植物吸收、转运和积累镉的机理研究进展

重金属镉(Cd)虽然不是植物生长的必需矿质元素,但依然能被植物吸收。且部分植物具有富集镉的特点,从而导致农产品镉含量超标,并通过食物链危害人类健康。研究植物吸收、转运和积累Cd的机理,对于培育低镉作物品种、降低农产品镉含量,以及选育超富集镉植物,修复镉污染土壤具有重要意义。从影响植物吸收Cd的因子,植物吸收、转运和积累Cd的机理以及植物拒Cd和富集Cd的分子机制等方面进行综述,以期为低镉作物的研究以及Cd污染土壤的综合治理提供一些参考。     

Fe对不同品种水稻吸收Cd的影响

1引言在农作物重金属污染中,Cd是一个毒性较强的元素,不仅对植物产生毒害引起产量下降[1,4],而且还会残留在植物可食部分,通过食物链进入人体,危害人体健康[2]。减少Cd进入食物链的可能途径之一是调节土壤中Cd的生物有效性;二是利用或培育吸Cd童少或Cd优先吸附保留在报中的植物品种水稻对土壤中Cd吸收量较大,通过第一种途径改良比较困难,因此利用植物自身的调控机制减少对Cd的吸收及其转移尤为重要Cd很容易被吸收并分配到植物的各个部位,为了减少它在食物链中的官集,有必要了解植物对它的吸收机制和在体内的分配过程本文研究…     

硼、镉元素及其交互作用与油菜产量和品质

硼和镉两种元素是影响油菜产量和品质的两个重要因素.硼是植物生长所必需的微量元素,施硼是油菜种植的必需环节;镉是植物生长的非必要元素,易在油菜体内富集,可能通过食物链危害人体健康.本文主要从镉含量与油菜食品安全品质角度考虑,阐述了油菜对镉的积累和耐受机制;同时,概括了前人总结的硼对油菜的产量和品质的影响.最后,结合本人研究区广西地区土壤有效硼含量低,全镉含量高的现状,提出运用硼镉交互作用机理,通过施加适量硼肥,提高油菜的产量和品质,消除土壤镉的潜在危害,从本质上改善该地区土壤存在的低硼高镉现状.     

广西某污染区金属元素在土壤-植物系统中的迁移规律

重金属镉（Cd）是一种毒性极强并广泛存在于环境中的有害元素。土壤中的Cd极易被植物吸收并通过食物链对普通人群的健康造成危害。由于Cd在土壤．植物系统的迁移及对人类健康的影响与某些金属元素之间存在着相互作用,研究这些元素对Cd在食物链中迁移及在人体内富集的影响机制成为Cd研究的热点。本研究对广西某污染区的菜田进行了调查,结果表明：污染区蔬菜的Cd、Ca、Cu、Fe、Pb、Zn的浓度明显高于非污染区;不同的蔬菜品种对重金属元素Cd、Cu、Pb、Zn的迁移和积累能力存在着较大差异,不同金属元素的迁移能力依次为Cd〉Zn〉Cu〉Pb;Cd在土壤-植物中的迁移受共存元素的影响。     

木本植物对Cd~(115+115m)的吸收及其在体内的分配

一、前言 近年来,随着采矿、冶炼以及镉处理等工业的发展,不仅有大量废水中的镉通过土壤——植物进入食物链,给人造成危害,而且还有大量含镉粉尘污染大气环境,通过呼吸及消化道进入人体,直接给人以危害。因此,镉污染及其防治问题引起了人们极大的关注。国内外对水稻、小麦、玉米及蔬菜、牧草中镉的吸收积累规律作了不少研究(董克虞等,1981;陈铨荣等,1978:陈涛等,1980:Reddy等,1977)。     

土壤中镉、铅、锌及其相互作用对作物的影响

通过作物盆栽模拟试验(砂壤质褐土、pH值8.2)揭示：土壤中分别施入镉(CdCl2)、铅[Pb(CH3COO)2]或锌(ZnSO4)其影响表现为,植物各器官镉的含量超过对照植物的数倍至500倍。土壤镉浓度<5ppm和<10ppm分别造成某些蔬菜和水稻的污染。铅主要积累在植物根部,土壤铅污染对作物的影响较小。锌主要积累在植物叶片和根部,对水稻产生生长抑制的土壤锌浓度临界值不大于200ppm,此浓度对旱作无影响。土壤中同时施入镉和铅,植物对镉的吸收增加。而土壤中镉的增加却减少了植物体内铅的含量。土壤中由于镉、锌或铅、锌相互作用的结果,水稻对它们的吸收都有增加。在旱地土壤锌浓度的增高,降低了植物对镉、铅的吸收。镉、铅、锌同时施入土壤由于相互作用的结果,除锌之外,植物对镉、铅的吸收有明显下降。评价土壤重金属污染,不仅要看它们的含量及其存在形态,而且要分析它们之间的相互作用(促进或拮抗)特点。     

