镉和砷在植物中的积累及其分子调控机制研究进展

植物源食物是人类摄入有毒金属元素镉(Cd)和砷(As)的主要途径。深化植物对Cd和As积累途径分子机制的认识,有助于培育可食部分中低有毒金属元素含量的作物新种质。该文基于近年来有关植物Cd和As积累在主要模式植物中所取得的实质性研究进展,对植物介导Cd和As吸收的转运蛋白、As形态和生物转化机制以及控制Cd和As根-地上部转运效率和分配的关键因子等方面的研究进展进行综述,并对未来的研究前景进行了展望。     

植物对锑的吸收和代谢及其毒性的研究进展

锑(Sb)是一种有毒致癌元素, 一些自然和人为因素已造成我国部分地区土壤、水体及农产品受到严重的锑污染。环境中高含量的锑不仅影响农作物生长、降低其产量, 如果通过食物链被人体大量吸收, 还会引起严重的健康问题。研究锑在植物体内的富集特征, 对于保护环境与人体健康具有重要的现实意义。该文对当前锑在环境中的含量、污染状况、植物对锑的吸收、代谢以及锑对植物的毒害作用等方面的研究现状进行了综述。同时建议今后应加强以下3方面的研究: (1) 锑在生物圈迁移与转化特征; (2) 植物对锑的吸收、转运和代谢机制及锑的毒害作用机理; (3) 锑污染土壤及水体的植物修复技术。     

高等植物硝酸盐转运蛋白的功能及其调控机制

硝酸盐是植物从土壤中吸收的重要无机氮素形态。植物为适应含有不同浓度NO3-的土壤环境,进化出了高亲和硝酸盐转运系统(HATS)和低亲和硝酸盐转运系统(LATS),两个基因家族NRT1和NRT2家族分别参与了LATS和HATS的NO3-的吸收和转运。近年来,随着分子生物学技术和植物基因组学的快速发展,研究人员克隆出了大量参与硝酸盐吸收和转运的基因,并对这些基因的功能进行了深入研究,逐渐形成了复杂的硝酸盐调控网络。综述了植物中硝酸盐转运蛋白基因的克隆、表达及调控,并对进一步的研究作了展望,这些结果对于理解植物硝酸盐吸收的调控机制具有重要作用。     

植物氮素吸收与转运的研究进展

氮素是植物生长发育所必须的基本营养元素,在植物生长发育和形态建成中起着重要作用.土壤中植物所利用的主要氮素形式是铵态氮和硝态氮,在进化过程中植物形成不同的吸收和转运铵态氮和硝态氮的分子机制.该文对植物吸收与转运氮素的生理学特征、分子机制及涉及的相关基因等研究进行概括性综述,为研究水稻中氮素吸收、转运相关基因提供理论基础...     

无机砷在植物体内的吸收和代谢机制

砷污染已成为全球非常突出且急需解决的环境问题,严重威胁人类健康和环境安全.在自然环境和土壤系统中,砷的存在形态相当复杂,但植物砷毒害主要源于As（V）和As（Ⅲ）暴露.As（V）通过Pi的吸收通道被植物根系吸收,并在还原酶（AR）作用下被快速还原为As（Ⅲ）.As（Ⅲ）通过NIP蛋白通道进入植物体内,在砷甲基转移酶(ArsM)的作用下转化为甲基化砷或与谷胱甘肽（GSH）、植物螯合肽（PC）等多肽的巯基螯合封存在根部液泡或转运到地上部分,从而起到砷解毒的作用.同时,植物吸收的一部分砷也可外排到外部介质.本文以农作物尤其是水稻为主线,详述了As（V）和As（Ⅲ）吸收、外排及As（V）还原、As（Ⅲ）甲基化、螯合作用的最新研究进展,并提出了今后的研究重点.     

植物对硼元素的吸收转运机制

硼是植物生长发育所必需的微量元素,但是在世界范围内,土壤中硼含量过高或者过低都会对植物生长产生影响,是农业生产上的主要问题.近来人们对硼的吸收转运机制的研究取得了突破性进展,鉴定了一些硼的转运通道和转运蛋白,例如：NIP5;1、NIP6;1、BOR1和BOR4,并对它们的转运机制有了一些了解.植物在硼缺少的情况下首先通过转运通道NIP5;1把硼吸收到共质体,然后通过转运蛋白BOR1运入中柱;在高硼毒害时,通过转运蛋白BOR4把过多的硼转出植物体,同时在植物中增加糖醇的含量,过表达BOR1或BOR4都能改变植物对硼含量变化的耐受性.因此,对植物中硼吸收转运机制的研究将有利于人们通过生物学手段提高作物对土壤中硼过高或过低的抗性.     

