生物修复技术研究侧重于利用外源微生物降解土壤中汞,动物修复技术研究较少,目前仅见有关蚯蚓富集汞的报道。现代生物修复技术已经发展成为一门包括土壤化学、植物生物学、生态学、土壤微生物学、分析化学及分子生物学等多学科融合性技术,借助这些学科力量可以对植物提取汞根际微界面过程和植物体内微界面过程、微生物和动物汞富集机制有更深刻的认识。综述最后对目前土壤汞污染生物修复技术主要研究方向进行总结和归纳,明确了汞污染生物修复领域存在的几大问题以及研究方向。     

转基因植物对有机污染物的吸收、转化和降解

有机污染物是土壤、水体和大气环境的重要污染物.利用和加强植物修复作用是控制环境污染的有效途径.近年来,一些具有修复功能的外源基因被陆续引入到植物中,使转基因植物的生物修复能力大大增强.文章介绍了植物对污染环境中有机污染物,尤其是持久性有机污染物(POPs)的吸收、转化和降解作用,阐述了转基因植物用于被污染环境修复方面的研究进展和应用前景.     

生物基因技术修复石油污染土壤研究进展

植物修复油污土壤是控制环境污染的有效途径,但在实际应用中存在着植物生物量较小、生长缓慢等不足。将具有修复功能的外源基因引入植物中,使转基因植物的生物修复功能大大增强,为解决土壤石油污染问题提供了有效手段。文章系统论述了转基因植物对石油污染土壤中有机污染物,尤其是对持久性有机污染物（POPs）的吸收、转化和降解作用以及近年来所取得的突破性进展,并指出了利用生物基因修复技术进行土壤石油污染研究的发展趋势。     

重金属污染的转基因植物修复——原理与应用

污染环境的植物修复技术具有成本低、不造成二次污染等优点。从自然界中寻找用于污染环境修复的超富积植物不仅难度大 ,而且受生物量、生长周期以及地理环境等因素的限制。近几年迅速发展起来的通过转基因植物进行污染环境的修复技术显示了广阔的应用前景。外源基因在植物的高效表达可以提高植物吸收、运输、降解污染物的能力以及修复的效率 ,并可以作为研究不同污染物修复机理的实验系统。以转基因植物修复几种主要的重金属污染为例 ,介绍了转基因植物修复的原理、现状及存在问题 ,并探讨了提高转基因植物修复效率的一些方法 。     

重金属污染土壤的植物修复技术

土壤受重金属污染的状况在国内外都相当严重,传统的重金属污染土壤的修复技术存在许多难以克服的缺陷;近年来,一种运用植物来去除有毒重金属的新兴修复技术(植物修复技术)给这一问题提供了良好的解决途径,该技术被认为是一种低成本有效的“绿色”技术.但其主要缺点是修复周期较长,筛选、培育超积累植物以及提高土壤中重金属的生物有效性是提高植物吸收效果、缩短修复周期的关键.本文就超积累植物的筛选、转基因超积累植物及螯合剂强化植物吸收等热点问题的研究进展作了介绍,并对我国当前植物修复技术研究工作的重点提出了建议.     

重金属污染环境的植物修复及其分子机制

重金属污染物的排放和扩散造成了日益严重的环境污染。如何消除环境中的重金属污染物已成为国际性难题。近年来,植物修复技术的出现和快速发展为我们展示了一条新的有效途径：即利用植物对重金属化合物的吸收、富集和转化能力去除土壤和水体中残存的重金属污染物。文章简要介绍了重金属污染物与植物修复的关系和植物修复的生理机制,重点总结了重金属污染环境的植物修复在分子生物学方面所取得的研究进展,包括有机汞裂解酶基因merB、汞离子还原酶基因merA和金属硫蛋白基因MT等的生物学功能及其在植物修复上的应用,展望了植物修复研究工作的发展方向,并针对汞污染提出了一套修复方案。     

用转基因植物修复重金属污染的土壤

将新的性状转入高生物量植物中,以此开发高效的转基因植物修复系统,用于重金属污染的土壤修复是一项具有广阔应用前景的技术.大量实验表明,将细菌、真菌、动物、人类及植物本身与重金属脱毒相关的基因转入高生物量植物,异源表达产物可介导转基因植物耐受和高积累重金属及类似物.综述了这方面的研究进展.     

