植物修复重金属污染及内生细菌效应

土壤和水体的重金属污染已严重危害人类生存环境与健康。由于受重金属污染的环境分布广泛,迫切需要开发经济的清除环境重金属的技术。植物修复是通过绿色植物降解或移除环境污染物,有望成为重金属污染环境的原位修复技术。植物内生菌是指定殖于健康植物的各种组织和器官内部的细菌,被感染的宿主植物不表现出外在病症,耐重金属的内生菌在多种超富集植物中存在。在植物修复过程中,野生型内生菌或基因工程内生菌的抗性系统能降低重金属植物毒性,促进其迁移金属。耐重金属内生菌还可以通过固氮、溶解矿物元素及产生类植物激素、铁载体和ACC脱氨酶等产物促进植物的生长。主要综述目前植物-内生菌相互作用及其潜在的促进植物修复重金属污染的研究进展。     

种子内生菌增强宿主植物重金属抗性的功能机制研究进展

种子是植物的繁殖器官,其内定殖有一定数量的内生菌,种子内生菌通过垂直传播成为新生植物组织内最早定殖的微生物,对连续几代植物内生菌群落的形成起着决定性作用,并在植物抗逆方面发挥着重要作用.本文对种子内生菌与宿主植物重金属抗性之间的关系及其功能机制进行综述,并对下一步研究方向予以展望.     

植物内生细菌在植物修复重金属污染土壤中的应用

土壤重金属污染是威胁人群健康和经济可持续发展的重要环境问题。植物修复具有经济、环保等特点,已成为治理重金属污染土壤的重要技术。如何提高植物对重金属的抗性、促进植物生长是影响植物修复效率的关键之一。内生菌群-植物共生关系在此方面具有独特优势。其中,植物内生细菌可改善植物营养、降低植物病菌感染、影响酶活性,以及分泌激素、含铁载体和有机配位体等,进而提高超积累植物对重金属的吸收作用。本文综述了近年来国内外关于抗重金属植物内生细菌筛选与应用的研究进展,分析了内生细菌促进植物生长、增强植物对重金属抗性、促进重金属向茎叶转移的机理,阐述了植物内生细菌在重金属污染土壤修复中的应用前景与研究重点。     

环境胁迫下内生菌与宿主代谢相互作用研究进展

植物体内成分是实时反映其生理状态的最直接指标,是其遭受生物或非生物胁迫应激状态的体现,微生物与植物的共生抗逆亦由代谢的重置与调控得以实现.内生菌可以自身细胞功能或代谢产物调控宿主代谢,其自身可产生独特的、显著区别于宿主的代谢成分参与抗逆;而宿主内环境的长期“驯化”亦可改变内生菌的表型和代谢.较全面地分析了植物与微生物共...     

内生菌协同宿主植物修复土壤复合污染的研究进展

土壤复合污染日益严重,危及植物生长及人类发展,寻找修复土壤复合污染的有效方法已经成为环境领域的优先事项。复合污染指同一环境中存在两种或两种以上的污染物,分为复合重金属污染、复合有机污染物污染及重金属-有机污染物复合污染。近些年发现内生菌能定殖在植物中,并且被感染的植物不会引起任何外在病症,其主要通过促进宿主植物生长,改变植物摄取污染物能力和酶促降解污染物等方法增强植物修复能力。本文综述了具有复合重金属和复合有机污染抗性的内生菌种类及其作用机制,并展望了内生菌协同宿主植物修复环境中复合污染物的研究方向。     

植物促生菌提高植物重金属耐受性研究进展

近年来植物修复技术因其独特的优势而被广泛关注。许多植物被认为是有价值的利用资源, 然而, 最有实际使用价值的植物对重金属的耐受性有限, 实际应用中变得越来越困难。植物促生菌资源对环境无污染, 具有独特的多样性和巨大的潜力。随着资源的开发和技术的发展, 微生物调控将会使植物修复技术变得更加可行和更有价值。回顾近年来新兴的微生物调控技术, 主要是植物促生菌的筛选、鉴定和应用价值。     

植物内生菌抗虫工程研究进展

生物防治已成为植物虫害防治的发展方向,越来越多地受到人们的关注。利用植物内生菌进行抗虫性的研究不断深入。本着重论述了内生菌的抗虫机制及其影响因素。同时,对抗虫策略的实施也进行了探讨。     

植物内生菌研究进展

内生菌由于生长于植物体内且不引起植物病害所以不易被发现,它是一类具有高实用价值的植物内生微生物。经过人们的不断研究,越来越多的植物内生菌被发现,其活性代谢产物的优势也得到了更多研究者的认可。综述了国内外有关植物内生菌研究的主要成果和进展,并从植物内生菌的发现、研究历史、多样性、生理生化特性以及植物内生菌与宿主植物间的作用关系等多个层次进行了概述,以期为植物内生菌相关研究提供参考。     

