小麦不同生育时期Cd、Cr、Pb污染监测指标体系

以小麦为供试材料,分别采用发芽试验、溶液培养、土柱栽培等毒理试验方法,研究了小麦萌芽期、幼苗期及成株期受重金属污染毒害的指标体系。结果表明,①小麦根伸长抑制率可作为萌芽期重金属污染评价的一项生物指标;Cd、Cr、Pb对小麦根生长的7d半效应浓度(EC50)值分别为1.39、0.20mmo.lL-1和2.75mmol.L-1,据此得到3种重金属对小麦同一性状的毒性次序为CrCdPb;此外各性状抑制率与胁迫浓度的关系可用双曲线模型y=x/(a+x/100)或指数曲线模型y=a(1-exp(-bx))较好模拟。②Cd、Cr、Pb单一污染胁迫对小麦幼苗性状的毒性次序均以影响叶面积和冠部干重为主,表明叶面积和冠部干重为幼苗期污染监测的敏感指标;重金属对除根干重外所有性状的毒性次序:CrCdPb,该毒性次序是根据引起50%抑制的临界浓度即EC50值确定的;各性状抑制率与胁迫浓度的关系可用直线模型、或双曲线模型、或指数曲线模型较好模拟。③重金属单一污染胁迫造成小麦籽粒产量下降幅度是CdCrPb;二元互作对产量影响的重要性次序为CdCrCdPbCrPb;在Cd、Cr、Pb复合污染胁迫条件下,穗数可以作为成株期重金属污染监测的首选指标。以上指标可为农田小麦重金属污染的监测和综合治理提供一些理论依据。     

小麦对Pb胁迫的生理生化反应研究

为了确定Pb污染土壤对植物生态系统造成的影响,运用植物幼苗早期生长实验,研究了Pb不同浓度（50、100、200、300）对小麦幼苗叶片的超氧化物歧化酶（SOD）、过氧化物酶（POD）活性、可溶性蛋白含量、丙二醛（MDA）以及叶片中叶绿素含量的影响。结果表明,Pb污染土壤对小麦的生理系统产生明显的影响,小麦叶片可溶性蛋白含量可以很好的指示土壤Pb污染的胁迫。在Pb胁迫下,小麦叶片MDA含量并没有显著增加;小麦植株叶片POD酶活能够被诱导而升高,小麦叶片中SOD酶活性没有一致的变化规律;幼苗受到损伤的明显症状之一是叶片叶绿素含量下降;重金属对小麦幼苗的毒害机理之一是抑制了蛋白质的生物合成。     

谷子幼苗对土壤铅、铬的生长响应及吸收积累的差异性

采用盆栽土培试验,研究了谷子幼苗对土壤中不同含量铅（Pb）、铬（Cr）的生长响应和吸收积累的差异性。结果表明,在所试浓度（50～800 mg·kg^-1）范围内,Pb、Cr在谷子幼苗地上部和地下部的积累量存在较大差异,幼苗重金属的吸收富集和转运系数均为Pb大于Cr、Pb、Cr胁迫对幼苗生物量的影响表现为低浓度的促进和高浓度的抑制作用,但Cr对生物量的影响比Pb更强。相同处理条件下,幼苗茎叶中可溶性蛋白质、DNA含量和增色效应对Pb、Cr的响应也有明显差别,Cr对幼苗的生理毒性和DNA损伤效应的作用强度大于Pb。     

小麦幼苗生长及其抗氧化酶活性对模拟酸雨与金属离子复合胁迫的响应

通过水培试验,研究了模拟酸雨(pH 3.5)与Al(3、30 mg/L)、Pb(25、250 mg/L)、Cd(0.11、mg/L)单独或复合胁迫对小麦幼苗生长及抗氧化酶活性的影响。结果表明,模拟酸雨与Al、Pb、Cd单独或复合处理12 d后,小麦幼苗根长降低54.01%~94.81%,苗高降低18.88%~77.95%,单粒萌根数降低21.87%~80.37%,其生长发育受到显著抑制,抑制效应随处理浓度增大和作用时间延长而增强,且复合处理组抑制效应更强;幼苗根部超氧化物歧化酶(SOD)活性在模拟酸雨与单一金属离子处理下显著升高,而在3种金属离子复合处理下显著降低,但酸性条件下无论金属离子单独及复合处理后,过氧化物酶(POD)活性均显著升高,过氧化氢酶(CAT)活性均明显下降。研究发现,酸性条件下3种金属离子对植物细胞均产生氧化胁迫作用,且它们复合胁迫的毒性效应大于其单独胁迫。     