伴矿景天-水稻轮作及磷修复剂对水稻锌镐吸收的影响

采用盆栽试验,将锌镉超积累植物伴矿景天与镉低积累水稻中香1号轮作种植于重金属污染土壤,并向土壤添加钙镁磷肥和磷矿粉,研究两种磷修复剂对伴矿景天和锡低积累水稻生长及地上部重金属积累性的影响.盆栽试验结果表明,在轻污染土壤上施用50g"kg-'磷矿粉时伴矿景天地上部的Zn,Cd吸收量分别达到每盆11.5和0.79 mg,效果好于施用4g·kg(-1)钙镁磷肥处理.在重金属污染土壤上种植伴矿景天使后茬水稻地上部Zn、Cd浓度上升,但钙镁磷肥的施用显著降低了水稻体内的Zn,Cd积累量.种植伴矿景天后添加钙镁磷肥稳定调控剂对土壤中水溶态及NH4 OAc提取态Zn、Cd的稳定效果明显优于磷矿粉,且在高污染土壤上效果更佳.田间试验结果显示,施用钙镁磷肥不仅可增加水稻产量,且可一定程度上降低水稻地上部的Zn、Cd吸收量.     

微生物镉解毒机制及微生物-植物互作修复研究进展

镉(cadmium,Cd)是引起粮食减产的主要金属之一,具有高溶解性及高迁移性,易被植物吸收和积累。微生物长期在镉胁迫的条件下进化出一系列的镉解毒机制。微生物对镉的解毒包括抑制Cd(Ⅱ)的进入、促进Cd(Ⅱ)的外排,以及将进入胞内的Cd(Ⅱ)进行“扣押”。微生物的Cd(Ⅱ)钝化是通过细胞吸附和胞外沉淀将游离态的Cd(Ⅱ)进行钝化,这类微生物具有较强的土壤镉污染治理潜力。本文主要介绍微生物的镉解毒机制、微生物-微生物互作、微生物-植物互作机制及其在镉污染生物修复中应用的最新研究进展。     

伴矿景天-水稻轮作及磷修复剂对水稻锌镉吸收的影响

采用盆栽试验,将锌镉超积累植物伴矿景天与镉低积累水稻中香1号轮作种植于重金属污染土壤,并向土壤添加钙镁磷肥和磷矿粉,研究两种磷修复剂对伴矿景天和镉低积累水稻生长及地上部重金属积累性的影响.盆栽试验结果表明,在轻污染土壤上施用50 g·kg^-1磷矿粉时伴矿景天地上部的Zn、Cd吸收量分别达到每盆11.5 和0.79 mg,效果好于施用4 g·kg^-1钙镁磷肥处理.在重金属污染土壤上种植伴矿景天使后茬水稻地上部Zn、Cd浓度上升,但钙镁磷肥的施用显著降低了水稻体内的Zn、Cd积累量.种植伴矿景天后添加钙镁磷肥稳定调控剂对土壤中水溶态及NH₄OAc提取态Zn、Cd的稳定效果明显优于磷矿粉,且在高污染土壤上效果更佳.田间试验结果显示,施用钙镁磷肥不仅可增加水稻产量,且可一定程度上降低水稻地上部的Zn、Cd吸收量.     

镉超积累植物及植物镉积累特性转基因改良研究进展

植物提取修复技术是一项既经济又环保的土壤镉(Cd)污染修复技术,该技术的关键是筛选Cd超积累植物或利用基因工程手段改良植物以提高其Cd积累能力。人们已发现遏兰菜等7种Cd超积累植物及美人蕉等潜在的Cd超积累植物。还发现了许多与Cd耐受和积累能力有关的基因:(1)编码与Cd积累、耐受有关酶的基因,如细菌中的ACC(1-aminocyclopropane-1-carboxylic acid),植物中的PCS(Phytochelatin Synthase)基因;(2)编码金属结合蛋白的基因:MT(Metallothionein)、转运蛋白(P-type ATPase、ABC型转运器)基因;(3)其它相关基因:Hvhsp17、PvSR2(Phaseolus vulgaris stress-related gene number 2)等。并将其中的一些基因转入到其它生物中,提高了其对Cd的耐受性和积累量,为实现Cd污染土壤修复的目标奠定基础。     