植物内生菌研究进展及其存在的问题

植物内生菌是一个多样性十分丰富的微生物类群 ,分布于没有外在感染症状的健康植物组织内 ,并与宿主植物协同进化 ,其存在和作用长期以来一直为人们所忽视。随着研究领域的不断拓宽和研究方法的不断深入 ,植物内生菌的生态和生理作用及其作为潜在的生防资源和外源基因载体 ,在农业和医药领域中的巨大应用潜力 ,已逐渐成为国内外研究的热点。本文综述了近 10年来国内外植物内生菌研究的概况和最新进展 ,并对该研究领域中存在的若干问题进行了探讨。     

植物螯合肽及其在重金属耐性中的作用

综述植物螯合肽的生物合成及其在重金属耐性中的作用．有毒重金属在土壤中的积累不仅影响作物的生长和产量形成,而且严重威胁农产品的安全性．植物对重金属的耐性和积累在种间和基因型之间存在着很大的差异,在重金属胁迫条件下植物螯合肽(PC)的合成是植物对胁迫的一种适应性反应,耐性基因型合成较多的PC谷胱苷肽是合成PC的前体,PC可与重金属螯合,并进一步转运至液泡贮存,使细胞质的重金属浓度降低,从而达到解毒效果．重金属诱导植物合成PC的遗传机理和生化途径有赖于分子生物学的深入研究,cD-敏感型拟南芥突变体Cad1-1(缺失GSH)和Cad2-1(缺失PC合成诱导酶)的分离及相关研究,佐证了PC在Cd-解毒中起关键作用．对PC在重金属污染土壤或水体的植物修复和农作物安全生产中的意义进行了讨论．     

芦竹对不同重金属耐性的研究

研究芦竹(Arundo donax)在不同重金属污染湿地中的耐毒性能,测定了不同生长时段芦竹的生物性状和叶绿素含量,以及土壤中重金属含量的变化.结果表明,芦竹分别在浓度为100 mg·kg^-1左右的CuCu²⁺、Pb²⁺、Cd²⁺、Zn²⁺、Ni²⁺、Hg²⁺和50 mg·kg^-1以下的Cr⁶⁺污染环境中能正常成活,在40 d的生长期内,植物体内叶绿素有不同程度降低,下降比率在20%～56%,植物出现叶片软化,叶尖枯黄等症状,但植株仍呈现增长趋势.与对照植物相比较,在重金属胁迫下,植株细长,茎、叶呈黄绿色,除Cr⁶⁺、Hg²⁺外,植物高度基本不受重金属胁迫的影响.芦竹在高浓度(100mg·kg^-1)Cr⁶⁺污染环境中耐性较弱,表现出生长缓慢,部分地下茎腐烂,叶片短时间内出现枯萎等症状.结果还表明,土壤中重金属浓度随植物生长期增长而降低,除被植物吸收,植物挥发外,还存在着重金属向根际圈环境迁移的趋势,根周边湿土中重金属含量,明显高于试验缸外围湿土中重金属含量.可以认为,芦竹具有生物量大,根系发达,适应性强等特点,对修复湿地重金属污染蕴藏着巨大潜力,研究芦竹在植物修复技术中的应用,具有一定的现实意义.     

Heavy metals toxicity in plants: An overview on the role of glutathione and phytochelatins in heavy metal stress tolerance of plants

Plants experience oxidative stress upon exposure to heavy metals that leads to cellular damage. In addition, plants accumulate metal ions that disturb cellular ionic homeostasis. To minimize the detrimental effects of heavy metal exposure and their accumulation, plants have evolved detoxification mechanisms. Such mechanisms are mainly based on chelation and subcellular compartmentalization. Chelation of heavy metals is a ubiquitous detoxification strategy described in wide variety of plants. A principal class of heavy metal chelator known in plants is phytochelatins (PCs), a family of Cys-rich peptides. PCs are synthesized non-translationally from reduced glutathione (GSH) in a transpeptidation reaction catalyzed by the enzyme phytochelatin synthase (PCS). Therefore, availability of glutathione is very essential for PCs synthesis in plants at least during their exposure to heavy metals. Here, I reviewed on effect of heavy metals exposure to plants and role of GSH and PCs in heavy metal stress tolerance. Further, genetic manipulations of GSH and PCs levels that help plants to ameliorate toxic effects of heavy metals have been presented.     

