矿区分离丛枝菌根真菌对万寿菊吸Cd潜力影响

盆栽试验研究土壤不同施Cd水平(0、5、20、50μg/g)下,接种矿区污染土壤中丛枝菌根真菌对万寿菊根系侵染率、植株生物量及Cd吸收与分配的影响。结果表明:接种丛枝菌根真菌显著提高Cd胁迫下万寿菊的根系侵染率和植株生物量;随着施Cd水平提高,各处理植株Cd浓度显著增加。各施Cd水平下万寿菊地上部Cd吸收量远远高于根系Cd吸收量,在土壤施Cd量达到50μg/g时,接种处理地上部Cd吸收量是根系的3.48倍,对照处理地上部Cd吸收量是根系的1.67倍;同一施Cd水平下接种处理植株Cd吸收量要显著高于对照。总体上,试验条件下污染土壤中分离的丛枝菌根真菌促进了万寿菊对土壤中Cd的吸收,并在一定程度上增加Cd向地上部分的运转,表现出植物提取的应用潜力。     

蚯蚓对土壤中铜、镉生物有效性的影响

以第四纪红黏土红壤和长江冲积物形成的高砂土为供试土壤、分别加入3个浓度的Cu^2 (100、200、400mg／kg)或Cd^2-(5.10、20mg/kg)模拟土壤污染．设置接种蚯蚓(Pheretima sp.)处理与不加蚯蚓对照．并种植黑麦草(Lolium multiflorum)、研究蚯蚓活动对土壤中Cu、Cd生物有效性的影响．以揭示蚯蚓在植物修复重金属污染土壤中的作用。结果表明：蚯蚓活动显著增加红黏中DTPA提取态Cu的含量、只有在浓度低于200mg／kgCu的处理中．才能增加CaCl2提取态Cu的含量．对H2O提取态Cu影响甚微;而对高砂土上Cu、Cd的各种形态影响均不显著;除红黏中浓度高于100mg／kgCu和10mg／kgCd处理外．蚯蚓活动显著提高了两种土壤上黑麦草地上部的生物量;接种蚯蚓后各种重金属处理中黑麦草对Cu的吸收量也显著增加,而Cd的吸收量变化不大。蚯蚓可能通过提高重金属的生物有效性而间接影响植物对重金属的修复效率。     

丛枝菌根真菌与高羊茅协同修复镉污染土壤

本研究采用温室盆栽试验,利用丛枝菌根（AM）真菌摩西管柄囊霉Funneliformis mosseae进行接种试验,研究了在Cd胁迫下（0、5、15和30mg/kg）接种AM真菌对高羊茅Festuca elata ‘Crossfire II’的生物量、防御酶活性、磷和镉（Cd）含量的影响。结果表明,随着Cd浓度的增加,高羊茅的菌根侵染率和菌根相对依赖性有所增加。接种AM真菌改善了磷从植株根系向地上部的转运,有助于植株在地上部积累更多的磷。此外,AM真菌和Cd胁迫对高羊茅植株抗氧化酶活性都有显著影响,在镉胁迫下,与未接种植株相比,接种AM真菌显著提高了植株的过氧化氢酶活性,而显著降低了植株的丙二醛含量。与未接种植株相比,接种摩西管柄囊霉显著提高了寄主植物对Cd的富集能力,有利于重金属在根部的积累,同时降低了地上部的Cd含量。本研究表明,高羊茅-丛枝菌根共生体在Cd污染土壤的修复中具有潜在应用价值。     

蚯蚓-秸秆及其交互作用对黑麦草修复Cu污染土壤的影响

以高沙土为供试土壤,加入Cu^2＋以模拟成：0,100,200,400mg／kgCu^2＋的Cu污染土壤,设置接种蚯蚓（E）、表施秸秆（M）,同时加入蚯蚓和秸秆（ME）及不加蚯蚓和秸秆的对照（CK）4个处理,并种植黑麦草。研究蚯蚓、秸秆相互作用对黑麦草吸收、富集铜的影响。结果表明：加入秸秆显著提高了蚯蚓的生物量,一定程度上缓解了重金属对蚯蚓的毒害,同时蚯蚓显著提高了秸秆的分解率,较无蚯蚓对照提高了58．11％～77．32％。接种蚯蚓（E,ME）还提高了土壤有效态重金属（DTPA-Cu）含量,秸秆处理（M）则降低了土壤有效态重金属含量。研究还发现,E处理促进了黑麦草地上部生长,而M和ME处理均显著提高了黑麦草地下部的生物量。E和ME处理同时提高了植物地上部和地下部的Cu浓度及Cu吸收量,M处理则只对植物的地下部Cu浓度和Cu吸收量有显著促进作用。总体来看,E处理、M处理及ME处理分别使黑麦草地上部Cu富集系数提高了31．22％～121．07％．2．12％～61．28％和25．56％～132．64％。     

