菌根和根分泌物在植物抗重金属中的作用

多年来人们对植物抗重金属的研究一直集中在植物体内的代谢调节和控制上。随着近年来对根际环境的研究,人们发现植物体外的根际环境对植物抗重金属有着重要的影响,目前研究主要集中在对菌根真菌和根系分泌物与植物抗重金属的关系,本文就近年来对菌根真菌和根系分泌物在植物抗重金属毒害中发挥的作用及其可能机理的研究状况作一概述,并对该领域的研究和应用前景作出展望。     

外生菌根缓解植物酸雨胁迫的机理研究进展

森林作为陆地生态系统的主体,是酸雨污染的主要受体,酸雨对生态系统产生着巨大的影响。菌根是菌根真菌与植物营养根的共生体。外生菌根真菌与宿主植物间互惠互利,在森林生态系统中,外生菌根在维持生态系统的养分平衡和改善树木营养等方面有重要的作用。本文综述了国内外关于菌根和酸雨关系的研究,酸雨能抑制外生菌根的形成,降低其活力;但另一方面,外生菌根能够缓解酸雨造成的植物危害,提高植株对酸雨的耐受力。外生菌根主要通过以下几方面缓解酸雨胁迫:(1)菌根形态结构的物理屏蔽作用;(2)增加养分吸收,增加御酸能力;(3)增强酶活性,提高植物生存能力;(4)产生有机酸或其他物质。     

外生菌根对植物非生物胁迫的缓解作用及作用机理研究进展

外生菌根在林木共生系统中占据重要的地位,具有提高宿主植物抗逆性的作用.在菌根学领域中,外生菌根与非生物胁迫互作的研究要远少于其他类型的菌根,尤其是缺乏综合、全面的总结性评述.文中总结了近5年来的相关研究,阐述了非生物胁迫(干旱、寒冷、高温、盐碱、重金属和有毒物质)下菌根共生体与植物抗逆性的关系,其他因子与外生菌根协同提...     

外生菌根对干旱胁迫的响应

从外生菌根真菌、外生菌根共生体以及外生菌根的间接作用等方面阐述外生菌根如何抵制干旱胁迫,并对未来我国外生菌根的研究提出了建议。干旱可以抑制外生菌根真菌的生长并降低其群落中真菌的多样性,干旱胁迫下外生菌根真菌子实体可以利用深度30cm以下的土壤水,子实体的表面积和体积比可作为筛选抗旱真菌的一个重要因子;在遭受干旱胁迫时,外生菌根共生体可以发生形态变化来应对干旱,同时增加了植株水分的吸收并改善了植物的光合作用、活性氧以及激素等相关代谢;外生菌根对植物生长的促进作用、增加土壤碳汇以及对其他根际微生物生长的促进作用等对宿主植物应对干旱胁迫有利。未来我国外生菌根研究应加强对干旱区优良菌-树组合的筛选工作,同时加大对乡土外生菌根真菌资源的调查力度,未来研究应重点向分子生物学领域推进。     

植物养分捕获的菌根塑性——外生菌根的塑性

植物根资源捕获塑性是地下生态学研究的重点之一, 在过去二三十年间有长足的进步。菌根塑性是根资源捕获塑性的重要方面, 但由于研究手段的限制, 目前仅有概念上的探讨。缺乏菌根塑性的根塑性研究至少是不全面的。菌根生物学的迅速发展, 尤其是分子生物学手段的介入, 使对菌根塑性进行深入研究成为可能。该文对外生菌根塑性进行讨论, 在简要介绍了外生菌根的生物学基本知识后, 着重讨论了外生菌根形态塑性和生理塑性的定义与内涵。通过文献综述, 分析讨论了外生菌根塑性的研究现状: 很少有研究聚焦在菌根塑性本身, 现有的材料多为其他研究的隐示或研究结果的引申, 并多在形态塑性方面。外生菌根的生理塑性未见有直接的实验数据。该文还对外生菌根研究中发展的、可用于菌根塑性研究的方法进行了综述。由于外生菌根塑性的复杂性, 对菌根塑性的研究会较植物根本身塑性的研究复杂得多, 问题也会相对复杂, 比如植物和外生菌根菌之间的营养需求关系、植物外生菌根塑性的生态意义、实验方法的缺陷等等。对今后外生菌根塑性研究的方向进行了探讨。     

外生菌根的生理学特征

我国外生菌根的出现和分布大都集中于暖热性针叶林、温凉性阔叶林、暖性阔叶林、暖性针叶林以及温凉性针叶林等森林中。外生菌根在林业生产、环境保护和引种驯化等领域内具有广泛应用价值和综合意义。本文仅就外生菌根的生理学特征进行概述。１侵染过程中的生理特征分布于...     