植物菌根共生磷酸盐转运蛋白

大多数植物能和丛枝菌根（arbuscular mycorrhiza, AM）真菌形成菌根共生体。AM能够促进植物对土壤中矿质营养的吸收,尤其是磷的吸收。磷的吸收和转运由磷酸盐转运蛋白介导。总结了植物AM磷酸盐转运蛋白及其结构特征,分析其分类及系统进化,并综述了AM磷酸盐转运蛋白介导的磷的吸收和转运过程及其基因的表达调控。植物AM磷酸盐转运蛋白属于Pht1家族成员,它不仅对磷的吸收和转运是必需的,而且对AM共生也至关重要,为进一步了解菌根形成的分子机理及信号转导途径提供了理论基础。     

菌根真菌与植物共生营养交换机制研究进展

菌根是陆地生态系统普遍存在的、由土壤中的菌根真菌侵染宿主植物根系形成的联合共生体.菌根的建立是以共生体双方的营养交换为基础的:菌根真菌从土壤中吸收氮、磷等营养物质并转运给宿主植物,供其生长;作为交换,植物则以脂质或糖的形式向菌根真菌提供其生长所必需的碳水化合物.近年来,菌根真菌与宿主植物间的营养交换机制一直是研究的热点,国内外对菌根真菌介导的植物营养物质吸收和转运机制的研究也取得了巨大进展.本文综述了丛枝和外生两种菌根真菌与宿主植物间营养交换的最新研究进展,尤其是碳、氮、磷等几种重要营养物质的吸收与双向转运机制,以及营养交换在菌根形成中的潜在调控作用,并对目前存在的关键问题和未来研究方向进行了分析和展望,这对菌根模型的建立及菌根效益的优化具有重要意义.     

镉在土壤-植物-人体系统中迁移积累及其影响因子

环境镉(Cd)污染对微生物、植物、动物和人体均可产生较大的危害。食物链是镉对普通人群造成健康危害的主要途径之一。污染土壤中的镉通过植物根系吸收与体内转运最终在植物可食部分中积累。Cd通过食物链进人人体并在体内蓄积受许多因素的影响,这些影响因素主要有3个方面：土壤性质(土壤含镉量、pH、有机质、粘土矿物和土壤养分状况),植物特性(包括基因型差异、根际过程和植物生理机制)和人体微量元素营养状况等因素。本文就镉在食物链中迁移积累及其调控机理的研究进展进行简要的综述。     

砷、钙对蜈蚣草中金属元素吸收和转运的影响

蜈蚣草是砷的超富集植物和钙质土壤的指示植物。本试验在砂培条件下,研究砷、钙对蜈蚣草吸收和转运必需金属元素K、Mg、Mn、Fe、Zn和Cu的影响。结果表明。提高营养液中的砷浓度显著降低根部Mg和Zn的吸收。但对根部其它元素的浓度没有明显影响;叶柄中的Mn和地上部的Fe浓度因介质中添加砷而显著减少。其它元素在地上部的分布不受抑制。添加砷限制Fe从地下部向地上部转运,但促进其从叶柄向羽叶中运输;另外,还显著促进Mn由叶柄向羽叶和Zn由根向羽叶的转运。提高钙处理浓度对蜈蚣草吸收Fe、Zn、Cu无显著影响,但显著限制K、Mg和Mn的吸收。Mn是研究的6种金属元素中惟一一种明显向地上部转运富集的元素。从根部到羽叶中。金属元素间的相关性增强,在根部Ca与各种金属元素都无相关性;叶柄中Ca和Fe浓度呈极显著正相关;在羽叶中,Ca与K、Mg、Mn和Zn浓度呈显著负相关。     

ars1, an Arabidopsis mutant exhibiting increased tolerance to arsenate and increased phosphate uptake

