植物铜转运蛋白的结构和功能

铜(Cu)是植物必需的微量营养元素, 参与植物生长发育过程中的许多生理生化反应。Cu缺乏或过量都会影响植物的正常新陈代谢过程。因此, 植物需要一系列Cu转运蛋白协同作用以保持体内Cu离子的稳态平衡。通常, Cu转运蛋白可分为两类, 即吸收型Cu转运蛋白(如COPT、ZIP和YSL蛋白家族)和排出型Cu转运蛋白(如HMA蛋白家族), 主要负责Cu离子的跨膜转运及调节Cu离子的吸收和排出。然而, 最近有研究表明, 有些Cu伴侣蛋白家族可能是从Cu转运蛋白家族进化而来, 且它们在维持植物细胞Cu离子稳态平衡中也具重要功能。该文对Cu转运蛋白和Cu伴侣蛋白的表达、结构、定位及功能等研究进展进行综述。     

与植物镉吸收转运相关的主要基因家族

镉(cadmium)是一种对植物毒性极强的非必需微量元素,影响植物生长发育,甚至死亡,并可在植物体内积累而威胁食物链顶端生物的生命健康。目前已发现有多类基因家族的成员参与了植物中镉的吸收转运过程,包括P型ATP酶、ABC、MATE、NRAMP、CE、CAX、ZIP、OPT等。这些基因家族主要是在吸收转运铁、锌、镁等植物必需微量元素的同时,也具有吸收转运镉等有毒重金属的功能。     

植物脂质转运蛋白的研究进展

高等植物脂质转运蛋白(lipid-transfer proteins,LTP)是一类小分子(约9 ku)的碱性蛋白质,已从多种植物中纯化出了LTP,且编码LTP的cDNA及基因也从不同植物中克隆.LTP能够在生物膜之间转运磷脂,因而认为LTP参与了细胞内生物膜形成.而近期的研究又发现LTP具信号肽,可从细胞内分泌到细胞外,位于细胞壁上,因而又对其在细胞内的转运脂质能力产生疑问.而有证据表明LTP参与了角质与腊质的形成、植物的抗病反应和植物对环境变化（温度、盐、干旱协迫）的适应.     

植物中铵转运蛋白的研究进展

铵转运蛋白在众多生物中被克隆与鉴定,它是一种广泛存在于微生物、植物细胞及动物的细胞膜上主动转运铵离子的载体,分子量约为48kD,含有10～11个跨膜域.本文阐述了植物铵转运蛋白分离鉴定的过程,对于铵转运蛋白的结构、功能、基因表达调控等方面作了较详细叙述.不同氮素条件下,铵转运蛋白基因通过转录调控表现了对铵离子吸收转运的不同特点,使植物根系在较宽的浓度范围中吸收铵离子,为细胞内铵离子库的内稳态提供了理论依据.铵转运蛋白有助于作物更有效的吸收氮素,为农业生产粮食增收提供了有利保障.     

植物重金属超富集机理研究进展

植物超富集重金属机理主要涉及植物对金属离子高的吸收、运输能力,区域化作用及螯合作用等方面,其中跨膜运载蛋白的表达、调控对重金属超富集这一特性起了关键作用。金属阳离子运载蛋白家族主要包括CDF家族、NRAMP家族和ZIP家族等,在超富集植物中已克隆出多个家族的金属运载蛋白基因,这些基因的过量表达对重金属在细胞中的运输、分布和富集及提高植物的抗性方面发挥了重要作用。综述了近年来研究重金属超富集植物吸收、转运和贮存Zn、Ni、Cd等重金属的生理和分子机制所取得的主要进展。     

植物中的核质转运相关蛋白

细胞内各个生命过程的有序进行需要生物大分子在细胞核与细胞质之间有选择、有控制地转运.而细胞核膜的存在为大分子的自由穿梭设置了屏障,因此生物大分子在细胞核与细胞质之间的转运要依赖于一些受体蛋白.输入蛋白β(importinβ)是首先从人类细胞中发现的生物大分子向细胞核输入的受体,其后相继鉴定出多个与输入蛋白β具有同源性的细胞核转运受体,命名为类输入蛋白β.这些转运受体介导的转运过程在生物有机体之间高度保守,在动物及酵母中调控核质穿梭以及各个信号过程的组分与分子机制研究较为清楚,但在植物中相对匮乏.本文在介绍细胞核转运受体共有结构特点和转运机制基础上,重点综述了植物细胞核转运受体的最新研究进展以及这些受体在植物信号转导中的重要调节作用.     

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。     

钙通道蛋白与植物抗盐性和抗冷性关系研究进展

植物钙通道蛋白几乎在植物生长发育的所有阶段都是必需的,它们参与细胞内钙离子浓度的调控,在植物细胞内钙离子的跨膜转运过程中起着极其重要的作用;它们同时调控植物细胞和组织的极性生长,参与植物应对一系列不同逆境胁迫因素的适应性反应,在植物抗逆方面同样起着极其重要的作用.本文对近年来国内外有关不同钙通道蛋白的性质及其在植物抗冷性和抗盐性中的作用研究进展进行综述,为在生理水平和分子水平上深入阐明植物钙通道蛋白参与植物抗逆性的机理提供信息资料.     