外生菌根菌在火炬松人工林应用的研究

连续６年研究了外生菌根菌在火炬松人工林的应用．结果表明,１２个供试菌株均能不同程度地在火炬松根系上形成外生菌根．在１２个供试菌株中,以松林小牛肝菌效果最佳,无论是在苗期还是上山造林,对促进寄主生长的效果均最好,且促进寄主生长的效果在立地条件较差的情况下表现得更为明显．     

外生菌根菌与森林树木的相互关系

生态系统的每个过程都伴随着各种微生物的活动,其中最重要的功能群之一是菌根真菌(菌根菌)。一般认为,菌根菌是自然界多数植物生存最基本的组成部分,陆地上约90％以上的高等植物都具有菌根菌。这些菌类的菌丝体与植物根系结合形成菌根,使植物生长成为可能,使不同种类植物的根系联在一起。根据菌根菌入侵植物根系的方式及菌根的形态特征,菌根可分为外生菌根、内生菌根和内外生菌根3组共7种类型。外生菌根主要出现在松科、桦木科、壳斗科等树种的森林生态系统中,在根系表面形成菌丝鞘,部分菌丝进入根系皮层细胞间隙形成哈氏网表面。菌根菌剂在森林经营中得到广泛地应用。外生菌根菌对森林树木的作用可归纳为：1)促进造林或育苗成活与生长;2)提高森林生态系统中植物的多样性、稳定性和生产力;3)对森林生态系统的综合效应,主要表现在增加植物一土壤联结,改善土壤结构,促进土壤微生物,增强植物器官的功能;4)抗拮植物根部病害病原菌等。树木与菌根菌相互关系研究主要包括：1)菌根共生的机理;2)菌根菌在退化森林生态系统恢复与改造中的作用;3)菌根菌的分布格局与森林生态系统服务功能的关系;4)菌根菌对森林生态系统的综合效应,如菌根菌与森林植物群落结构、物种多样性以及森林系统稳定性和生产力的研究。     

乳菇属真菌与松属植物形成的外生菌根

描述了两种乳菇属真菌在湿地松上形成菌根的形态学和组织学特征,结果表明两种真菌形成菌根在形态学和组织学上基本相似,其区别在菌根的颜色及受伤后产生的乳汁颜色,与文献报道的该属真菌形成的菌根的形态特征比较,表明具有乳汁菌丝是本属真菌形成菌根的共同特征,根据目前已有资料给出了乳菇属真菌所形成菌根的检索表。     

庐山外生菌根真菌的分布

早在一个世纪以前,人们就发现自然界中许多高等植物与真菌存在共生关系,并把这种共生体叫做菌根（Ｍｙｃｏｒｒｈｉｚａ）,最常见的菌根分为内生菌根（Ｅｎｄｏｔｒｏｐｈｉｃｍｙｃｏｒｒｈｉｚａ）和外生菌根（Ｅｎｔｏｔｒｏｐｈｉｃｍｙｃｏｒｒｈｉｚａ）。据Ｔｒｐｐｅ的调查［１］,能够形成菌根的真菌很多,与木本植物形成外生菌根的真菌多属于伞菌、多孔菌、腹菌等计有１１目３０科９０多个属;在植物界除了水生植物和极少数陆生植物种属外都能形成菌根。我国已报道能形成外生菌根的真菌约２８个科６３个属［２．４］。庐山是…     

Inhibition of photosynthesis by heavy metals

Inhibition of photosynthesis by heavy metals is well documented. In this review the results are compared between in vitro experiments on isolated systems (chloroplasts, enzymes ­.), experiments on excised leaves and intact plants and algae in vivo. In vitro experiments suggest potential sites of heavy metal interaction with photosynthesis at several levels of organisation, which are not necessarily confirmed in vivo. Analytical data on subcellular heavy metal level are generally missing to discuss their mechanism of action in the intact organism. In the field factors such as soil characteristics and air pollution have to be taken into account for assessing the mechanism of action of heavy metals on photosynthesis in plants, growing in a polluted erea.paper presented at the FESPP meeting in Strasbourg (1984)     

Biosensors for heavy metals

A biosensor is an analytical device that consists of an immobilized biocomponent in conjunction with a transducer, and represents a synergistic combination of biotechnology and microelectronics. This review summarizes the use of biosensors for detecting and quantifying heavy metal ions. Heavy metal contamination is of serious concern to human health since these substances are non-biodegradable and retained by the ecological system. Conventional analytical techniques for heavy metals (such as cold vapour atomic absorption spectrometry, and inductively coupled plasma mass spectrometry) are precise but suffer from the disadvantages of high cost, the need for trained personnel and the fact that they are mostly laboratory bound. Biosensors have the advantages of specificity, low cost, ease of use, portability and the ability to furnish continuous real time signals. The analysis of heavy metal ions can be carried out with biosensors by using both protein (enzyme, metal-binding protein and antibody)-based and whole-cell (natural and genetically engineered microorganism)-based approaches.Published online: March 2005     

