Evaluation of Transgenic Poplars Over-Expressing Enzymes of Glutathione Synthesis for Phytoremediation of Cadmium

Abstract: Recently, phytoremediation of soils polluted with heavy metals has received a lot of attention. Since glutathione (GSH) and its derivatives (e.g., phytochelatins) play a major role in plant defence against environmental pollutants, we tested the effects of over-expression of bacterial genes for GSH synthesis in poplar on cadmium accumulation. A pilot experiment with CdCl₂ in hydroponics revealed that poplars over-expressing γ-glutamylcysteine synthetase (γ-ECS) accumulated significantly more Cd in root tissue than wild type or glutathione synthetase over-expressing poplars. To test the partitioning of Cd in different organs, poplar lines over-expressing γ-ECS in the cytosol and in chloroplasts were treated with 0.2 mM CdCl₂ in hydroponics. Significant amounts of Cd were translocated to leaves, but significant differences in Cd accumulation were not observed between transgenic and wild type plants. To evaluate these lines for large-scale phytoremediation of cadmium, plants were treated with 2 mM Cd in soil. Over a four-week period, the poplar plants were able to accumulate up to 5.3 mg Cd. Most remarkably, in young leaves of both transgenic lines, Cd was accumulated to concentrations 2.5 - 3 times higher than in the wild type. The increased allocation of cadmium to the young leaves represents a potentional advantage for the phytoremediation process using the same plants over several vegetation periods. The use of transgenic poplar lines with enhanced glutathione production capacity seems to be of particular advantage in highly polluted soils.     

Enhanced tolerance of transgenic poplar plants overexpressing gamma-glutamylcysteine synthetase towards chloroacetanilide herbicides.

A wild-type poplar hybrid and two transgenic clones overexpressing a bacterial gamma-glutamylcysteine synthetase in the cytosol or in the chloroplasts were exposed to the chloroacetanilide herbicides acetochlor and metolachlor dispersed in the soil. The transformed poplars contained higher gamma-glutamylcysteine and glutathione (GSH) levels than wild-type plants and therefore it was supposed that they would have an elevated tolerance towards these herbicides, which are detoxified in GSH-dependent reactions. Phenotypically, the transgenic and wild-type plants did not differ. The growth and the biomass of all poplar lines were markedly reduced by the two chloroacetanilide herbicides. However, the decrease of shoot and root fresh weights caused by the herbicides was significantly smaller in the transgenic than in wild-type plants. In addition, the growth rate of poplars transformed in the cytosol was reduced to a significantly lesser extent than that of wild-type plants following herbicide treatments. The effects of the two herbicides were similar. Herbicide exposures markedly increased the levels of gamma-glutamylcysteine and GSH in leaves of each poplar line. The increase in the foliar amounts of these thiols was stronger in the transgenic lines than in the wild type, particularly in the upper leaves. Considerable GST activities were detected in leaves of all poplar plants. Exposure of poplars to chloroacetanilide herbicides resulted in a marked induction of GST activity in upper leaf positions but not in middle and lower leaves. The extent of enzyme induction did not differ significantly between transgenic and wild-type poplars. Although the results show that the transgenic poplar lines are good candidates for phytoremediation purposes, the further improvement of their detoxification capacity, preferably by transformation using genes encoding herbicide-specific GST isoenzymes, seems to be the most promising way to obtain plants suitable for practical application.     

Chloroplast parameters differ in wild type and transgenic poplars overexpressing gsh1 in the cytosol