植物多药和有毒化合物排出转运蛋白研究进展

植物在生长及适应环境的过程中会吸收很多有益或有害的物质,自身也会产生大量代谢物,植物对这些物质的转运是植物生长发育及适应环境的重要环节,有多种转运蛋白家族参与其中。多药和有毒化合物排出转运蛋白(MATEs)是生物体中重要的转运蛋白家族之一,而植物中MATE基因的丰富程度要远远高于其他生物。根据植物MATEs的蛋白结构,这些基因被分为4个主要的亚家族,即MATE I,MATEⅡ,MATEⅢ和MATE IV。同一亚家族或同一MATE基因簇的基因还具有相同或相似的功能。植物MATEs定位于细胞的各种生物膜上,如细胞质膜、液泡膜、高尔基膜及囊泡膜等。此外,一些MATEs的表达还具有组织特异性,它们转运的底物也具有多样性和特异性,使得MATEs呈现出多种生物学功能。它们在外源性物质的排出、次生代谢产物的转运和累积、铁转运、铝脱毒和植物激素信号传递及植物的抗病性等方面都起着重要作用。该文对MATEs的发现、基因分类、亚细胞定位及生理功能等方面进行了概述,对深入研究该基因家族提供了思路,对该基因家族的应用进行了展望。     

锌转运蛋白基因研究进展

锌作为一种重要的微量元素参与了植物体内广泛的生理和生化过程,本文详细介绍了涉及Zn^2＋吸收转运的ZIP基因家族（ZRT／IRT相关蛋白）和CDF（Cation　diffusion　facilitator）家族。ZIP家族转运蛋白主要负责将Zn^2＋等二价阳离子跨膜转运进细胞内,以完成细胞内多种生理生化反应。CDF家族转运蛋白主要负责将过量Zn^2＋运出细胞,或者将细胞内过量Zn^2＋进行区室化隔离,降低Zn^2＋对细胞的危害作用。ZIP家族转运蛋白和CDF家族转运蛋白的相互协调使得Zn^2＋在细胞和有机体水平上维持着稳态,进而为细胞内各种生理生化反应的进行供一种保障机制。     

Biochemical changes and adaptive strategies of plants under heavy metal stress

Heavy metal contamination of soil, aqueous waste stream and ground water causes major environmental and human health problems. Heavy metals are major environmental pollutants when they are present in high concentration in soil and show potential toxic effects on growth and development in plants. Due to unabated, indiscriminate and uncontrolled discharge of hazardous chemicals including heavy metals into the environment, plant continuously have to face various environmental constraints. In plants, seed germination is the first exchange interface with the surrounding medium and has been considered as highly sensitive to environmental changes. One of the crucial events during seed germination entails mobilization of seed reserves which is indispensable for the growth of embryonic axis. But, metabolic alterations by heavy metal exposure are known to depress the mobilization and utilization of reserve food by affecting the activity of hydrolytic enzymes. Some plants possess a range of potential mechanisms that may be involved in the detoxification of heavy metals by which they manage to survive under metal stress. High tolerance to heavy metal toxicity could rely either on reduced uptake or increase planned internal sequestration which is manifested by an interaction between a genotype and its environment. Such mechanism involves the binding of heavy metals to cell wall, immobilization, exclusion of the plasma membrane, efflux of these toxic metal ions, reduction of heavy metal transport, compartmentalization and metal chelation by tonoplast located transporters and expression of more general stress response mechanisms such as stress proteins. It is important to understand the toxicity response of plant to heavy metals so that we can utilize appropriate plant species in the rehabilitation of contaminated areas. Therefore, in the present review attempts have been made to evaluate the effects of increasing level of heavy metal in soils on the key behavior of hydrolytic and nitrogen assimilation enzymes. Additionally, it also provides a broad overview of the strategies adopted by plants against heavy metal stress.     

Emerging mechanisms for heavy metal transport in plants

Heavy metal ions such as Cu(2+), Zn(2+), Mn(2+), Fe(2+), Ni(2+) and Co(2+) are essential micronutrients for plant metabolism but when present in excess, these, and non-essential metals such as Cd(2+), Hg(2+) and Pb(2+), can become extremely toxic. Thus mechanisms must exist to satisfy the requirements of cellular metabolism but also to protect cells from toxic effects. The mechanisms deployed in the acquisition of essential heavy metal micronutrients have not been clearly defined although a number of genes have now been identified which encode potential transporters. This review concentrates on three classes of membrane transporters that have been implicated in the transport of heavy metals in a variety of organisms and could serve such a role in plants: the heavy metal (CPx-type) ATPases, the natural resistance-associated macrophage protein (Nramp) family and members of the cation diffusion facilitator (CDF) family. We aim to give an overview of the main features of these transporters in plants in terms of structure, function and regulation drawing on information from studies in a wide variety of organisms.     