Mechanisms of metal resistance in plants: aluminum and heavy metals

Plants have evolved sophisticated mechanisms to deal with toxic levels of metals in the soil. In this paper, an overview of recent progress with regards to understanding fundamental molecular and physiological mechanisms underlying plant resistance to both aluminum (Al) and heavy metals is presented. The discussion of plant Al resistance will focus on recent advances in our understanding of a mechanism based on Al exclusion from the root apex, which is facilitated by Al-activated exudation of organic acid anions. The consideration of heavy metal resistance will focus on research into a metal hyperaccumulating plant species, the Zn/Cd hyperaccumulator, Thlaspi caerulescens, as an example for plant heavy metal research. Based on the specific cases considered in this paper, it appears that quite different strategies are used for Al and heavy metal resistance. For Al, our current understanding of a resistance mechanism based on excluding soil-borne Al from the root apex is presented. For heavy metals, a totally different strategy based on extreme tolerance and metal hyperaccumulation is described for a hyperaccumulator plant species that has evolved on naturally metalliferous soils. The reason these two strategies are the focus of this paper is that, currently, they are the best understood mechanisms of metal resistance in terrestrial plants. However, it is likely that other mechanisms of Al and/or heavy metal resistance are also operating in certain plant species, and there may be common features shared for dealing with Al and heavy resistance. Future research may uncover a number of novel metal resistance mechanisms in plants. Certainly the complex genetics of Al resistance in some crop plant species, such as rice and maize, suggests that a number of presently unidentified mechanisms are part of an overall strategy of metal resistance in crop plants.     

Effect of simultaneous establishment of Sedum alfredii and Zea mays on heavy metal accumulation in plants

Land application of biosolids to improve agricultural productivity is a cost-effective approach for resource recovery. Unfortunately, municipal biosolids often contain high concentrations of heavy metals, including zinc and copper. In this study, a co-cropping technique was investigated using a known zinc hyperaccumulator, Sedum alfredii with a grain crop, Zea mays. After a 3-mo growth trial, the results indicate that when Z. mays is co-cropped with S. alfredii, heavy metals accumulated in the grains were significantly reduced when compared to monoculture cropping. Co-cropping improved the growth of both plant species. In addition, the biosolids maintained stable pH, N-P-K concentrations, germination potential, and water content after the plant treatment, regardless of the plant species used in the trial. In conclusion, co-cropping with hyperaccumulators may be an effective approach to reducing the risk of contaminant uptake in edible crops.     

Response of ectomycorrhizalPinus banksiana andPicea glauca to heavy metals in soil

Pinus banksiana andPicea glauca inoculated or not with the ectomycorrhizal fungusSuillus luteus were grown in a sandy loam soil containing a range of Cd, Cu, Ni, Pb and Zn concentrations. Ectomycorrhizal colonization rates were significantly reduced on Pinus and Picea seedlings by the heavy metals, particularly Cd and Ni. Needle tissue metal concentrations were lower in ectomycorrhizal seedlings at low soil metal concentrations. However, at higher soil concentrations, heavy metal concentrations of needle tissue were similar in ectomycorrhizal and nonmycorrhizal plants. The growth of nonmycorrhizal seedlings exposed to heavy metals was reduced compared to those inoculated withSuillus luteus. Apparently ectomycorrhizal colonization can protect Pinus and Picea seedlings from heavy metal toxicity at low or intermediate soil concentrations of Cd, Cu, Ni, Pb and Zn.     

Bacterial resistance and detoxification of heavy metals

Microbial cells have resistances to essentially all of the toxic heavy metals of the Periodic Table. In bacterial cells, the genetic determinants of these resistances are frequently found on small extrachromosomal plasmids and transposons. Sometimes the resistances are associated with detoxifying enzymes. This is true for the Hg²⁺ → Hg⁰ reductase, the As³⁺ → As⁵⁺ oxidase and the Cr⁶⁺ → Cr³⁺ reductase. In other cases, such as As⁵⁺, Ag⁺ and Cd²⁺, no change in redox state occurs but, rather, uptake and transport differences accompany resistance determinants. This article summarizes what is known of bacterial metal resistances for which enzymatic detoxification is known to be the mechanism of resistance. The characteristics and functions of the enzymes are described, as well as a summary of the newer DNA sequence analysis (basic science) and bench-scale efforts (applied science) for the mercuric resistance system.     