持久性有机污染土壤的植物修复及其机理研究进展

随着人类对化学品的依赖程度越来越高,环境的有机污染状况也越来越严重.有机污染土壤的植物修复是指利用植物在生长过程中,吸收、降解、钝化有机污染物的一种原位处理污染土壤的方法,具有应用成本低、生态风险小、对环境副作用小等特点.本文综述了近年来国内外有机污染土壤的植物修复研究进展情况,重点介绍了多氯联苯、多环芳烃、农药和硝基芳香化合物等持久性有机污染物的植物修复,阐述了有机污染土壤植物修复的关键机制,并分析了该技术在实际工程应用中的局限性及应考虑的因素.最后,指出了今后该领域的重点研究方向.     

土壤氟形态与氟污染土壤修复

我国土壤氟污染问题严峻,给部分地区人体健康和生态安全造成严重威胁,但土壤氟污染与防治问题仍没有受到人们的广泛关注.本文概述了土壤中氟的存在形态以及发生的主要化学反应,综述了近年来国内外有关氟污染土壤修复的研究进展,提出了今后氟污染土壤修复的研究方向,以期为氟污染土壤的修复提供借鉴和参考.土壤中氟主要分为5种形态,其中90%以上以残渣态存在,土壤溶液中的氟主要发生沉淀-溶解、络合-解离和吸附-解吸等反应来维持水-土系统中的氟平衡.目前,氟污染土壤修复技术研究主要集中在化学固定修复技术、化学淋洗技术、电动修复技术以及植物修复技术.今后需要重点研究氟在土壤中的赋存形态及其影响因子,筛选功能微生物和植物,开发联合修复技术以修复氟污染土壤.     

Acclimation of subsurface microbial communities to mercury

We studied the acclimation to mercury of bacterial communities of different depths from contaminated and noncontaminated floodplain soils. The level of mercury tolerance of the bacterial communities from the contaminated site was higher than those of the reference site. Furthermore, the level of mercury tolerance and functional versatility of bacterial communities in contaminated soils initially were higher for surface soil, compared with the deeper soils. However, following new mercury exposure, no differences between bacterial communities were observed, which indicates a high adaptive potential of the subsurface communities, possibly due to differences in the availability of mercury. IncP-1 trfA genes were detected in extracted community DNA from all soil depths of the contaminated site, and this finding was correlated to the isolation of four different mercury-resistance plasmids, all belonging to the IncP-1beta group. The abundance of merA and IncP-1 plasmid carrying populations increased, after new mercury exposure, which could be the result of selection as well as horizontal gene exchange. The data in this study suggest a role for IncP-1 plasmids in the acclimation to mercury of surface as well as subsurface soil microbial communities.     

Ecological strategy for soil contaminated with mercury

Aims

The paper presents results from plot experiments aimed at the development of an ecological strategy for soil contaminated with mercury. Meadow grass (Poa pratensis) was tested on mercury contaminated soil in a former chlor-alkali plant (CAP) in southern Poland for its phytoremediation potential.

Methods

The stabilisation potential of the plants was investigated on plots without additives and after the addition of granular sulphur. Biomass production, uptake and distribution of mercury by plants, as well as leachates and rhizosphere microorganisms were investigated, along with the growth and vitality of plants during one growing season.

Results

The analysed plants grew easily on mercury contaminated soil, accumulating lower amounts of mercury, especially in the roots, from soil with additive of granular sulphur (0.5 % w/w) and sustained a rich microbial population in the rhizosphere. After amendment application the reduction of Hg evaporation was observed.

Conclusions

The obtained results demonstrate the potential of using Poa pratensis and sulphur for remediation of mercury contaminated soil and reduction of the Hg evaporation from soil. In the presented study, methods of Hg reduction on “hot spots” were proposed, with a special focus on environmental protection. This approach provides a simple remediation tool for large areas heavily contaminated with mercury.