Foliar Spraying and Seed Soaking of Zinc Fertilizers Decreased Cadmium Accumulation in Cucumbers Grown in Cd-Contaminated Soils

It is important to use proper agronomic management to reduce cadmium (Cd) accumulation in plants, ensuring food safety. To find the most effective agronomic approach, the effect of foliar spraying and seed soaking of zinc (Zn) fertilizers on Cd accumulation in cucumbers (Cucumis sativus L.) grown in two soil Cd levels (2 and 5 mg kg^?1 Cd) with and without an immobilizing amendment (red mud, RM) was investigated in the present study. The results showed that the treatment of foliar Zn or seed Zn significantly decreased the Cd concentration in cucumber shoots by about 12–36% in Cd-contaminated soils without amendment. Combined with RM treatment, the foliar Zn treatment further decreased the Cd concentration in cucumber shoots by up to 48–66% in Cd-contaminated soils. There were significant negative correlations between Cd and Zn concentrations in shoots of cucumbers grown in soils treated with RM and foliar Zn. The results revealed that the cucumber seedlings treated with RM and foliar Zn had a higher capacity for limiting the transfer of Cd to aboveground tissues. The results also suggested that increasing seed Zn concentrations sufficiently might act as an efficient, economic, and practical method for decreasing Cd uptake in crops grown in mildly Cd-contaminated and Zn-deficient soils.     

Fertilizer Impacts on Cadmium Availability in Agricultural Soils and Crops

Ingestion in food is a major pathway of cadmium (Cd) exposure for humans. It is therefore desirable to ensure that Cd concentrations in crops that enter the human food chain do not increase to levels that may lead to health risks. Phosphorus fertilizers contain Cd as a contaminant at levels varying from trace amounts to as much as 300 mg Cd kg^–1 of dry product and therefore can be a major source of Cd input to agricultural systems. Fertilization can influence Cd accumulation in crops by direct Cd addition and by indirect effects on soil pH, ionic strength, Zn concentration, rhizosphere chemistry, microbial activity, and plant growth. Cadmium will accumulate in the soils from fertilizer applications if the amount of Cd added in fertilizer is greater than the amount of Cd removal, whether in harvested crop removal or other loss pathways such as leaching, erosion, or bioturbation. Assessment of the impact of fertilizer management practices on the risk of Cd toxicity to the soil ecosystem and the risk of movement of Cd into the human diet must consider both the direct influence of Cd addition as a fertilizer contaminant and the indirect effects of fertilizer application on Cd phytoavailability. Cadmium accumulation in soils and crops can be minimized by adoption of management practices that improve fertilizer-use efficiency while minimizing Cd input.     

Using hyperaccumulator plants to phytoextract soil Ni and Cd

Two strategies of phytoextraction have been shown to have promise for practical soil remediation: domestication of natural hyperaccumulators and bioengineering plants with the genes that allow natural hyperaccumulators to achieve useful phytoextraction. Because different elements have different value, some can be phytomined for profit and others can be phytoremediated at lower cost than soil removal and replacement. Ni phytoextraction from contaminated or mineralized soils offers economic return greater than producing most crops, especially when considering the low fertility or phytotoxicity of Ni rich soils. Only soils that require remediation based on risk assessment will comprise the market for phytoremediation. Improved risk assessment has indicated that most Zn + Cd contaminated soils will not require Cd phytoextraction because the Zn limits practical risk from soil Cd. But rice and tobacco, and foods grown on soils with Cd contamination without corresponding 100-fold greater Zn contamination, allow Cd to readily enter food plants and diets. Clear evidence of human renal tubular dysfunction from soil Cd has only been obtained for subsistence rice farm families in Asia. Because of historic metal mining and smelting, Zn + Cd contaminated rice soils have been found in Japan, China, Korea, Vietnam and Thailand. Phytoextraction using southern France populations of Thlaspi caerulescens appears to be the only practical method to alleviate Cd risk without soil removal and replacement. The southern France plants accumulate 10-20-fold higher Cd in shoots than most T. caerulescens populations such as those from Belgium and the UK. Addition of fertilizers to maximize yield does not reduce Cd concentration in shoots; and soil management promotes annual Cd removal. The value of Cd in the plants is low, so the remediation service must pay the costs of Cd phytoextraction plus profits to the parties who conduct phytoextraction. Some other plants have been studied for Cd phytoextraction, but annual removals are much lower than the best T. caerulescens. Improved cultivars with higher yields and retaining this remarkable Cd phytoextraction potential are being bred using normal plant breeding techniques.     