Genotoxic effects of heavy metals in rat hepatocytes

The genotoxic interaction of metals, which are common environmental contaminants, was studied in cultured hepatocytes. Freshly isolated rat hepatocytes were exposed to concentrations of cadmium, copper, silver and lead salts ranging from non-cytotoxic to moderately cytotoxic (as determined by LDH release), and the incorporation of [³H]thymidine into the DNA, as a measure of repair synthesis, was followed. In addition, the uptake of metals by the nuclear fraction was determined using Inductively Coupled Plasma/Mass Spectrometry or atomic absorption spectrophotometry. The evaluation of binding of ¹⁰⁹Cd to the DNA in situ was also attempted. It was observed that after a 20 h exposure period, all the metals investigated were found in the nuclear fraction of hepatocytes, with Ag apparently being accumulated less efficiently. In parallel, Cd (0.18 to 1.8 µM) and Cu (7.9 to 78.5 µM) consistently produced a statistically significant stimulation of [³H]thymidine incorporation into the DNA, in the presence or absence of hydroxyurea while Ag was active only at the highest concentration tested (18.5 µM). In contrast, Pb failed to induce a UDS response at the levels used. Moreover, exposure of hepatocytes to 1.8 µM ¹⁰⁹CdCl₂ for 20 h led to a DNA binding ratio of 0.98 ± 0.23 ng Cd/ µg DNA. The present results support the view that the nucleus may be an important target organelle for metal toxicity.Abbreviations 2-AAF 2-acetylaminofluorene - Cd cadmium - HU hydroxyurea - lCP/MS inductively coupled plasma/mass spectrometry - Hg mercury - Ni nickel - UDS unscheduled DNA synthesis     

Pesticides and heavy metals in Danish streambed sediment

The role of streambed sediment as a sink for pesticides and heavy metals was investigated in 30 Danish lowland streams. The investigated streams drain catchments varying in hydrology, topography, soil type and land use. The <250 m newly accumulated fraction of the uppermost 1–2 cm layer of streambed sediment was analysed for 19 old and modern pesticides and 9 heavy metals. DDE was present in the sediment of all the streams. Of the herbicides, fungicides and insecticides currently in use, the most frequently detected was diuron (50.0%), fenpropimorph (66.7%) and lambda-cyhalothrin (6.7%), respectively. The pesticides detected in the highest concentration were fenpropimorph (1700 ng g^–1), propiconazole (130 ng g^–1) and isoproturon (110 ng g^–1). The heavy metals are listed in order of increasing median concentration: Cd (0.80 g g^–1), Co (9.1 g g^–1), As (12.0 g g^–1), Ni (19.0 g g^–1), Cr (19.2 g g^–1), Pb (19.7 g g^–1), Cu (20.1 g g^–1), V (28.5 g g^–1), Zn (103 g g^–1). The average number of pesticides detected in the 27 streams draining predominantly agricultural catchments was (3.7±2.0) being higher (p=0.077) than in the three streams draining non-agricultural catchments (1.7±0.6). Pesticides were significantly related to catchment size, soil type and hydrological regime. Several heavy metals (Cr, Cu, Pb, V and Zn) were related to urban activity and soil type.     

Distribution of extractable heavy metals in different soil fractions

Abstract

Due to the difficulties of precisely characterizing environmentally contaminated soil, the effects of heavy metals on plants are studied using uncontaminated soil spiked with known quantities of heavy metals. One problem in using spiked soils is how accurately the distribution of metals mimics stabilized natural soils. We studied the distribution of cadmium, chromium, copper, lead, nickel, and zinc in soil fractions after application in soluble form. The soil samples included a control (an uncontaminated Typic Argiudoll) and two samples spiked with either a moderate or high heavy metal concentration). After application of the salts the soils were subjected to wet/dry cycles over the course of three months. The soils were fractionated using a sequential chemical extraction procedure employing: (1) CaCl₂,(2) NaOH, (3) Na₂EDTA and (4) HNO₃, HCl, and HF. Soil physical separation was carried out by ultrasonic dispersion. The heavy metal levels were determined using ICP-AES. Each heavy metal displayed a unique behavior when added to soil in the form of soluble salts. Cadmium and zinc remained in the soluble fraction, indicating that no equilibrium was attained, while nickel primarily appeared in the insoluble fraction. Chromium, copper and lead were distributed among various soil chemical fractions. The highest levels of all metals appeared in the clay fraction except lead which was mainly present in the silt fraction.     

淮河安徽段水及沉积物中重金属的研究

对采集淮河安徽段水及沉积物样品,利用ICP-AES进行重金属分析,结果表明砷、铅、铬超标,在沉积物中的含量最多。研究区域的重金属开始富集于生物体内,已对水生态系统及水产品安全产生影响,应进一步加强检测工作,以便及时采取相应防治对策。