大蒜植物络合素合酶基因转化对酵母重金属抗性的提高

重金属污染是全球面临的亟待解决的生态问题。利用植物对重金属的富集作用来清除环境重金属污染即植物修复已成为重要的环境生物技术之一。这一技术的长远发展有赖于在重金属富集或耐受中起关键作用的基因的克隆和应用。植物络合素是植物体内一类重要的对重金属起螯合作用的多肽, 其合成受植物络合素合酶的催化。该文取得了如下研究结果:1)通过原子吸收测定表明,在大蒜(Allium sativum)的根部可以积累3 000 mg·kg^-1的重金属镉;2)将克隆的大蒜植物络合素合酶基因(AsPCS)置于酵母表达启动子之下,构建酵母表达载体,并将其分别转入了因CUP1和acr3基因缺失而对重金属镉和砷敏感的酵母突变体菌株后,发现来自大蒜的AsPCS基因的表达使酵母CUP1缺失菌株对镉的耐受性提高了4倍, acr3缺失菌株对砷的耐受性提高了两倍;3)表达AsPCS基因酵母的生长模式证实了AsPCS基因的表达是酵母对重金属耐受性提高的原因。这些结果暗示, 大蒜植物络合素合酶基因在大蒜对重金属的抗性及大蒜根部对镉的积累中起关键作用,可作为重要的基因元件应用到修复污染的植物基因工程中。     

有机螯合剂在芦苇富集转运铅中的作用

近年来,随着人口的激增和工农业生产的迅猛发展,土壤和水体的重金属污染日益加重。植物提取技术作为一种新兴的修复重金属污染的治理方法,以其潜在的高效、经济及其生态协调性等优势被广泛关注。其研究主要是利用对某些重金属具有超富集能力的超积累植物或耐性植物,配合添加一定量的鳌合剂来进行修复。由于超富集植物一般生长缓慢且生物量小,因此利用对重金属有一定耐性的生长快速、生物量大的植物来进行修复更具有广阔的应用前景。芦苇作为一种多年生禾本科植物,具有生物量大、耐受性强和分布广泛的特点,已经被研究和应用到环境治理的多个领域。本文通过户外盆栽沙培试验,研究了铅胁迫下,分别在 2-10 mmol·L-1共 5 个浓度梯度的 EDTA 和柠檬酸两种鳌合剂处理下,芦苇生长对铅的响应以及对铅在植物体内的富集转运的影响。初试结果表明∶在 4mmol·L-1 Pb(NO3)2胁迫下,施加 EDTA 对芦苇的生长具有一定的抑制作用。当 EDTA 浓度为 10 mmol·L-1 时,透灌 7 d 后,其芦苇根和地上部(茎和叶)干重分别是空白试验(未加螯合剂)的 68.0% 和 72.3%,而柠檬酸对植物生物量的影响较小。同时,EDTA 和柠檬酸对铅在芦苇体内的富集和转运,都起到了促进作用。分别施加 10 mmol·L-1的 EDTA 和柠檬酸,其植物根部和地上部的铅浓度分别为空白试验的 7.4 倍、10.7 倍、2.5 倍、3.5 倍。EDTA 在促进植物体内铅的吸收和从根部到地上部的转运效率方面要比柠檬酸更为有效。尽管像 EDTA 和柠檬酸这样的鳌合剂能够在一定程度上提高植物的富集效率,但考虑到螯合剂自身对植物的毒害性、对环境的潜在威胁以及运行成本等方面因素,目前,寻找高效、廉价、可生物降解的鳌合剂以及大生物量的耐性植物成为植物提取技术的研究重点。     

泉州湾河口红树林湿地重金属的分布与迁移

通过测定泉州湾河口湿地2种红树植物(桐花树和秋茄)不同部位(根、枝和叶)及其根际沉积物中重金属酸可提取态含量,探讨该区域重金属元素的分布、在植物不同部位富集和迁移的情况。结果表明:2种红树植物根际沉积物中酸可提取态重金属含量顺序均为FeMnZnPbCuCrNi;秋茄根际沉积物中Cu、Zn、Pb、Ni和Cr两两之间呈正相关,桐花树根际沉积物中Cu与Zn呈正相关,Pb与其他重金属的相关性不显著;2种红树植物根中大多数重金属含量与根际沉积物中重金属酸可提取态含量之间呈正相关,而枝中的相关性不显著;2种红树植物重金属富集的情况较接近,Mn富集系数最大,其次是Cu和Zn;Mn、Cu、Zn、Cr主要富集在叶中,而Pb、Fe、Ni主要富集在根部;2种植物中Mn的迁移能力最强,易于从根部运输到叶中。     