放线菌对干旱胁迫下黑麦草生长及抗氧化特性的影响

采用菌剂接种及盆栽生物实验,研究了干旱缺水条件下放线菌对黑麦草生长和抗氧化特性的影响。结果显示:(1)干旱胁迫下,土壤中接种放线菌显著促进黑麦草的生长,其中根分蘖及根部生物量分别显著增加35.00%和37.47%;(2)接种放线菌后,黑麦草叶片的叶绿素总量和类胡萝卜素含量分别显著增加了12.02%和10.38%;(3)加菌后3种主要的抗氧化酶超氧化物歧化酶(SOD)、过氧化物酶(POD)和过氧化氢酶(CAT)较不加菌对照均增加,其增率分别为12.72%、2.38%和24.83%,其中SOD和CAT的活性增加显著。研究表明,干旱胁迫下放线菌接种土壤后,提高了黑麦草叶绿素含量和类胡萝卜素含量,增强了黑麦草抗干旱胁迫的抗氧化酶活性,可显著促进黑麦草的生长,增加其生物量。     

不同生态型摩西球囊霉菌株对蜈蚣草砷吸收的影响

砷超富集植物——蜈蚣草无论是在野外或是在室内均能被丛枝菌根真菌(AM真菌)侵染,但其对蜈蚣草砷吸收及转运的机理尚不清晰.本研究将分离于湖南省郴州市金川塘某铅锌尾矿蜈蚣草根际土壤(Glomus mosseae BGC GD01,简称污染菌株)和云南省未污染土壤(G.mosseae BGC YN05,简称非污染菌株)的2种摩西球囊霉菌株分别接种于非污染生态型和污染生态型蜈蚣草根际,8周后利用菌根化蜈蚣草幼苗在浓度为100 μmol·L-1砷(Na2HAsO4·7H2O)营养液中进行为期24 h的水培试验.结果表明,2种生态型摩西球囊霉菌株分别与蜈蚣草形成中等程度侵染,侵染率为25.2％ ～31.3％.无论是接种污染菌株或是非污染菌株,均明显促进了蜈蚣草根部对磷的吸收.在24 h水培试验期间,接种非污染菌株显著促进了蜈蚣草根部砷的吸收,但接种污染菌株对蜈蚣草根部砷吸收的促进作用有限,说明AM真菌对蜈蚣草砷吸收存在种内差异.     

丛枝菌根真菌对羊草生物量和氮磷吸收及土壤碳的影响

采用大田试验的方法在内蒙古锡林格勒草原进行牧草接种试验,通过灭菌和未灭菌两种土壤研究接种丛枝菌根真菌Glomus mosseae和Glomus claroidium对内蒙古典型草原优势种羊草生长的影响.结果显示,接种丛枝菌根真菌对羊草的地上部干重未产生显著影响,但向未灭菌土壤中接种能显著增加羊草根系量,同时接种G.mosseae显著增加了地上部的N、P含量及吸收量,有效地改善了植株N、P营养,提高了牧草品质;2种菌对根系的营养吸收影响不同,接种G.mosseae在灭菌土壤和未灭菌土壤中均能显著增加根系的N、P吸收量,而接种G.claroidium仅在土壤未灭菌状态下增加根系N、P吸收量;接种对土壤中的菌丝密度未产生显著影响,但接种后土壤中微生物量碳有增加的趋势,短期内难以观察到接种对土壤有机碳的影响.研究表明,丛枝菌根真菌能够提高牧草对N、P吸收,促进牧草的生长,改善牧草品质,增强牧草根际微生物量碳.     

丛枝菌根真菌对枳根净离子流及锌污染下枳苗矿质营养的影响

盆栽实验研究了不同施Zn水平(0、300 mg/kg和600 mg/kg)下,接种丛枝菌根真菌Glomus intraradices对枳苗生长、Zn、Cu、P、K、Ca、Mg分布的影响,并采用非损伤微测技术测定分析了菌根化与非菌根化枳根净Ca²⁺、H⁺、NO₃^-离子流动态。结果表明:(1)在不同施Zn水平下,接种菌根真菌显著提高了枳苗地上部及根部鲜重;随着施Zn水平的提高,菌根侵染率呈降低趋势,枳苗地上部与根部Zn含量呈增加趋势,且接种株根部Zn含量显著高于未接种株。(2)接种株未施Zn处理的地上部Cu、P、K、Mg和根部Cu含量、施600 mg/kg Zn处理的根部Cu及施300 mg/kg Zn处理的根部P含量均显著高于对照,而菌根真菌侵染对枳苗Ca含量并无显著性影响。(3)接种株未施Zn处理的根部距根尖端0 μm和600 μm处净Ca²⁺流出速率、600 μm处净H⁺流入速率、2400 μm处净NO₃^-流入速率均显著高于未接种株。     