镉、铅及其复合污染对大麦幼苗部分生理指标的影响

以Cd、Pb为胁迫因子，以大麦为试验材料，采用室内培养法，研究了重金属Cd﹑Pb及复合污染不同时间（3、5d）对大麦幼苗叶片部分生理指标的影响。结果表明，随着 Cd﹑Pb及Cd+Pb处理浓度的增加，大麦幼苗叶片中可溶性糖的含量表现为先升后降。在Cd﹑Pb单一处理条件下，不同浓度Cd﹑Pb均可造成叶细胞膜透性增大，叶片的相对电导率和脯氨酸含量上升。不同浓度的Cd+Pb复合处理对叶细胞膜的损伤均大于单一处理，低浓度Cd+Pb（5+50 mg·L^-1）复合处理组的可溶性糖含量比单一处理高。在不同处理时间（3、5d）内，所有Cd+Pb复合处理组叶中脯氨酸含量均高于单一处理组，Cd﹑Pb复合处理对脯氨酸的积累有促进作用。单一处理中Cd对大麦幼苗的毒性比Pb大，而复合处理（Cd+Pb）对大麦幼苗的损伤和毒害作用比单一处理更为严重，其交互作用机理值得进一步研究。     

Pb和Cd单一及复合胁迫条件下溪荪(Iris sanguinea)生长及金属离子积累特征分析

采用水培法,对Pb和Cd单一及复合胁迫(500 mg·L-1Pb、25 mg·L-1 Cd、500 mg·L-1pb-25 mg·L-1Cd)条件下溪荪(Iris sanguinea Donn ex Horn.)幼苗不同部分的生长及Pb、Cd、Zn、Cu、K和Na积累状况进行了研究.结果显示:在Pb单一胁迫条件下,溪荪幼苗地下部分干质量较对照降低了18.2％,地上部分干质量和耐性指数均与对照无显著差异;在Cd单一胁迫条件下,地下部分与地上部分的干质量较对照分别降低了16.4％和14.1％,耐性指数降低了7％;在Pb-Cd复合胁迫条件下,溪荪幼苗不同部分的干质量以及耐性指数均与对照无显著差异.在Pb单一及Pb-Cd复合胁迫条件下,幼苗不同部分的Pb含量均明显高于对照,Pb单一胁迫处理组幼苗地上部分和地下部分的Pb含量分别比Pb-Cd复合胁迫处理组高19.8％和16.0％.在Cd单一及Pb-Cd复合胁迫条件下,幼苗不同部分的Cd含量均明显高于对照,Pb-Cd复合胁迫处理组幼苗地上部分和地下部分的Cd含量分别为Cd单一胁迫处理组的2.02和5.74倍.经Pb和Cd单一及复合胁迫后,幼苗不同部分的Zn、Cu和Na含量均明显高于对照,而K含量则低于对照;地上部分的Zn、K和Na含量均高于地下部分,但Cu含量在幼苗不同部分的变化趋势则有所不同.比较结果表明:Pb-Cd复合胁迫对溪荪幼苗的Pb积累有促进作用、对Cd积累有抑制作用,表现出拮抗作用;溪荪对Pb胁迫的耐性相对更强,对Pb和Cd及其他金属元素有一定的积累能力,可用于Pb污染环境尤其是湿地Pb污染环境的修复.     

Cd2+胁迫对小麦幼苗生长及呼吸作用的影响

以小麦品种郑州9023为材料,研究了不同浓度Cd2 胁迫对小麦幼苗生长及呼吸作用的影响.结果显示:(1)随Cd2 胁迫浓度的升高,小麦幼苗根和芽的呼吸速率及琥珀酸脱氢酶(SDH)活性均呈先上升后下降的趋势.(2)Cd2 胁迫对小麦幼苗根中细胞色素氧化酶(COD)、苹果酸脱氢酶(MDH)、异柠檬酸脱氢酶(IDH)同工酶表达的影响较小,都呈低浓度诱导、高浓度抑制的效应,且Cd2 处理诱导了根中新的MDH、IDH同工酶带的表达;而不同浓度Cd2 对小麦幼苗芽中COD、MDH、IDH同工酶的表达影响较小.(3)随Cd2 胁迫浓度的增加,芽长、根长、芽干重、根干重均呈持续下降的趋势,且对根的抑制作用明显大于对芽.研究表明,Cd2 胁迫可以改变小麦幼苗根和芽中SDH、COD、MDHI、DH等呼吸作用关键酶的活性或同工酶表达,从而影响其呼吸作用,最终抑制了幼苗的生长.     