水培条件下四种植物对Cd、Pb富集特征

利用水培方法测定了不同浓度下向日葵、蓖麻、紫花苜蓿及芥菜的生物量和植物体内重金属Cd、Pb含量,分析了植物对重金属的富集特征。结果表明:经过5周培养后,4种植物根部与地上部对重金属的富集量随着浓度的增加而增加,Cd浓度为20mg·L-1时,向日葵的根部Cd含量最高,达到237.86mg·kg-1,地上部Cd含量为89.48mg·kg-1;而Pb浓度为200mg·L-1时,芥菜根部对Pb的吸收量较高,达到597.22mg·kg-1,地上部Pb含量最高的则出现在向日葵处理Pb100mg·L-1中,为318.33mg·kg-1。4种植物对Cd、Pb的富集系数随重金属浓度的增加而减小;根部及地上部富集系数与生物量和重金属浓度呈现出一定的相关性;另外,在Cd、Pb复合处理中,一种重金属的存在会在不同程度上影响植物对另一种重金属的吸收。通过比较4种植物根部与地上部的生物量和对Cd、Pb富集特征,认为相对于其他3种植物向日葵对Cd、Pb具有较强的吸收潜力,并可以作为Cd、Pb污染土壤植物修复的备选植物。     

植物内生细菌修复重金属污染土壤作用机制研究进展

内生细菌生活在植物组织内部,长期以来与宿主植物形成了紧密的共生关系。内生细菌在重金属吸收、耐受和解毒方面具有优良的特性,为修复重金属污染土壤提供了有效的新方案。综述了内生细菌强化植物修复重金属污染土壤的作用机制,包括内生细菌通过产生植物生长调节激素,分泌ACC脱氨酶和几丁质酶等,促进宿主植物在重金属胁迫条件下的生长;通过改变重金属的生物有效性/毒性,减轻植物重金属毒害;通过与植物形成联合修复体,加强植物抗重金属毒性的能力。分析了近几年超富集植物内生细菌多样性及其影响因素,探讨了联合修复过程中影响内生细菌强化修复效果的主要因素,包括内生细菌的来源、活性和环境胁迫等各种生物因素和非生物因素,并对内生细菌与植物联合修复的研究方向进行展望,涉及内生细菌自身存活原因和如何耐受重金属的机制研究,植物内生细菌的行为动力学和代谢,以及内生细菌、植物及土壤之间的生态互作效应等,以期推动内生细菌大规模应用于植物修复重金属污染土壤。     

施硅对抑制植物吸收重金属镉的效应研究进展

施用化学改良剂是控制土壤重金属污染的有效手段。研究施硅对抑制植物吸收重金属镉的影响及其作用机制,对促进利用硅肥作为改良剂治理重金属污染土壤技术的发展有重要意义。近年来,以硅肥作改良剂对重金属污染的土壤进行治理的研究大量涌现。本文从施硅对抑制植物吸收镉及镉在植物体内的分布、迁移的影响;从植物细胞膜透性、抗氧化物酶系和抗氧化剂等新陈代谢或生理过程及硅-金属复合物的结构组成等方面对植物抗镉胁迫的生理生化效应及其抑制植物吸收重金属镉的机制进行综述,并对今后有待进一步研究的问题提出了建议。     

生物耐铜的分子机理及铜污染环境的生物联合修复

铜是动植物和人类必需的微量元素,缺乏或过多都将产生不良影响。随着社会经济的发展,人类活动对环境的干扰日益加剧,工业和农业生产活动常可导致土壤铜污染,铜已成为土壤重金属污染的主要元素之一。总结了铜在植物体内的自发内稳态调节机制,在细菌和真菌体内的吸收、分布、解毒和调节因子,同时以蚯蚓为例简要阐述了土壤动物对铜的解毒机理;从分子生物学角度对重金属铜在生物体内的代谢机理及生物对环境中过量铜的联合修复研究进展进行了综述,以期为铜污染环境的植物、微生物和动物联合修复的分子机理研究提供借鉴。     