     

香根草及添加剂对模拟降雨条件下汞污染土壤和矿渣地表径流中汞含量的影响

通过盆栽试验,模拟降雨研究香根草(Vetiveria zizanioides)及添加剂(木屑、腐殖土)对汞污染土壤和汞矿渣中汞通过地表径流向周围迁移的影响,结果显示:(1)颗粒态汞占地表径流总汞的80%以上,是汞进行迁移的最主要途径.(2)在汞污染土壤中直接种植香根草,或者将香根草分别与木屑或腐殖土结合,能有效减少地表径流中的总汞(63%～85%)、颗粒态汞(63%～85%)和可溶态汞(27%～73%)向周围环境迁移,其效果显著高于直接在污染土壤中添加单一的木屑(5%)或腐殖土(23%).(3)在矿渣中直接添加低汞土壤或木屑、或直接种植香根草,或将香根草分别与低汞土壤、木屑、腐殖土结合均能有效固定矿渣中的总汞(29%～82%)、颗粒态汞(27%～84%)和可溶态汞(20%～70%).     

Mercury in waterfowl from a contaminated river in Virginia

Many bodies of water around the world are contaminated with mercury from historic industrial and mining activities or ongoing atmospheric deposition, resulting in numerous fish consumption advisories. However, concerns about mercury have only rarely led to consumption advisories on waterfowl. In contrast with fish, waterfowl frequently disperse long distances to new watersheds, so hunters and wildlife managers do not know whether waterfowl at a pristine site have spent time at a contaminated site elsewhere. We sampled tissue mercury concentrations of mallards (Anas platyrhynchos), wood ducks (Aix sponsa), and Canada geese (Branta canadensis) at a site contaminated with mercury, during the breeding and hunting seasons. We found that many mallards had bioaccumulated mercury to levels that had the potential to produce reproductive effects and exceeded consumption advisories set for fish by regulatory agencies, whereas this was true for only a few wood ducks and Canada geese. We also documented that mercury-exposed waterfowl from this contaminated site were harvested by hunters as far as 1,054 km away. Our results suggest the need for more proactive sampling of waterfowl for mercury, and likely other bioaccumulating contaminants, in order to allow hunters to make more informed choices about consumption of their harvest. © 2012 The Wildlife Society.     

Mercury in Plants from Fields Surrounding a Contaminated Channel of Ria de Aveiro,Portugal

Samples of plants and soil were collected in March and June 1995 at 12 sites in fields surrounding the Estarreja Channel (Ria de Aveiro), where the mercury-rich effluent of a chlor-alkali plant has been discharged since the 1950s. Mercury concentrations in soil ranged from 0.64 to 182 μ g g^?1. The highest values were attributed to soil contaminated with sediments dredged from the Estarreja Channel. Plant roots contained between 0.03 and 3.2 μ g g^?1 of total mercury, and there is evidence that root systems uptake mercury from the soil. The linear relationship between mercury concentrations in the roots of Holcus lanatus and in soil over a wide range of mercury concentrations suggests that mercury uptake depends on the element's concentration in the soil. The ratio root:soil concentrations for the analyzed plants varied between 0.003 and 0.199, indicating varying mercury uptake by the root systems. Levels of mercury in the aerial parts of plants showed no clear relationship with the values found in soil or in roots, presumably being influenced mostly by the atmospheric deposition of airborne particles or absorption of atmospheric mercury.     

Diseases of the gladiolus: II. Experiments on dry rot disease caused by Sclerotinia gladioli Drayt

Inoculation experiments show that (1) young corms are more susceptible than old and become less susceptible as they develop, (2) infection of unwounded corms readily takes place, (3) inoculation of the top of an old corm is more effective than that of the side or base.
The percentage diseased new corms produced from infected parent corms varies from o to 100 according to soil conditions. Disease is favoured by wet soil.
Removal of 'husks' (leaf bases) increases the susceptibility of corms planted in contaminated soil, but the presence of husks is not an effective control. Dehusking did not increase the number of diseased young corms in an infected stock planted in new soil.
No variety was strikingly more resistant than the rest.
Good control was obtained when, corms of a diseased stock were treated with mercuric chloride, mercurous chloride (calomel) or the proprietary mercury fungicide Aretan. Calomel gave the most consistent results. Various other treatments were tested in small-scale trials with some success. Red copper oxide, formalin and the proprietary mercury compound, Ceresan, were harmful.
Sterilization of contaminated soil with formalin, mercuric chloride, Aretan or Uspulun gave good but not complete control. Formalin was the least effective.     