Poplar mutants overexpressing the bacterial genes gsh1 or gsh2 encoding the enzymes of glutathione biosynthesis are among the best‐characterised transgenic plants. However, this characterisation originates exclusively from laboratory studies, and the performance of these mutants under field conditions is largely unknown. Here, we report a field experiment in which the wild‐type poplar hybrid Populus tremula × P. alba and a transgenic line overexpressing the bacterial gene gsh1 encoding γ‐glutamylcysteine synthetase in the cytosol were grown for 3 years at a relatively clean (control) field site and a field site contaminated with heavy metals. Aboveground biomass accumulation was slightly smaller in transgenic compared to wild‐type plants; soil contamination significantly decreased biomass accumulation in both wild‐type and transgenic plants by more than 40%. Chloroplasts parameters, i.e., maximal diameter, projection area and perimeter, surface area and volume, surface/volume ratio and a two‐dimensional form coefficient, were found to depend on plant type, leaf tissue and soil contamination. The greatest differences between wild and transgenic poplars were observed at the control site. Under these conditions, chloroplast sizes in palisade tissue of transgenic poplar significantly exceeded those of the wild type. In contrast to the wild type, palisade chloroplast volume exceeded that of spongy chloroplasts in transgenic poplars at both field sites. Chlorophyll content per chloroplast was the same in wild and transgenic poplars. Apparently, the increase in chloroplast volume was not connected to changes in the photosynthetic centres. Chloroplasts of transgenic poplar at the control site were more elongated in palisade cells and close to spherical in spongy mesophyll chloroplasts. At the contaminated site, palisade and spongy cell chloroplasts of leaves from transgenic trees and the wild type were the same shape. Transgenic poplars also had a smaller chloroplast surface/volume ratio, both at the control and the contaminated site. Chloroplast number per cell did not differ between wild and transgenic poplars at the control site. Soil contamination led to suppression of chloroplast replication in wild‐type plants. From these results, we assume that overexpressing the bacterial gsh1 gene in the cytosol interacts with processes in the chloroplast and that sequestration of heavy metal phytochelatin complexes into the vacuole may partially counteract this interaction in plants grown at heavy metal‐contaminated field sites. Further experiments are required to test these assumptions.     

Effect of genetically modified poplars on soil microbial communities during the phytoremediation of waste mine tailings

The application of transgenic plants to clean up environmental pollution caused by the wastes of heavy metal mining is a promising method for removing metal pollutants from soils. However, the effect of using genetically modified organisms for phytoremediation is a poorly researched topic in terms of microbial community structures, despite the important role of microorganisms in the health of soil. In this study, a comparative analysis of the bacterial and archaeal communities found in the rhizosphere of genetically modified (GM) versus wild-type (WT) poplar was conducted on trees at different growth stages (i.e., the rhizospheres of 1.5-, 2.5-, and 3-year-old poplars) that were cultivated on contaminated soils together with nonplanted control soil. Based on the results of DNA pyrosequencing, poplar type and growth stages were associated with directional changes in the structure of the microbial community. The rate of change was faster in GM poplars than in WT poplars, but the microbial communities were identical in the 3-year-old poplars. This phenomenon may arise because of a higher rate and greater extent of metal accumulation in GM poplars than in naturally occurring plants, which resulted in greater changes in soil environments and hence the microbial habitat.     

Fungal community associated with genetically modified poplar during metal phytoremediation

Due to the increasing demand for phytoremediation, many transgenic poplars have been developed to enhance the bioremediation of heavy metals. However, structural changes to indigenous fungal communities by genetically modified organisms (GMO) presents a major ecological issue, due to the important role of fungi for plant growth in natural environments. To evaluate the effect of GM plant use on environmental fungal soil communities, extensive sequencing-based community analysis was conducted, while controlling the influence of plant clonality, plant age, soil condition, and harvesting season. The rhizosphere soils of GM and wild type (WT) poplars at a range of growth stages were sampled together with unplanted, contaminated soil, and the fungal community structures were investigated by pyrosequencing the D1/D2 region of the 28S rRNA gene. The results show that the overall structure of the rhizosphere fungal community was not significantly influenced by GM poplars. However, the presence of GM specific taxa, and faster rate of community change during poplar growth, appeared to be characteristic of the GM plant-induced effects on soil-born fungal communities. The results of this study provide additional information about the potential effects of GM poplar trees aged 1.5–3 years, on the soil fungal community.     

Over-expression of gsh1 in the cytosol affects the photosynthetic apparatus and improves the performance of transgenic poplars on heavy metal-contaminated soil