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。     

一氧化氮对植物重金属胁迫抗性的影响研究进展

一氧化氮(NO)作为一种重要的信号分子,在调节植物重金属胁迫抗性方面上起着非常重要的作用。综述了NO在植物体内的产生途径,重金属胁迫下植物体内内源NO含量的变化以及外源NO与内源NO对植物重金属胁迫抗性的影响。大量研究表明外源NO能够增强植物对重金属胁迫的抗性,一方面是通过增强植物细胞的抗氧化系统或直接清除活性氧,另一方面是通过影响植物对重金属的吸收以及重金属在植物细胞内的分布。然而内源NO在调节植物重金属胁迫抗性上的功能角色仍存在争议。有些研究表明内源NO是有益的,能够缓解重金属胁迫诱导的毒性;但是也有证据表明内源NO是有害的,能够通过促进植物对重金属的吸收以及对植物螯合素进行S-亚硝基化弱化其解毒功能,从而参与重金属诱导的毒害反应和细胞凋亡过程。     

土壤种子库与矿业废弃地植被恢复研究：定居植物对重金属的吸收和再分配

研究了从引入的土壤种子所萌发,并成功地铅锌尾矿上定居的4个优势种植物,雀稗（Paspalum thunbergii)、双穗雀稗（P.disichum)、黄花稔（Sida rhombifolia)和银合欢（Leucaena leucocephala),对理金属的吸收及其在体内的再分配。植物组织中铜（Cu）和锌(Zn)的浓度,除了雀稗和双穗雀稗根中的锌浓度分别为344．2mg.kg^-1和331．9mg.kg^-1显得较高外,其作仍属植物体内正常水平范围（Zn:27-150mg.kg^-1,Cu:5-30mg.kg^-1)。草本植物雀稗、双穗稗和黄花稔对有毒重金属元素铅（Pb）的吸收表现出不同的模式,Pb在地上部与地下部分的浓度比以雀稗最低（为0．209）,表明雀稗所吸收的Pb大部分被滞留在根部,使之较少影响到地上部茎叶的光合作用功能及生长,从而使植物对重金属Pb环境更具耐性。相反,双穗雀稗和黄花稔则较高（分别为0．509和0．653）,显示所吸收的Pb较多地被转移到便于收获移走的地上部分,因而具有较大的植物修复潜力（Phytoremediation potential)。木本植物银合欢,所吸收的重金属Pb总量的80％以上是积累在根、茎的皮和木质部及枝条部分,只有15％左右分布在叶片中。这表明随着生长,有越来越多的Pb被吸收和积累在更新周期较长的器官中,只有很小的比例会随着落叶而归还到环境中去,因此,在利用植物重复金属污染土壤的实践中,这是一个特别值得利用的优点。     

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.     

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～...     

Studying how plants defend themselves: a chemical weapon produced by chilli fruit

Students often prefer to study animals rather than plants, because they see plants as passive, less interesting organisms. This paper proposes a simple hands-on laboratory exercise for high-school students (grade 12) to arouse their interest in learning about plants and to demonstrate to them that plants are active organisms capable of defending themselves. In this classroom exercise, students investigate how a plant responds to an invader. As a model for study, the exercise uses three organisms: red chilli fruit, the yeast biological control agent Saccharomyces cerevisiae, and the pathogenic fungus Rhizopus stolonifer. Students gain basic knowledge about how plants defend themselves against pathogens by observing the physical changes of an infected wound site and by investigating the chemical compounds produced by plants in response to pathogen invasion; they are also encouraged to think critically about using biological control as a means to promote environmentally friendly agricultural practices.     

硫对土壤重金属形态转化及植物有效性的影响研究进展

生源要素硫在土壤中的化学循环不仅会直接影响土壤重金属元素的环境行为,也可通过调控植物根际微环境间接影响植物对重金属元素的吸收累积.土壤中的硫被植物根吸收后在植株中合成的有机硫化合物如植物螯合素(PCs)和金属硫蛋白(MTs)可与重金属形成毒性较低的络合物,构成植物重金属解毒的重要机制之一.我国部分土壤缺硫现象严重,为保证作物高质高产,硫肥的使用逐渐被重视,而硫与重金属的交互作用机制也逐渐成为研究热点.本文综合相关研究,介绍了硫在土壤中的生物化学转化,探讨了土壤硫的化学转化对土壤重金属形态转化及植物有效性的影响,并对今后硫在土壤重金属控制的应用提出展望.
     