Assessing the applicability of phytoremediation of soils with mixed organic and heavy metal contaminants

Soil pollution is a major environmental problem and many contaminated sites are tainted with a mixture of organic and heavy metal contaminants. Compared to other remedial strategies, phytoremediation is a low cost, environmentally-friendly, sustainable means of remediating the contamination. This review first provides an overview of phytoremediation studies where the soil is contaminated with just one type of pollutant (heavy metals or organics) and then critically evaluates the applicability of phytotechnologies for the remediation of contaminated sites where the soil is polluted by a mixture of organic and heavy metal contaminants. In most of the earlier research studies, mixed contamination was held to be detrimental to plant growth, yet there were instances where plant growth was more successful in soil with mixed contamination than in the soil with only individual contaminants. New effective phytoremediation strategies can be designed for remediation of co-contaminated sites using: (a) plants species especially adapted to grow in the contaminated site (hyperacumulators, local plants, transgenic plants); (b) endophytic bacteria to enhance the degradation in the rizhosphere; (c) soil amendments to increase the contaminants bioavailability [chelating agents and (bio)surfactants]; (d) soil fertilization to enhance the plant growth and microbial activity in the soil; and (e) coupling phytoremediation with other remediation technologies such as electrokinetic remediation or enhanced biodegradation in the rhizosphere.     

Expression of mercuric ion reductase in Eastern cottonwood (Populus deltoides) confers mercuric ion reduction and resistance

Mercury is one of the most hazardous heavy metals and is a particular problem in aquatic ecosystems, where organic mercury is biomagnified in the food chain. Previous studies demonstrated that transgenic model plants expressing a modified mercuric ion reductase gene from bacteria could detoxify mercury by converting the more toxic and reductive ionic form [Hg(II)] to less toxic elemental mercury [Hg(0)]. To further investigate if a genetic engineering approach for mercury phytoremediation can be effective in trees with a greater potential in riparian ecosystems, we generated transgenic Eastern cottonwood (Populus deltoides) trees expressing modified merA9 and merA18 genes. Leaf sections from transgenic plantlets produced adventitious shoots in the presence of 50 microm Hg(II) supplied as HgCl2, which inhibited shoot induction from leaf explants of wild-type plantlets. Transgenic shoots cultured in a medium containing 25 microm Hg(II) showed normal growth and rooted, while wild-type shoots were killed. When the transgenic cottonwood plantlets were exposed to Hg(II), they evolved 2-4-fold the amount of Hg(0) relative to wild-type plantlets. Transgenic merA9 and merA18 plants accumulated significantly higher biomass than control plants on a Georgia Piedmont soil contaminated with 40 p.p.m. Hg(II). Our results indicate that Eastern cottonwood plants expressing the bacterial mercuric ion reductase gene have potential as candidates for in situ remediation of mercury-contaminated soils or wastewater.     

The effect of long-term mercury pollution on the soil microbial community

The effect of long-term exposure to mercury on the soil microbial community was investigated in soil from three different sites along a pollution gradient. The amount of total and bioavailable mercury was negatively correlated to the distance from the center of contamination. The size of the bacterial and protozoan populations was reduced in the most contaminated soil, whereas there was no significant difference in fungal biomass measured as chitinase activity. Based on the number of colony morphotypes, moreover, the culturable bacterial population was structurally less diverse and contained a higher proportion of resistant and fast-growing forms. The profiles of amplified 16S rDNA sequences obtained from community DNA by denaturating gradient gel electrophoresis (DGGE) also reflected the altered community structure and decreased diversity along the mercury gradient as expressed in terms of the number and abundance of bands. The functional potential of the microbial population measured as sole carbon source utilization by Ecoplates((R)) differed between the soils, but there was no change in the number of substrates utilized. The observed changes in the different soil microbial populations are probably a combination of both direct and indirect effects of the mercury contamination.     

Versatile biosensor vectors for detection and quantification of mercury

Three different whole cell biosensor constructs were made by fusing the mercury inducible promoter, P(mer), and its regulatory gene, merR, from transposon Tn21 with reporter genes luxCDABE, lacZYA, or gfp. In Escherichia coli these biosensor constructs responded to low levels of mercury by producing light, beta-galactosidase or green fluorescent protein, respectively. Since the responses were quantitative, the constructs were used to quantify bioavailable mercury in different environments. The constructs were cloned into mini-Tn5 delivery vectors, thus enabling the transfer of the mer-lux, mer-lac or mer-gfp cassettes to a variety of Gram-negative bacteria. The mer-lux cassette was transferred to a Pseudomonas putida strain, which was used to quantify water-extractable mercury in contaminated soil.