Recent studies of transgenic poplars over‐expressing the genes gsh1 and gsh2 encoding γ‐glutamylcysteine synthetase (γ‐ECS) and glutathione synthetase, respectively, provided detailed information on regulation of GSH synthesis, enzymes activities and mRNA expression. In this experiment, we studied quantitative parameters of leaves, assimilating tissues, cells and chloroplasts, mesophyll resistance for CO₂ diffusion, chlorophyll and carbohydrate content in wild‐type poplar and transgenic plants over‐expressing gsh1 in the cytosol after 3 years of growth in relatively clean (control) or heavy metal‐contaminated soil in the field. Over‐expression of gsh1 in the cytosol led to a twofold increase of intrafoliar GSH concentration and influenced the photosynthetic apparatus at different levels of organisation, i.e., leaves, photosynthetic cells and chloroplasts. At the control site, transgenic poplars had a twofold smaller total leaf area per plant and a 1.6‐fold leaf area per leaf compared to wild‐type controls. Annual aboveground biomass gain was reduced by 50% in the transgenic plants. The reduction of leaf area of the transformants was accompanied by a significant decline in total cell number per leaf, indicating suppression of cell division. Over‐expression of γ‐ECS in the cytosol also caused changes in mesophyll structure, i.e., a 20% decrease in cell and chloroplast number per leaf area, but also an enhanced volume share of chloroplasts and intercellular airspaces in the leaves. Transgenic and wild poplars did not exhibit differences in chlorophyll and carotenoid content of leaves, but transformants had 1.3‐fold fewer soluble carbohydrates. Cultivation on contaminated soil caused a reduction of palisade cell volume and chloroplast number, both per cell and leaf area, in wild‐type plants but not in transformants. Biomass accumulation of wild‐type poplars decreased in contaminated soil by more than 30‐fold, whereas transformants showed a twofold decrease compared to the control site. Thus, poplars over‐expressing γ‐ECS in the cytosol were more tolerant to heavy metal stress under field conditions than wild‐type plants according to the parameters analysed. Correlation analysis revealed strong dependence of cell number per leaf area unit, chloroplast parameters and mesophyll resistance with the GSH level in poplar leaves.     

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.     

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。     

Understanding molecular mechanisms for improving phytoremediation of heavy metal-contaminated soils

Heavy metal pollution of soil is a significant environmental problem with a negative potential impact on human health and agriculture. Rhizosphere, as an important interface of soil and plants, plays a significant role in phytoremediation of contaminated soil by heavy metals, in which, microbial populations are known to affect heavy metal mobility and availability to the plant through release of chelating agents, acidification, phosphate solubilization and redox changes, and therefore, have potential to enhance phytoremediation processes. Phytoremediation strategies with appropriate heavy metal-adapted rhizobacteria or mycorrhizas have received more and more attention. In addition, some plants possess a range of potential mechanisms that may be involved in the detoxification of heavy metals, and they manage to survive under metal stresses. High tolerance to heavy metal toxicity could rely either on reduced uptake or increased plant internal sequestration, which is manifested by an interaction between a genotype and its environment.A coordinated network of molecular processes provides plants with multiple metal-detoxifying mechanisms and repair capabilities. The growing application of molecular genetic technologies has led to an increased understanding of mechanisms of heavy metal tolerance/accumulation in plants and, subsequently, many transgenic plants with increased heavy metal resistance, as well as increased uptake of heavy metals, have been developed for the purpose of phytoremediation. This article reviews advantages, possible mechanisms, current status and future direction of phytoremediation for heavy-metal–contaminated soils.     

Enhanced Heavy Metal Tolerance and Accumulation by Transgenic Sugar Beets Expressing Streptococcus thermophilus StGCS-GS in the Presence of Cd,Zn and Cu Alone or in Combination

Phytoremediation is a promising means of ameliorating heavy metal pollution through the use of transgenic plants as artificial hyperaccumulators. A novel Streptococcus thermophilus γ-glutamylcysteine synthetase-glutathione synthetase (StGCS-GS) that synthesizes glutathione (GSH) with limited feedback inhibition was overexpressed in sugar beet (Beta vulgaris L.), yielding three transgenic lines (s2, s4 and s5) with enhanced tolerance to different concentrations of cadmium, zinc and copper, as indicated by their increased biomass, root length and relative growth compared with wild-type plants. Transgenic sugar beets accumulated more Cd, Zn and Cu ions in shoots than wild-type, as well as higher GSH and phytochelatin (PC) levels under different heavy metal stresses. This enhanced heavy metal tolerance and increased accumulation were likely due to the increased expression of StGCS-GS and consequent overproduction of both GSH and PC. Furthermore, when multiple heavy metal ions were present at the same time, transgenic sugar beets overexpressing StGCS-GS resisted two or three of the metal combinations (50 μM Cd-Zn, Cd-Cu, Zn-Cu and Cd-Zn-Cu), with greater absorption in shoots. Additionally, there was no obvious competition between metals. Overall, the results demonstrate the explicit role of StGCS-GS in enhancing Cd, Zn and Cu tolerance and accumulation in transgenic sugar beet, which may represent a highly promising new tool for phytoremediation.     