Red mud (RM)-Induced enhancement of iron plaque formation reduces arsenic and metal accumulation in two wetland plant species

Human activities have resulted in arsenic (As) and heavy metals accumulation in paddy soils in China. Phytoremediation has been suggested as an effective and low-cost method to clean up contaminated soils. A combined soil-sand pot experiment was conducted to investigate the influence of red mud (RM) supply on iron plaque formation and As and heavy metal accumulation in two wetland plant species (Cyperus alternifolius Rottb., Echinodorus amazonicus Rataj), using As and heavy metals polluted paddy soil combined with three rates of RM application (0, 2%, 5%). The results showed that RM supply significantly decreased As and heavy metals accumulation in shoots of the two plants due to the decrease of As and heavy metal availability and the enhancement of the formation of iron plaque on the root surface and in the rhizosphere. Both wetland plants supplied with RM tended to have more Fe plaque, higher As and heavy metals on roots and in their rhizospheres, and were more tolerant of As and heavy metal toxicity. The results suggest that RM-induced enhancement of the formation of iron plaque on the root surface and in the rhizosphere of wetland plants may be significant for remediation of soils contaminated with As and heavy metals.     

How Plants Cope with Cadmium: Staking All on Metabolism and Gene Expression

Environmental pollullon is one of the major problems for human health. Toxic heavy metals are normally present as soil constituents or can also be spread out in the environment by human activity and agricultural techniques. Soil contamination by heavy metals as cadmium, highlights two main aspects: on one side they interfere with the life cycle of plants and therefore reduce crop yields, and on the other hand, once adsorbed and accumulated into the plant tissues, they enter the food chain poisoning animals and humans. Considering this point of view, understanding the mechanism by which plants handle heavy metal exposure, In particular cadmium stress, is a primary goal of plant-blotechnology research or plant breeders whose aim is to create plants that are able to recover high amounts of heavy metals, which can be used for phytoremediation, or identify crop varieties that do not accumulate toxic metal in grains or fruits. In this review we focus on the main symptoms of cadmium toxicity both on root apparatus and shoots. We elucidate the mechanisms that plants activate to prevent absorption or to detoxify toxic metal ions, such as synthesis of phytochelatins, metallothioneins and enzymes involved in stress response. Finally we consider new plant-biotechnology applications that can be applied for phytoremediation.     

How Plants Cope with Cadmium: Staking All on Metabolism and Gene Expression

Environmental pollullon is one of the major problems for human health. Toxic heavy metals are normally present as soil constituents or can also be spread out in the environment by human activity and agricultural techniques. Soil contamination by heavy metals as cadmium, highlights two main aspects: on one side they interfere with the life cycle of plants and therefore reduce crop yields, and on the other hand, once adsorbed and accumulated into the plant tissues, they enter the food chain poisoning animals and humans. Considering this point of view, understanding the mechanism by which plants handle heavy metal exposure, In particular cadmium stress, is a primary goal of plant-blotechnology research or plant breeders whose aim is to create plants that are able to recover high amounts of heavy metals, which can be used for phytoremediation, or identify crop varieties that do not accumulate toxic metal in grains or fruits. In this review we focus on the main symptoms of cadmium toxicity both on root apparatus and shoots. We elucidate the mechanisms that plants activate to prevent absorption or to detoxify toxic metal ions, such as synthesis of phytochelatins, metallothioneins and enzymes involved in stress response. Finally we consider new plant-biotechnology applications that can be applied for phytoremediation.     

金属硫蛋白和植物螯合肽在植物重金属耐性中的作用

植物螯合肽和金属硫蛋白广泛存在于植物界中,它们对植物耐重金属特别重要,能够与重金属形成复合物,以缓解重金属对植物的危害。本文就这两种金属螯合蛋白的结构、生物合成和基因调控,以及在植物体内缓解重金属毒害的作用方面作了简要介绍。     

Plant virus infection development as affected by heavy metal stress

The work was focused on the investigation of possible dependencies between the development of viral infection in plants and the presence of high heavy metal concentrations in soil. Field experiments have been conducted in order to study the development of systemic tobacco mosaic virus (TMV) infection in Lycopersicon esculentum L. cv. Miliana plants under effect of separate salts of heavy metals Cu, Zn and Pb deposited in soil. As it is shown, simultaneous effect of viral infection and heavy metals in tenfold maximum permissible concentration leads to decrease of total chlorophyll content in experiment plants mainly due to the degradation of chlorophyll a. The reduction of chlorophyll concentration under the combined influence of both stress factors was more serious comparing to the separate effect of every single factor. Plants' treatment with toxic concentrations of lead and zinc leaded to slight delay in the development of systemic TMV infection together with more than twofold increase of virus content in plants that may be an evidence of synergism between these heavy metal's and virus' effects. Contrary, copper although decreased total chlorophyll content but showed protective properties and significantly reduced amount of virus in plants.