巨大芽孢杆菌对伴矿景天修复镉污染农田土壤的强化作用

伴矿景天(Sedum plumbizincicola)是一种Cd/Zn超积累植物,常用于Cd污染土壤的植物修复。巨大芽孢杆菌(Bacillus megaterium)是一种溶磷型细菌,既可以促进植物生长,也可以提高土壤重金属生物有效性,对重金属污染土壤植物修复具有强化作用。本研究采用盆栽试验方法,分析了巨大芽孢杆菌不同接种量(10～60 mL)对伴矿景天修复Cd污染农田土壤效率的影响。结果表明: 在Cd污染农田土壤中接种巨大芽孢杆菌可以提高土壤中Cd的活性,土壤有效态Cd含量较对照(CK)增加15.0%～45.0%。与CK相比,巨大芽孢杆菌提高了伴矿景天地上和地下部的生物量,增幅分别为8.7%～66.7%和13.6%～81.8%,并显著增加了伴矿景天地上部的Cd含量,增幅在29.2%～60.4%。在种植伴矿景天并接种巨大芽孢杆菌条件下,土壤Cd去除率在26.7%～42.9%。这说明接种巨大芽孢杆菌可以促进伴矿景天的生长,增加其Cd含量,从而提高Cd污染农田土壤的修复效率。     

在蚯蚓影响下土壤Pb、Cd有效态的变化及小白菜对Pb、Cd的富集转移作用

研究了在蚯蚓影响下Pb、Cd添加量不同(Pb:500～1 700 μg·g-1;Cd:1～30 μg·g-1)的土壤中Pb和Cd有效态及其含量的变化以及小白菜(Brassica chinensis L. )对土壤中Pb和Cd的富集和转移作用.结果显示,在蚯蚓的影响下,Pb添加量为500～1 400 μg·g-1的土壤中酸提取态和可还原态Pb含量显著提高,有效态Pb总含量也随土壤中Pb添加量的提高逐渐增加;Cd添加量为5～20 μg·g-1的土壤中酸提取态Cd含量显著提高,有效态Cd总含量也随土壤中Cd添加量的提高而逐渐增加;当土壤中Pb和Cd添加量分别达到1 700和30 μg·g-1时,蚯蚓对Pb和Cd基本无活化作用.在蚯蚓的影响下,小白菜地上部分Pb含量显著提高,对Pb的转移系数也均高于各自的对照,地上部分和地下部分对Pb的富集系数分别为0.037～0.061和0.401～0.628.在蚯蚓影响下,在Cd添加量较低(1～5 μg·g-1)的土壤中小白菜地上部分和地下部分的Cd含量以及对Cd的富集系数均高于各自的对照;而在Cd添加量较高(10～30 μg·g-1)的土壤中小白菜地上部分和地下部分的Cd含量以及对Cd的富集系数均低于各自的对照,并随土壤中Cd添加量的提高逐渐降低;小白菜地上部分和地下部分对Cd的富集系数分别为1.196～11.516和1.744～20.425;各处理组小白菜对Cd的转移系数与各自的对照差异不显著.研究结果显示,蚯蚓主要对土壤中酸提取态和可还原态Pb以及酸提取态Cd有活化作用,并且可促进Pb由小白菜地下部分向地上部分的转移,但对Cd的转移无明显促进作用;此外,小白菜对Pb的富集作用不明显,但对Cd有一定的富集能力,这种能力的大小与土壤Cd含量有关.     

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.     

重金属污染的植物修复及相关分子机制

随着近代工业的发展,土壤重金属污染问题日益严重。重金属即使在极低浓度下仍然可以对人畜造成健康上的威胁,因此迫切需要有效的修复方法对土壤进行修复。生物修复,特别是植物修复目前已经成为重金属污染修复的重要手段之一,了解相关植物的重金属解毒和积累分子机制是提高修复效率、解决重金属污染问题的基础。文中以土壤修复方式为起点,结合植物吸收积累重金属以及解毒的相关分子机制研究,探讨了植物修复的发展现状以及趋势。     

重金属污染土壤植物修复中细胞分裂素的作用与机制

植物修复因投资成本低、环境扰动少、二次污染易控制、美化环境等优点成为重金属污染土壤修复重要的治理技术。植物内源细胞分裂素调控植物生理活动,外源细胞分裂素对植物生理生态特征产生显著影响,且在植物修复中逐渐受到研究人员的关注。细胞分裂素能够调控植物根茎发育、叶片衰老、激素传递等过程,同时在重金属胁迫下也参与蒸腾、光合、抗性、解毒等系统的运转。以细胞分裂素对植物生理活动的调控作用研究为基础,阐述了细胞分裂素在植物修复中的作用机制。主要包括：增强光合作用,延缓叶片衰老,提升植物抗性能力;调控根茎叶发育,增加植物生物量,强化植物富集效果;增强转运蛋白表达,提高叶面蒸腾作用,促进重金属吸收转运;参与解毒过程,降低重金属毒性,调控重金属体内转化。最后提出了细胞分裂素在重金属污染土壤植物修复中的研究方向,这对促进细胞分裂素在植物修复中的实际应用具有重要意义。     

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.     