Enhanced drought and salt tolerance by expression of AtGSK1 gene in poplar

A GSK3/shaggy-like kinase (AtGSK1) has been implicated in the regulation of drought and salt tolerance. We transferred AtGSK1 from Arabidopsis thaliana to a hybrid poplar (Populus alba × P. tremula var. grandulosa) to determine the effect of the transgene expression in the transgenic trees. The results from northern blot and RT-PCR analyses showed that the expression level varied among the transgenic lines. During their culture on tissue culture media, the transgenic poplars formed vigorous growing roots even in the presence of 125 mM NaCl and callus in the presence of 150 mM NaCl. When the transgenic poplars were growing in pots and provided with NaCl solution, they stayed much healthier than did nontransgenic poplars, showing higher rates of photosynthetic rates, stomatal conductance, and evaporation rates under the stress. Whereas the total level of leaf Na⁺ level increased dramatically in transgenic poplars under severe saline conditions (150 mM NaCl), that of leaf K⁺ decreased in the same plants under the same conditions. Total root Na⁺ level increased in nontransgenic poplars under severe saline conditions. In contrast, total root K⁺ level decreased in the same plants under the same conditions. The chloride content and relative electrical conductivity of the transgenic poplars after salt stress treatment were lower than those of nontransgenic poplars. The transgenic poplars were also tolerant to up to 20 % PEG remaining significantly healthy when compared with nontransgenic poplars with necrosis and chlorosis symptoms. Another dramatic feature of the transgenic poplars was wilting tolerance for prolonged drought treatment up to 2 weeks. The results provide evidence that the expression of AtGSK1 gene conferred drought and salt tolerance in the transgenic poplars.     

Overexpression of Glutathione Synthetase in Indian Mustard Enhances Cadmium Accumulation and Tolerance

An important pathway by which plants detoxify heavy metals is through sequestration with heavy-metal-binding peptides called phytochelatins or their precursor, glutathione. To identify limiting factors for heavy-metal accumulation and tolerance, and to develop transgenic plants with an increased capacity to accumulate and/or tolerate heavy metals, the Escherichia coli gshII gene encoding glutathione synthetase (GS) was overexpressed in the cytosol of Indian mustard (Brassica juncea). The transgenic GS plants accumulated significantly more Cd than the wild type: shoot Cd concentrations were up to 25% higher and total Cd accumulation per shoot was up to 3-fold higher. Moreover, the GS plants showed enhanced tolerance to Cd at both the seedling and mature-plant stages. Cd accumulation and tolerance were correlated with the gshII expression level. Cd-treated GS plants had higher concentrations of glutathione, phytochelatin, thiol, S, and Ca than wild-type plants. We conclude that in the presence of Cd, the GS enzyme is rate limiting for the biosynthesis of glutathione and phytochelatins, and that overexpression of GS offers a promising strategy for the production of plants with superior heavy-metal phytoremediation capacity.     

Phytoremediation efficiency OF CD by Eucalyptus globulus transplanted from polluted and unpolluted sites

The capacity of plants to uptake heavy metals from contaminated soils has shown great phytoremediation potential. The development, resistibility and Cd extraction of Eucalyptus globulus individuals from metalliferous and clean sites in different years were analyzed under a specific environment. Eucalyptus globulus planted in Guiyu for phytoremediation or cultivated in an uncontaminated, natural environment for economic purposes were transplanted to Yuecheng town, which, in recent years, has been involved in the e-waste dismantling and recycling business, to compare the phytoremediation efficiency of Eucalyptus globulus trees grown in different environments. Trees cultivated in polluted areas can remove far more Cd and Hg from the contaminated soil than the individuals from clean soils because metalliferous Eucalyptus globulus can produce more biomass and uptake more heavy metals than nonmetalliferous plants per year. As polluted environments negatively affect the growth of plants, we speculated that the phytoremediation efficiency of metalliferous Eucalyptus globulus should decrease over time and that nonmetalliferous trees should adapt to the local environment.     