Differential effects of AM fungal isolates on Medicago truncatula growth and metal uptake in a multimetallic (Cd, Zn, Pb) contaminated agricultural soil

Toxic metal accumulation in soils of agricultural interest is a serious problem needing more attention, and investigations on soil–plant metal transfer must be pursued to better understand the processes involved in metal uptake. Arbuscular mycorrhizal (AM) fungi are known to influence metal transfer in plants by increasing plant biomass and reducing metal toxicity to plants even if diverging results were reported. The effects of five AM fungi isolated from metal contaminated or non-contaminated soils on metal (Cd, Zn) uptake by plant and transfer to leachates was assessed with Medicago truncatula grown in a multimetallic contaminated agricultural soil. Fungi isolated from metal-contaminated soils were more effective to reduce shoot Cd concentration. Metal uptake capacity differed between AM fungi and depended on the origin of the isolate. Not only fungal tolerance and ability to reduce metal concentrations in plant but also interactions with rhizobacteria affected heavy metal transfer and plant growth. Indeed, thanks to association with nodulating rhizobacteria, one Glomus intraradices inoculum increased particularly plant biomass which allowed exporting twofold more Cd and Zn in shoots as compared to non-mycorrhizal treatment. Cd concentrations in leachates were variable among fungal treatments, but can be significantly influenced by AM inoculation. The differential strategies of AM fungal colonisation in metal stress conditions are also discussed.     

郑汴路路旁土壤-小麦系统重金属积累及其健康风险评价

按离路基不同距离采集土壤、麦苗和籽粒样品, 在测定样品重金属 (Pb、Cd、Zn、Cr和Cu) 的基础上, 开展了路旁土壤-小麦系统重金属分布、积累和污染状况分析, 并对膳食小麦 (Triticumaestivum) 引起的健康风险进行了评价。结果表明:1) 土壤-小麦系统重金属含量随着离开路基距离的增加呈先增加后减少的趋势, 土壤重金属含量>麦苗重金属含量>籽粒重金属含量。2) 麦苗和小麦籽粒对土壤重金属富集能力的大小顺序均为Cu>Cd>Zn>Pb>Cr, 麦苗对重金属的富集能力大于小麦籽粒。3) 膳食小麦所致的Cd个人健康风险较大。     

Molecular mechanisms underlying the toxicity and detoxification of trace metals and metalloids in plants

Plants take up a wide range of trace metals/metalloids (hereinafter referred to as trace metals) from the soil, some of which are essential but become toxic at high concentrations (e.g., Cu, Zn, Ni, Co), while others are non-essential and toxic even at relatively low concentrations (e.g., As, Cd, Cr, Pb, and Hg). Soil contamination of trace metals is an increasing problem worldwide due to intensifying human activities. Trace metal contamination can cause toxicity and growth inhibition in plants, as well as accumulation in the edible parts to levels that threatens food safety and human health. Understanding the mechanisms of trace metal toxicity and how plants respond to trace metal stress is important for improving plant growth and food safety in contaminated soils. The accumulation of excess trace metals in plants can cause oxidative stress, genotoxicity, programmed cell death, and disturbance in multiple physiological processes. Plants have evolved various strategies to detoxify trace metals through cell-wall binding, complexation, vacuolar sequestration, efflux, and translocation. Multiple signal transduction pathways and regulatory responses are involved in plants challenged with trace metal stresses. In this review, we discuss the recent progress in understanding the molecular mechanisms involved in trace metal toxicity, detoxification, and regulation, as well as strategies to enhance plant resistance to trace metal stresses and reduce toxic metal accumulation in food crops.     

Uptake and distribution of zinc,cadmium, lead and copper in Brassica napus var. oleífera and Helianthus annus grown in contaminated soils

Brassica napus var. oleifera and Helianthus annus were grown in artificially contaminated soils. Accumulation and translocation of the environmental pollutants zinc, cadmium, lead, and copper, was evaluated in different portions of the plants at two harvesting times. The distribution into the plants of these metal ions, as well as their capacity for contaminant phytoextraction and accumulation was assessed. For this purpose, an analytical method utilizing focused ultrasound employed for extraction and stripping voltammetry for measurement has been optimized and validated for the simultaneous measurement of Zn, Cd, Pb, and Cu in plant extracts.     