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(Triticum aestivum)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。     

绿洲土Cd、Pb、Zn、Ni复合污染下重金属的形态特征和生物有效性

通过模拟基于干旱区绿洲土壤Cd-Pb-Zn-Ni复合污染下的油菜盆栽试验,采用Tessier五步连续浸提法探究了重金属复合污染对油菜生长的影响及其各形态的转化归趋和生物有效性.结果显示,随着Cd-Pb-Zn-Ni复合胁迫水平的升高,油菜的干重先增加后减小,根系的生长由促进作用转变为抑制作用;对照土壤中4种重金属元素均以残渣态为主要赋存形态,可交换态的含量均很小;随着外源重金属的添加,油菜种植土壤中4种重金属元素的各形态含量随之增加,Cd、Pb、Zn的可交换态和Ni的碳酸盐结合态对外界胁迫响应强度最大,Cd、Pb、Zn、Ni的活性增加,且Cd、Pb的主要赋存形态迅速转变为碳酸盐结合态和铁锰氧化态,Zn的主要赋存形态由残渣态和碳酸盐结合态过渡到碳酸盐结合态和铁锰氧化态,Ni的主要赋存形态为碳酸盐结合态;Cd、Zn在茎叶中的含量大于根系,Pb、Ni反之,油菜能将Cd、Zn更多的运输至茎叶,Pb、Ni则主要积累在根系;油菜茎叶吸收Cd和油菜各部位吸收Zn的主要贡献形态为可交换态,根吸收Cd的主要贡献形态由可交换态转变为有机结合态,根吸收Pb和油菜各部位吸收Ni的主要贡献形态为碳酸盐结合态.     

镉、锌、铜胁迫对向日葵早期幼苗生长的影响

分析了3种重金属离子(Cd2+、Cu2+、Zn2+)对向日葵种子胚根伸长和早期幼苗生长的影响.结果表明,3种重金属离子对向日葵胚根伸长的抑制作用依次为:Cd2+>Cu2+>Zn2+.3种重金属胁迫明显降低了幼苗生长和叶绿素含量,并显著提高了H2O2水平.其中Cd2+胁迫引起幼苗H2O2爆发高于Cu2+和Zn2+胁迫.进一步分析植株抗氧化系统的变化发现,随着重金属离子浓度的增加,向日葵幼苗酶类抗氧化物质SOD和CAT的活性表现为先增加后降低的趋势;重金属胁迫提高了非酶类的抗氧化物质脯氨酸和GSH的含量.其中Cd2+和Zn2+胁迫对脯氨酸含量变化的影响大于Cu2+胁迫;而Cu2+胁迫对GSH含量变化的影响大于Cd2+和Zn2+胁迫.     

Effect of heavy metals on isoperoxidases of Wheat

The influence of increasing concentrations of copper, zinc, lead, nickel, chromium and cadmium on 14-day-old seedlings of wheat (Triticum aestivum L. cv. Vergina) was studied. Plants were grown in 1/10 strength Rorison’s nutrient solution with increasing concentrations of each of the metals added separately. The toxicity of metals depressed shoot growth but the most evident symptoms were on roots. The concentration of each metal which caused inhibition of root growth was chosen to study the influence of metals on isoperoxidases of wheat shoots. The concentrations employed did not alter the number of peroxidase bands but almost in all cases enhanced the intensities of bands of pH 4.0-4.2 and 5.0-5.4, while they decreased the intensities of bands of pH 4.2-4.6 and 5.4-6.5. The similar effects of the different heavy metals employed may suggest similarity in metal action on wheat isoperoxidases. The increased intensities of peroxidase bands may be considered as an indication of enhanced senescence caused by the heavy metal treatments. Generally, our results suggest that the heavy metals employed have caused complex changes on the multiple forms of peroxidases.     