Light-dependent modulation of foliar glutathione synthesis and associated amino acid metabolism in poplar overexpressing γ-glutamylcysteine synthetase

Glutathione (GSH), γ-glutamylcysteine (γ-EC) and major free amino acids were measured in darkened and illuminated leaves from untransformed poplars (Populus tremula × P. alba) and poplars expressing Escherichia coli genes for γ-glutamylcysteine synthetase (γ-ECS; EC 3.2.3.3) and glutathione reductase (GR; EC 1.6.4.2). In poplars overexpressing γ-ECS, foliar γ-EC contents and GSH contents were markedly enhanced compared to poplars lacking the bacterial gene for the enzyme. However, the quantitative relationship between the foliar pools of γ-EC and GSH in these transformants was markedly dependent on light. In the dark, GSH content was relatively low and γ-EC content high, the latter being higher than the foliar GSH contents of untransformed poplars in all conditions. Hence, this transformation appears to elevate γ-EC from the ranks of a trace metabolite to one of major quantitative importance. On illumination, however, γ-EC content decreased fourfold whereas GSH content doubled. Glutathione was also higher in the light in untransformed poplars and in those overexpressing GR. In these plants, γ-EC was negligible in the light but increased in the dark. Cysteine content was little affected by light in any of the poplar types. No light-dependent changes in the extractable activities of γ-ECS, glutathione synthetase (EC 3.2.3.2) or GR were observed. In contrast, both the activation state and the maximum extractable activity of nitrate reductase (EC 1.6.6.1) were increased by illumination. In all poplar types, glutamate and aspartate were the major amino acids. The most marked light-induced increases in individual amino acids were observed in the glutamine, asparagine, serine and glycine pools. Illumination of leaves from poplars overexpressing γ-ECS at elevated CO₂ or low O₂ largely abolished the inverse light-dependent changes in γ-EC and GSH. Low O₂ did not affect foliar contents of cysteine or glutamate but prevented the light-induced increase in the glycine pool. It is concluded that light-dependent glycine formation through the photorespiratory pathway is required to support maximal rates of GSH synthesis, particularly under conditions where the capacity for γ-EC synthesis is augmented. Received: 17 December 1996 / Accepted: 28 January 1997     

Molecular mechanisms of heavy metal hyperaccumulation and phytoremediation

A relatively small group of hyperaccumulator plants is capable of sequestering heavy metals in their shoot tissues at high concentrations. In recent years, major scientific progress has been made in understanding the physiological mechanisms of metal uptake and transport in these plants. However, relatively little is known about the molecular bases of hyperaccumulation. In this paper, current progresses on understanding cellular/molecular mechanisms of metal tolerance/hyperaccumulation by plants are reviewed. The major processes involved in hyperaccumulation of trace metals from the soil to the shoots by hyperaccumulators include: (a) bioactivation of metals in the rhizosphere through root–microbe interaction; (b) enhanced uptake by metal transporters in the plasma membranes; (c) detoxification of metals by distributing to the apoplasts like binding to cell walls and chelation of metals in the cytoplasm with various ligands, such as phytochelatins, metallothioneins, metal-binding proteins; (d) sequestration of metals into the vacuole by tonoplast-located transporters. The growing application of molecular-genetic technologies led to the well understanding of mechanisms of heavy metal tolerance/accumulation in plants, and subsequently many transgenic plants with increased resistance and uptake of heavy metals were developed for the purpose of phytoremediation. Once the rate-limiting steps for uptake, translocation, and detoxification of metals in hyperaccumulating plants are identified, more informed construction of transgenic plants would result in improved applicability of the phytoremediation technology.     