Contribution of the arbuscular mycorrhizal symbiosis to heavy metal phytoremediation

High concentrations of heavy metals (HM) in the soil have detrimental effects on ecosystems and are a risk to human health as they can enter the food chain via agricultural products or contaminated drinking water. Phytoremediation, a sustainable and inexpensive technology based on the removal of pollutants from the environment by plants, is becoming an increasingly important objective in plant research. However, as phytoremediation is a slow process, improvement of efficiency and thus increased stabilization or removal of HMs from soils is an important goal. Arbuscular mycorrhizal (AM) fungi provide an attractive system to advance plant-based environmental clean-up. During symbiotic interaction the hyphal network functionally extends the root system of their hosts. Thus, plants in symbiosis with AM fungi have the potential to take up HM from an enlarged soil volume. In this review, we summarize current knowledge about the contribution of the AM symbiosis to phytoremediation of heavy metals.     

植物根际促生菌及丛枝菌根真菌协助植物修复重金属污染土壤的机制

植物修复是一种前景广阔的重金属污染土壤的主要修复技术,在微生物的协助下效果更为显著。植物根际促生菌可通过分泌吲哚-3-乙酸(IAA)、产铁载体、固氮溶磷等方式促进植物生长、改善植物重金属耐受性,从而有效提高重金属污染土壤的植物修复效率。菌根真菌是土壤-植物系统中重要的功能菌群之一,可侵染植物根系改变根系形态和矿质营养状况,通过菌丝体吸附重金属,也可产生球囊霉素、有机酸、植物生长素等次生代谢产物改变重金属生物有效性。植物根际促生菌与丛枝菌根真菌可对植物产生协同促生作用,在重金属污染土壤修复中具有一定应用潜力。目前,国内外关于植物根际促生菌和丛枝菌根真菌互作已有大量研究,而二者的相互作用机理仍处于探索阶段。本文综述了近年来国内外植物根际促生菌和丛枝菌根真菌在重金属污染土壤植物修复中的作用机制,并对其研究前景进行展望。     

Root fungal endophytes: identity,phylogeny and roles in plant tolerance to metal stress

Metal trace elements accumulate in soils mainly because of anthropic activities, leading living organisms to develop strategies to handle metal toxicity. Plants often associate with root endophytic fungi, including nonmycorrhizal fungi, and some of these organisms are associated with metal tolerance. The lack of synthetic analyses of plant-endophyte-metal tripartite systems and the scant consideration for taxonomy led to this review aiming (1) to inventory non-mycorrhizal root fungal endophytes described with respect to their taxonomic diversity and (2) to determine the mutualistic roles of these plant-fungus associations under metal stress. More than 1500 species in 100 orders (mainly Hypocreales and Pleosporales) were reported from a wide variety of environments and hosts. Most reported endophytes had a positive effect on their host under metal stress, but with various effects on metal uptake or translocation and no clear taxonomic consistency. Future research considering the functional patterns and dynamics of these associations is thus encouraged.     

Phytochelatins and heavy metal tolerance

The induction and heavy metal binding properties of phytochelatins in heavy metal tolerant (Silene vulgaris) and sensitive (tomato) cell cultures, in water cultures of these plants and in Silene vulgaris grown on a medieval copper mining dump were investigated. Application of heavy metals to cell suspension cultures and whole plants of Silene vulgaris and tomato induces the formation of heavy metal–phytochelatin-complexes with Cu and Cd and the binding of Zn and Pb to lower molecular weight substances. The binding of heavy metal ions to phytochelatins seems to play only a transient role in the heavy metal detoxification, because the Cd- and Cu-complexes disappear in the roots of water cultures of Silene vulgaris between 7 and 14 days after heavy metal exposition. Free heavy metal ions were not detectable in the extracts of all investigated plants and cell cultures. Silene vulgaris plants grown under natural conditions on a mining dump synthesize low molecular weight heavy metal binding compounds only and show no complexation of heavy metal ions to phytochelatins. The induction of phytochelatins is a general answer of higher plants to heavy metal exposition, but only some of the heavy metal ions are able to form stable complexes with phytochelatins. The investigation of tolerant plants from the copper mining dump shows that phytochelatins are not responsible for the development of the heavy metal tolerant phenotypes.     

Morphological and physiological alterations in the diatom Gomphonema pseudoaugur due to heavy metal stress

Periphytic diatom communities were analyzed from several heavy metal contaminated water bodies of Haryana, India. Among the analyzed sites, site HO3 (Saraswati Dham, Kurukshetra, Pehowa) showed significant response in the periphytic diatom community in terms of community shift (dominance of Gomphonema pseudoaugur) and lower biodiversity indices (species richness and Shannon index). Gomphonema pseudoaugur responded more specifically through induction of lipid bodies and occurrence of deformities in diatom frustules. PCA analysis showed that site HO3 is contaminated with heavy metals, especially Pb and Se. Pearson's correlation analysis showed a positive and statistically strong relationship between induction of lipid bodies and deformities with heavy metals (Pb and Se). Finally, from the present study, we concluded that heavy metal stress induces increased lipid body (LBs) size and deformities in the diatom species Gomphonema pseudoaugur, which could be a valuable indicator species for biomonitoring and a consideration in biofuel production.