重金属污染影响植食性昆虫的研究进展

重金属污染是世界各国面临的最为棘手的问题之一,对生态系统和食品安全构成了严重威胁。作为生态系统中食物链和食物网的重要环节,植食性昆虫是环境中重金属迁移、积累的重要媒介,其因重金属污染而受到的影响引起了大家的关注。本文综述了从2007至2018年重金属污染对植食性昆虫影响的研究进展。昆虫受重金属胁迫的研究途径有人工饲料添加、野外田间暴露、“土壤-植物-昆虫”食物链传递以及体外注射等。积累在植食性昆虫体内的过量重金属可导致其存活率、繁殖力和种群增长率降低,生长发育迟缓。重金属污染对植食性昆虫的生理生化毒性包括细胞超微结构破坏和DNA损伤,体内能量物质含量降低,酶活性、基因表达改变等。植食性昆虫会通过重金属硫蛋白、解毒酶活性的诱导等机制抵御重金属的毒害,从而对低浓度、长期重金属暴露产生生态适应性,甚至提高对其他逆境(如农药等)的耐受性。     

Proteomic changes in various plant tissues associated with chromium stress in sunflower

Heavy metal stress is one of the major abiotic stresses that cause environmental pollution in recent decades. An elevated concentration of these heavy metals is highly toxic to plant. Chromium (Cr) is one of the heavy metals whose concentration in the environment is still increasing alarmingly. It is harmful for plant growth and achene yield. To check out the growth and protein alternation towards pollutants, two sunflower varieties (RA-713 and AHO-33) were subjected to different chromium concentrations (control, 200 ppm, 400 ppm) by soil application. This study has elaborated that 400 ppm Cr resulted in a reduction of various growth parameters. Sodium dodecyl sulphate polyacrylamide gel electrophoresis (SDS-PAGE) was used to enhance the understanding of plant proteomic modulation under Cr stress. Different protein bands like 48 and 49, 26 kDa have newly appeared, and three 60, 47, and 42 kDa, and two protein bands 49 and 13 kDa were up-regulated in seeds of RA-713 and AHO-33, respectively. Some proteins (52, 16 kDa) are down-regulated in leaf tissues of both varieties. Only 6 and 81 kDa protein showed up-regulation and 154 kDa down-regulation behavior in the shoot in response to stress. The finding s of study might support the selection of tolerant genotype under Cr contamination and the discovery of new protein biomarkers that can use as monitoring tools in heavy metal stress biology.     

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.     

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.     

矿井废水灌溉对小麦生理特性及重金属积累的影响

以井水灌溉为对照 (CK),采用盆栽试验研究了矿井废水灌溉对小麦生理特性和重金属积累的影响.设置了3个矿区废水灌溉处理:洗煤废水(T₁)、经沉淀处理的洗煤废水 (T₂) 和煤矸石淋溶水 (T₃),于返青期开始进行矿区废水灌溉处理.结果表明： 矿井废水灌溉处理对小麦的生长发育和产量均有不同程度的负面影响.到开花期时,T₁、T₂和T₃处理小麦的单茎质量和叶面积、根系活力和光合速率均显著低于对照(P＜0.05),T₃处理小麦株高和叶绿素含量(SPAD值)显著降低(P＜0.05);T₁、T₂和T₃处理的籽粒产量分别比对照下降15.4%、9.8%和17.8%.此外,矿井废水灌溉处理小麦籽粒中Cr、Pb、Cu和Zn的含量均显著高于对照,表明矿井废水灌溉导致重金属在小麦籽粒中积累.
     

Growth, root and leaf structure, and biomass allocation in Leucanthemum vulgare Lam. (Asteraceae) as influenced by heavy-metal-containing slag

Effects of heavy metal contamination on growth, leaf turnover, biomass allocation and leaf and root structure of Leucanthemum vulgare Lam. were investigated. Plants were grown in two outdoor experiments, for 5 weeks or for 3 months, respectively, on sand with different additions of slag containing elevated levels of heavy metals, especially Cu and Ni. In the 3-month experiment nutrients were provided as composted manure, in the 5-week experiment as a solution. Slag contamination reduced plant growth, biomass allocation to roots, specific root length and specific leaf area, while root tissue density and leaf dry matter content increased. Fine root diameter increased, whereas coarse root diameters showed a non-significant decreasing trend. Toxicity of slag was lower in the 3-month experiment, probably due to organic matter in the substrate. We conclude that heavy metals in the soil around Cu–Ni smelters may, besides directly reducing growth of the plants, increase their susceptibility to other stresses such as drought, by reducing the root length to leaf area ratio. Fine and coarse roots show distinct responses, indicating that different root diameter classes should be regarded separately to fully understand stress responses of root systems.