转基因杨树林下种植转基因棉花对转基因杨棉复合系统内节肢动物群落多样性的影响

【目的】转Bt基因棉花和转Bt基因杨树在我国已推广使用。本研究的目的是调查和分析不同转基因杨棉复合系统内地上节肢动物群落多样性变化,为转基因杨树大规模应用提供生态安全方面的数据。【方法】2019年4-10月,在河北任丘采取欧洲黑杨Populus nigra林下种植转基因棉花Gossypium hirsutum的模式,设置转基因杨树 转基因棉花(复合生态系统1)和非转基因杨树-转基因棉花(复合生态系统2)两种杨棉复合系统,调查杨树和棉花地上部植株节肢动物种类和个体数量,比较节肢动物各功能群的物种数量和个体数量以及香农指数、优势集中性指数、均匀度指数等群落多样性指数,并测定了转基因杨树和棉花叶片Bt蛋白含量。【结果】复合生态系统1中转基因杨树和棉花各自植株上鳞翅目种群累计个体数均显著低于复合生态系统2相应植株上的个体数量。转基因杨树上叶甲类累计个体数量显著高于非转基因杨树上的,寄生蜂类累计个体数量则显著低于非转基因杨树上的。在6月5日、6月21日和9月7日的调查中,转基因杨树上的节肢动物群落香农指数显著高于非转基因杨树上的。除鳞翅目害虫外,2个复合系统中棉株上节肢动物各功能群累计个体数量无显著性差异,香农指数、优势集中性指数和均匀度指数随时间变化的趋势基本一致且同一调查时间无显著性差异,仅在8月17调查中复合生态系统1中棉株上节肢动物香农指数显著高于复合生态系统2棉株上的。将杨树和棉花上节肢动物各类群累计数量相加作为系统整体,复合生态系统1和复合生态系统2在香农指数、优势集中性指数和均匀度指数数值上无显著差异。在调查后期,2个复合系统中节肢动物种群均向杨树叶片聚集。转基因棉花叶片Bt蛋白含量在各调查期均显著高于转基因杨树叶片的。【结论】转基因杨树对靶标害虫种群数量有较好的控制作用,对同系统内棉花上鳞翅目害虫数量亦有协同控制作用。转基因杨棉复合系统中地上节肢动物群落结构稳定,对系统内棉花地上部节肢动物群落多样性无显著影响。靶标害虫对转Bt基因杨树的抗性发展需持续监测。     

Phytoremediation--a novel and promising approach for environmental clean-up

Phytoremediation is an eco friendly approach for remediation of contaminated soil and water using plants. Phytoremediation is comprised of two components, one by the root colonizing microbes and the other by plants themselves, which degrade the toxic compounds to further non-toxic metabolites. Various compounds, viz. organic compounds, xenobiotics, pesticides and heavy metals, are among the contaminants that can be effectively remediated by plants. Plant cell cultures, hairy roots and algae have been studied for their ability to degrade a number of contaminants. They exhibit various enzymatic activities for degradation of xenobiotics, viz. dehalogenation, denitrification leading to breakdown of complex compounds to simple and non-toxic products. Plants and algae also have the ability to hyper accumulate various heavy metals by the action of phytochelatins and metallothioneins forming complexes with heavy metals and translocate them into vacuoles. Molecular cloning and expression of heavy metal accumulator genes and xenobiotic degrading enzyme coding genes resulted in enhanced remediation rates, which will be helpful in making the process for large-scale application to remediate vast areas of contaminated soils. A few companies worldwide are also working on this aspect of bioremediation, mainly by transgenic plants to replace expensive physical or chemical remediation techniques. Selection and testing multiple hyperaccumulator plants, protein engineering ofphytochelatin and membrane transporter genes and their expression would enhance the rate of phytoremediation, making this process a successful one for bioremediation of environmental contamination. Recent years have seen major investments in the R&D, which have also resulted in competition of filing patents by several companies for economic gains. The details of science & technology related to phytoremediation have been discussed with a focus on future trends and prospects of global relevance.     

解磷微生物修复土壤重金属污染研究进展

土壤重金属污染问题日益严重,具有普遍性、隐蔽性、表聚性、不可逆性等特点,已经成为环境污染治理中的热点、难点问题。解磷微生物能够依靠自身的代谢产物或通过与其他生物的协同作用,将土壤中的难溶性磷转化为可供植物吸收利用的磷,具有多重植物促生长功能和重金属解毒能力,可在重金属毒害水平下,促进植物生长、提高植物抗病能力、克服重金属对植物生长的不利影响,从而增强重金属修复植物的生存竞争力。从解磷微生物的研究现状入手,介绍了解磷微生物对土壤重金属污染的修复能力,综述了解磷微生物对土壤重金属污染修复的作用机制,分析了目前解磷微生物在重金属修复过程中存在的问题,并提出了今后研究的方向,为重金属污染土壤的修复提供了新思路。