Utilization of Multi-Tasking Non-Edible Plants for Phytoremediation and Bioenergy Source-A Review

Heavy metal contamination of land and freshwater resources is a serious concern worldwide. It adversely affects the health of animals, plants and humans. Therefore, remediation of toxic heavy metals must be highly considered. Unlike other techniques, phytoremediation is a holistic technology and can be used in large scale for soil remediation as it is costless, novel, environmentally-safe and solar-driven technology. Utilization of non-edible plants in phytoremediation is an ingenious technique as they are used to generate new bioenergy resources along with the remediation of contaminated soils. Some nonfood bioenergy crops such as Salix species, Miscanthus species, Populus species, Eucalyptus species, and Ricinus communis exhibit high capability to accumulate various metals and to grow in contaminated lands. However, there are still sustainable challenges facing coupling phytoremediation with bioenergy production from polluted lands. Therefore, there has long been a need for developing different strategies to resolve such challenges. In this article review, we will discuss the phytoremediation mechanism, the technique of phytoremediation coupling with bioenergy production, sustainable problems facing linking phytoremediation with energy production as well as possible strategies to enhance the efficiency of bioenergy plants for soil decontamination by improving their characteristics such as metal uptake, transport, accumulation, and tolerance.     

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。     

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。     

Phytoremediation of Heavy Metals: Physiological and Molecular Mechanisms

Heavy metals (HM) are a unique class of toxicants since they cannot be broken down to non-toxic forms. Concentration of these heavy metals has increased drastically, posing problems to health and environment, since the onset of the industrial revolution. Once the heavy metals contaminate the ecosystem, they remain a potential threat for many years. Some technologies have long been in use to remove, destroy and sequester these hazardous elements. Even though effective techniques for cleaning the contaminated soils and waters are usually expensive, labour intensive, and often disturbing. Phytoremediation, a fast-emerging new technology for removal of toxic heavy metals, is cost-effective, non-intrusive and aesthetically pleasing. It exploits the ability of selected plants to remediate pollutants from contaminated sites. Plants have inter-linked physiological and molecular mechanisms of tolerance to heavy metals. High tolerance to HM toxicity is based on a reduced metal uptake or increased internal sequestration, which is manifested by interaction between a genotype and its environment. The growing interest in molecular genetics has increased our understanding of mechanisms of HM tolerance in plants and many transgenic plants have displayed increased HM tolerance. Improvement of plants by genetic engineering, i.e., by modifying characteristics like metal uptake, transport and accumulation and plant’s tolerance to metals, opens up new possibilities of phytoremediation. This paper presents an overview of the molecular and physiological mechanisms involved in the phytoremediation process, and discusses strategies for engineering plants genetically for this purpose.     

Heavy metal detoxification mechanisms in halophytes: an overview

Heavy metals are among the major pollutants from anthropogenic inputs that reach mangrove ecosystem by urban and agricultural runoff, industrial effluents, boating, mining and other processes. To minimize the detrimental effects of heavy metal exposure and their accumulations, plants in general have evolved biological detoxification mechanisms, which include avoidance or exclusion, excretion and accumulation. To protect the cellular components from oxidative damage by heavy metal contamination, biological systems have developed enzymatic and non-enzymatic antioxidant mechanisms. Another detoxification mechanisms produced in plants are osmoprotectants, which are the compatible solutes which maintain a favourable water potential gradient and protect cellular structures from toxic ions. Besides these mechanisms, another heavy metal detoxification system in plants involves the chelation of metals by metal binding molecules like metallothioneins (MTs) and phytochelatins (PCs). To limit the heavy metal toxicity from mangrove ecosystem, it was found that phytoremediation is a most useful technology where in plants are used to remove pollutants from the environment and it is considered as a comparatively new, low-cost and highly promising technology for the remediation of heavy metal. Rhizofiltration, phytovolatilization, phytoextraction and phytostabilization are the important phytoremediation techniques. Among these phytoextraction and phytostabilization are found highly important in the case of mangroves and are promising means of phytoremediation.