Arsenic is one of the most toxic pollutants at contaminated sites, yet little is known about the mechanisms by which certain plants survive exposure to high arsenic levels. To gain insight into the mechanisms of arsenic tolerance in plants, we developed a genetic screen to isolate Arabidopsis thaliana mutants with altered tolerance to arsenic. We report here on the isolation of a mutant arsenic resisant 1 (ars1) with increased tolerance to arsenate. ars1 germinates and develops under conditions that completely inhibit growth of wild-type plants and shows a semi-dominant arsenic resistance phenotype. ars1 accumulates levels of arsenic similar to that accumulated by wild-type plants, suggesting that ars1 plants have an increased ability to detoxify arsenate. However, ars1 plants produce phytochelatin levels similar to levels produced by the wild type, and the enhanced resistance of ars1 is not abolished by the gamma-glutamylcysteine synthetase inhibitor l-buthionine sulfoxime (BSO). Furthermore, ars1 plants do not show resistance to arsenite or other toxic metals such as cadmium and chromium. However, ars1 plants do show a higher rate of phosphate uptake than that shown by wild-type plants, and wild-type plants grown with an excess of phosphate show increased tolerance to arsenate. Traditional models of arsenate tolerance in plants are based on the suppression of phosphate uptake pathways and consequently on the reduced uptake of arsenate. Our data suggest that arsenate tolerance in ars1 could be due to a new mechanism mediated by increased phosphate uptake in ars1. Models discussing how increased phosphate uptake could contribute to arsenate tolerance are discussed.     

Metalloids in plants: A systematic discussion beyond description

Metalloids represent a wide range of elements with intermediate physiochemical properties between metals and non-metals. Many of the metalloids, like boron, selenium, and silicon are known to be essential or quasi-essential for plant growth. In contrast, metalloids viz. arsenic and germanium are toxic to plant growth. The toxicity of metalloids largely depends on their concentration within the living cells. Some elements, at low concentration, may be beneficial for plant growth and development; however, when present at high concentration, they often exert negative effects. In this regard, understanding the molecular mechanisms involved in the uptake of metalloids by roots, their subsequent transport to different tissues and inter/intra-cellular redistribution has great importance. The mechanisms of metalloids' uptake have been well studied in plants. Also, various transporters, as well as membrane channels involved in these processes, have been identified. In this review, we have discussed in detail the aspects concerning the positive/negative effects of different metalloids on plants. We have also provided a thorough account of the uptake, transport, and accumulation, along with the molecular mechanisms underlying the response of plants to these metalloids. Additionally, we have brought up the previous theories and debates about the role and effects of metalloids in plants with insightful discussions based on the current knowledge.     

Pathways of arsenic uptake in prokaryotic and eukaryotic cells

Mechanisms of arsenic uptake and detoxification are present in all studied organisms. These mechanisms are considerably well described in unicellular organisms such as bacterium Escherichia coli and baker's yeast Saccharomyces cerevisiae, still leaving much to be revealed in multicellular organisms. Full identification of arsenic uptake and detoxification is of great importance. This knowledge can be very helpful in improving effectiveness of arsenic-containing drugs used in chemotherapy of parasitoses as well as in treatment of acute promielyocytic leukemia. Increased proficiency of bioremediation of arsenic-contaminated soils can be obtained by using plants hyperaccumulating arsenic. This kind of plants can be engineered by modulating expression levels of genes encoding arsenic transporters. The same technique may be used to decrease levels of accumulated arsenic in crops. The aim of this paper is to review current knowledge about systems of arsenic uptake in every studied organism--from bacteria to human.     

水稻砷的吸收机理及阻控对策

水稻积累砷的能力较其他农作物强,稻米是我国人群从食品中摄入无机砷的主要来源,降低稻米砷含量对增进农产品质量安全有重要意义。本文阐述了稻田砷的生物地球化学转化特征及水稻对不同形态砷的吸收、运输与储存机理,提出阻控稻米砷积累的对策,并讨论了需要进一步研究的问题。     

Nutrient Constraints in Arsenic Phytoremediation

Arsenic contamination has increased due to several environmental and anthropogenic activities. It is considered a carcinogen by the International Agency for Research on Cancer. It affects human health and causes various ailments and nervous system disorders. An environmental concern arises as arsenic enters the food chain through consumption of crops grown in arsenic affected areas. It has been observed that uptake of arsenic in plant parts is affected by the concentration of nutrients. Addition of nutrients either enhances the uptake of arsenic or the uptake of arsenic is reduced. Arsenic influences the nutrient uptake and distribution of nutrients in plants by either competing directly with nutrients and/or altering metabolic processes. The role played by nutrients has a direct bearing on the arsenic remediation of the crops and hence, it will be of significance to crop growers in reducing the arsenic content in crops. This review reports about the mobility, bioavailability and plant response to the presence of nutrients and their effect on arsenic phytoremediation. In this review, major emphasis has been made to contemplate the effects of nutrients like phosphorus, nitrogen, ferrous, calcium, potassium, sulphur and selenium in arsenic phytoremediation.     