Metal oxidoreduction by microbial cells

Summary For many organisms, some heavy metals in external media are essential at low concentrations but are toxic at high concentrations. Strongly toxic heavy metals are toxic even at low concentrations. Recently, it was proven that changes of valencies of Fe, Cu and Mn were necessary for these metals to be utilized by organisms, especially microorganisms. The valencies of Hg and Cr are changed by reducing systems of cells in the process of detoxifying them. Thus, the processes of oxidoreduction of these metals are important for biological systems of metal-autoregulation and metal-mediated regulation. Metal ion-specific reducing enzyme systems function in the cell surface layer of microorganisms. These enzymes require NADH or NADPH as an electron donor and FMN or FAD as an electron carrier component. Electron transport may be operated by transplamsa-membrane redox systems. Metal ion reductases are also found in the cytoplasm. The affinities of metal ions to ligand residues change with the valence of the metal elements and mutual interactions of various metal ions are important for regulation of oxidoreduction states. Microorganisms can utilize essential metal elements and detoxify excess metals by respective reducing enzyme systems and by regulating movement of heavy metal ions.     

Transporters of ligands for essential metal ions in plants

Essential metals are required for healthy plant growth but can be toxic when present in excess. Therefore plants have mechanisms of metal homeostasis which involve coordination of metal ion transporters for uptake, translocation and compartmentalization. However, very little metal in plants is thought to exist as free ions. A number of small, organic molecules have been implicated in metal ion homeostasis as metal ion ligands to facilitate uptake and transport of metal ions with low solubility and also as chelators implicated in sequestration for metal tolerance and storage. Ligands for a number of essential metals have been identified and proteins involved in the transport of these ligands and of metal-ligand complexes have been characterized. Here we review recent advances in understanding the role of mugineic acid, nicotianamine, organic acids (citrate and malate), histidine and phytate as ligands for iron (Fe), zinc (Zn), copper (Cu), manganese (Mn) and nickel (Ni) in plants, and the proteins identified as their transporters.     

植物耐重金属机理研究进展

由于工业“三废”和机动车尾气的排放、污水灌溉及农药、除草剂和化肥的使用,严重地污染了土壤、水质和大气,其中土壤中的重金属（Ｈｇ、Ｃｄ、Ａｓ、Ｃｕ和Ａｌ）污染更为严重［１］。重金属在植物根、茎、叶及籽粒中的大量累积,不仅严重地影响植物的生长和发育［１～...     

A long way ahead: understanding and engineering plant metal accumulation

Some plants can hyperaccumulate metal ions that are toxic to virtually all other organisms at low dosages. This trait could be used to clean up metal-contaminated soils. Moreover, the accumulation of heavy metals by plants determines both the micronutrient content and the toxic metal content of our food. Complex interactions of transport and chelating activities control the rates of metal uptake and storage. In recent years, several key steps have been identified at the molecular level, enabling us to initiate transgenic approaches to engineer the transition metal content of plants.     

Research Advances on the Mechanisms of Heavy Metal Tolerance in Plants

Heavy metals impact on the cytoplasmic function in a number of different ways, principally by their binding to protein sulflhdryl groups, by producing a deficiency of essential ions and, eventually, by substituting the essemial ions. Other modes of toxicity are possible, including disruption of cell transport processes and oxidative damage by free radicals generated by metal redox cycling. Plants have developed a variety of biochemical defense strategies to prevent heavy metal poisoning. The possible defense mechanism in plant may involve: metal binding to cell walls, avoidance of uptake these toxic metal ions, reduction of heavy metal transport across the cell membrane, active efflux, compartmentalization and metal chelation. Phytochelatins that can tightly bind and sequester metals may play an important role in the accumulation of heavy metals and preventing them from entering the cell metabolic pathway, the rates of high molecular weight (HMW) metal phytochelatin complexes (Cd-Sa-complex) formation may be an important determinant of the plant tolerance. In addition, plants possess several antioxidant defense systems to protect themselves from the oxidative stress by heavy metals.     

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.     

Bacterial resistances to mercury and copper.

Heavy metals are toxic to living organisms. Some have no known beneficial biological function, while others have essential roles in physiological reactions. Mechanisms which deal with heavy metal stress must protect against the deleterious effects of heavy metals, yet avoid depleting the cell of a heavy metal which is also an essential nutrient. We describe the mechanisms of resistance in Escherichia coli to two different heavy metals, mercury and copper. Resistance of E. coli to mercury is reasonably well understood and is known to occur by transport of mercuric ions into the cytoplasmic compartment of the bacterial cell and subsequent reductive detoxification of mercuric ions. Recent mutational analysis has started to uncover the mechanistic detail of the mercuric ion transport processes, and has shown the essential nature of cysteine residues in transport of Hg(II). Resistance to copper is much less well understood, but is known to involve the increased export of copper from the bacterial cell and modification of the copper; the details of the process are still being elucidated. Expression of both metal resistance determinants is regulated by the corresponding cation. In each case the response enables the maintenance of cellular homeostasis for the metal. The conclusions drawn allow us to make testable predictions about the regulation of expression of resistance to other heavy metals.     

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.