Phytoavailability of Heavy Metals and Metalloids in Soils Irrigated with Wastewater,Akaki, Ethiopia: A Greenhouse Study

Irrigation with untreated wastewater from several industrial, commercial, and domestic discharges for decades caused accumulation of various heavy metals and metalloids in soils along the Akaki River in Ethiopia. Assessment of environmental threats and the potential phytoremediation of the soils require understanding of the toxic elements’ uptake and distribution in plant parts. Hence, a greenhouse study was performed to examine the phytoavailability and distribution of Cr, Ni, Co, Cu, Zn, Cd, Pb, Hg, Se, V, and As in forage grasses: Oat (Avena sativa), Rhodes grass (Chloris gayana), Setaria (Setaria sphacelata), and the legumes Alfalfa (Medicago sativa) and Desmodium (Desmodium unicinatum). The average contents of Cr, Ni, Co, Cu, Zn, Pb, Hg, Se, and V in the plants were generally higher than the background levels for forage grasses/legumes, and some of these elements were in the phytotoxic range. Root bioconcentration factor (BCF = root to soil concentration ratio) > 1 was observed for Cu (Oat, Rhodes, Desmodium, and Setaria: Fluvisol), Zn (Setaria: Fluvisol), Cd (Rhodes: Fluvisol; Setaria from both soils) and Hg (Oat and Alfalfa: Fluvisol). Alfalfa and Desmodium displayed translocation factor > 1 (TF = shoot to root concentration ratio) for most heavy metals. Most heavy metals/metalloids may pose a health threat to humans and stock via introduction to the food chain. The plant factors (species and plant part), soil factors (soil type, soil fractions, pH, and CEC), and their interactions significantly (p < 0.05) influenced plant heavy metal and metalloid levels. However, the role of plant part and species emerged as the most important on heavy metal uptake, translocation, sequestration, and ultimately transfer to the food chain. Accordingly, the uptake and distribution of heavy metals/metalloids in the plants reflect the potential environmental and health hazards attributable to the use of fodder grasses, legumes, and cultivation of vegetables in soils with polymetallic and metalloid contamination.     

Uptake of soil cadmium by three field crops and its prediction by a pH-dependent Freundlich sorption model

Crop contamination with cadmium is a function of soil contamination. Here we study the applicability of the soil solution bioavailability hypothesis to Cd: that is, whether uptake of Cd was more directly related to its concentration or activity in the soil solution than in the soil solid phase. Experimental data from past soil-crop surveys for Cd were used to test this hypothesis. It was also investigated whether pH-dependent desorption of cadmium would be an important mechanisms in affecting cadmium activity and thus uptake. To do so we calculated the correlation between the Cd transfer factor (ratio between Cd level in plant dry material and Cd level in the topsoil) and either the soil pH, or the calculated soil solution Cd concentrations. There was no correlation between the Cd contents of the soil and of the edible parts of leafy plants (endive, spinach and lettuce). There was a strong negative correlation between soil pH and the log transfer factor for Cd at pH 4.5–7.2 and thus plant content. There also was a negative correlation between soil pH and calculated cadmium concentrations in the soil solution. For spinach grown on soils with pH > 7.2 the transfer factor increased, which is tentatively ascribed to cadmium mobilization by dissolved organic matter. The soil solution hypothesis should be further tested by pot and field trials. Special attention should be paid to the role of pH and dissolved organic matter. A C Borstlap Section editor     

Plant Cd2+ and Zn2+ status effects on root and shoot heavy metal accumulation in Thlaspi caerulescens

* In this study we address the impact of changes in plant heavy metal, (i.e. zinc (Zn) and cadmium (Cd)) status on metal accumulation in the Zn/Cd hyperaccumulator, Thlaspi caerulescens. * Thlaspi caerulescens plants were grown hydroponically on both high and low Zn and Cd regimes and whole-shoot and -root metal accumulation, and root (109)Cd(2+) influx were determined. * High-Zn-grown (500 microm Zn) plants were found to be more Cd-tolerant than plants grown in standard Zn conditions (1 microm Zn). Furthermore, shoot Cd accumulation was significantly greater in the high-Zn-grown plants. A positive correlation was also found between shoot Zn accumulation and increased plant Cd status. Radiotracer (109)Cd root flux experiments demonstrated that high-Zn-grown plants maintained significantly higher root Cd(2+) influx than plants grown on 1 microm Zn. It was also found that both nickel (Ni) and copper (Cu) shoot accumulation were stimulated by high plant Zn status, while manganese (Mn) accumulation was not affected. * A speculative model is presented to explain these findings, suggesting that xylem loading may be one of the key sites responsible for the hyperaccumulation of Zn and Cd accumulation in Thlaspi caerulescens.