The biochemistry of environmental heavy metal uptake by plants: Implications for the food chain

Plants absorb a number of elements from soil, some of which have no known biological function and some are known to be toxic at low concentrations. As plants constitute the foundation of the food chain, some concerns have been raised about the possibility of toxic concentrations of certain elements being transported from plants to higher strata of the food chain. Special attention has been given to the uptake and biotransformation mechanisms occurring in plants and its role in bioaccumulation and impact on consumers, especially human beings. While this review draws particular attention to metal accumulation in edible plants, researched studies of certain wild plants and their consumers are included. Furthermore, this review focuses on plant uptake of the toxic elements arsenic, cadmium, chromium, mercury, and lead and their possible transfer to the food chain. These elements were selected because they are well-established as being toxic for living systems and their effects in humans have been widely documented. Arsenic is known to promote cancer of the bladder, lung, and skin and can be acquired, for example, through the consumption of As-contaminated rice. Cadmium can attack kidney, liver, bone, and it also affects the female reproduction system. Cadmium also can be found in rice. Chromium can produce cancer, and humans can be exposed through smoking and eating Cr-laden vegetables. Lead and mercury are well known neurotoxins that can be consumed via seafood, vegetables and rice.     

Arsenic hazards: strategies for tolerance and remediation by plants

Arsenic toxicity has become a global concern owing to the ever-increasing contamination of water, soil and crops in many regions of the world. To limit the detrimental impact of arsenic compounds, efficient strategies such as phytoremediation are required. Suitable plants include arsenic hyperaccumulating ferns and aquatic plants that are capable of completing their life cycle in the presence of high levels of arsenic through the concerted action of arsenate reduction to arsenite, arsenite complexation, and vacuolar compartmentalization of complexed or inorganic arsenic. Tolerance can also be conferred by lowering arsenic uptake by suppression of phosphate transport activity, a major pathway for arsenate entry. In many unicellular organisms, arsenic tolerance is based on the active removal of cytosolic arsenite while limiting the uptake of arsenate. Recent molecular studies have revealed many of the gene products involved in these processes, providing the tools to improve crop species and to optimize phytoremediation; however, so far only single genes have been manipulated, which has limited progress. We will discuss recent advances and their potential applications, particularly in the context of multigenic engineering approaches.     

Reduction and coordination of arsenic in Indian mustard

The bioaccumulation of arsenic by plants may provide a means of removing this element from contaminated soils and waters. However, to optimize this process it is important to understand the biological mechanisms involved. Using a combination of techniques, including x-ray absorption spectroscopy, we have established the biochemical fate of arsenic taken up by Indian mustard (Brassica juncea). After arsenate uptake by the roots, possibly via the phosphate transport mechanism, a small fraction is exported to the shoot via the xylem as the oxyanions arsenate and arsenite. Once in the shoot, the arsenic is stored as an As(III)-tris-thiolate complex. The majority of the arsenic remains in the roots as an As(III)-tris-thiolate complex, which is indistinguishable from that found in the shoots and from As(III)-tris-glutathione. The thiolate donors are thus probably either glutathione or phytochelatins. The addition of the dithiol arsenic chelator dimercaptosuccinate to the hydroponic culture medium caused a 5-fold-increased arsenic level in the leaves, although the total arsenic accumulation was only marginally increased. This suggests that the addition of dimercaptosuccinate to arsenic-contaminated soils may provide a way to promote arsenic bioaccumulation in plant shoots, a process that will be essential for the development of an efficient phytoremediation strategy for this element.     

蜈蚣草中砷超富集的分子机制研究进展

砷是一种毒性很强的类金属元素,土壤砷污染可引发一系列食品安全问题,进而威胁人类健康。蜈蚣草具有极强的富集砷的能力,在砷污染土壤的植物修复中具有重要的应用价值。深入阐释蜈蚣草超富集砷的分子机制是植物修复技术的核心理论基础。文中综述了蜈蚣草超富集砷的组学研究进展,以及目前鉴定到的砷富集过程中的重要分子元件,并对未来的研究方向和趋势进行了展望。