不同程度镉污染农田中粉葛镉富集转运特征

探究不同程度镉（Cd）污染土壤对粉葛植株Cd积累分配特征的影响,为Cd污染农田的植物修复提供参考依据.在不同Cd污染［ω（Cd）为0.32~38.08 mg ·kg^-1］农田开展多点试验,分析了粉葛主要生育期不同部位生物量、Cd含量、Cd积累量及其富集和转运系数.结果表明,研究区粉葛块根干重为5.04~11.98 t ·hm^-2,生物量为13.21~29.07 t ·hm^-2,Cd积累量为15.74~106.03 g ·hm^-2;粉葛对Cd的吸收规律表现为：主藤>叶片>侧枝>葛头>块根;随着土壤Cd含量的增加,粉葛各部位Cd含量均显著增加（P<0.05）,而生物量均显著降低（P<0.05）;粉葛地上部Cd富集和转运系数呈先增大后减小的变化趋势,而根部Cd富集和转运系数均逐渐减小.相关分析表明,土壤Cd含量是影响粉葛Cd积累的关键因素.在轻中度Cd污染下,粉葛经济部分（葛粉）ω（Cd）为0.03~0.22 mg ·kg^-1,均低于药用植物的标准限值（≤0.30 mg ·kg^-1）;在中度污染粉葛地上部Cd富集和转运系数分别为2.43~7.97和3.02~9.81.粉葛具有很强的Cd富集和运输能力,是适合用作Cd污染土壤修复的潜力植物.     

Ability of Agrogyron elongatum to accumulate the single metal of cadmium, copper, nickel and lead and root exudation of organic acids

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Does hyperaccumulated nickel affect leaf decomposition? A field test using Senecio coronatus (Asteraceae) in South Africa

Summary. Nickel hyperaccumulator plants contain unusually elevated levels of Ni (>1,000 mg Ni kg⁻¹). The high Ni concentration of hyperaccumulator tissues may affect ecosystem processes such as decomposition, but this has yet to be studied under field conditions. We used Senecio coronatus Thunb. (Harv.) from two pairs of serpentine sites: one member of each pair contained a hyperaccumulator population and the other a non-hyperaccumulator population. Our main goal was to determine if leaf Ni status (hyperaccumulator or non-hyperaccumulator) affected leaf decomposition rate on serpentine sites. We also used a non-serpentine site on which leaves from all four S. coronatus populations were placed to compare decomposition at a single location. Dried leaf fragments were put into fine-mesh (0.1 mm) nylon decomposition bags and placed on field sites in mid-summer (early February) 2000. Sets of bags were recovered after 1, 3.5, and 8 months, their contents dried and weighed, and the Ni concentration and total Ni content of high-Ni leaves was measured. For the serpentine sites, there was no significant effect of leaf Ni status or site type on decomposition rates at 1 and 3.5 months. By 8 months, leaf Ni status and site type significantly influenced decomposition on one pair of sites: hyperaccumulator leaves decomposed more slowly than non-hyperaccumulator leaves, and leaves of both types decomposed more slowly on the non-hyperaccumulator site. At the non-serpentine site, the highest-Ni leaves (15,000 mg Ni kg⁻¹) decomposed more slowly than all others, but leaves containing 9,200 mg Ni kg⁻¹ did not decompose more slowly than non-hyperaccumulator leaves. Nickel in decomposing hyperaccumulator leaves was released rapidly: after 1 month 57–68% of biomass was lost and only 9–28% of original Ni content remained. We conclude that very high (>10,000 mg Ni kg⁻¹) leaf Ni concentrations may slow decomposition and that Ni is released at high rates that may impact co-occurring litter- and soil-dwelling organisms.     

Reactive oxygen species metabolism during the cadmium hyperaccumulation of a new hyperaccumulator Sedum alfredii （Crassulaceae）

Sedum alfredii Hance, a newly discovered hyperaccumulator, could serve as a good material for phytoremediation Cd polluted sites. Malondialdehyde (MDA), reactive oxygen species (ROS) and antioxidases (catalase (CAT); superoxide dismutase (SOD); peroxidase (POD)) in the leaf were determined when S. alfredii was treated for 15 d with various CdCl2 concentrations ranging from 0 to 800 μmol/L. The results showed that the production rate of 2′,7′-dichlorofluorescein (DCF), which is an indicator of ROS level, reached up to the maximum at 400 μmol/L CdCl2 and then declined with the increase of CdCl2 concentration, while MDA accumulation tended to increase. CAT activity was significantly inhibited at all tested CdCl2 concentrations and SOD activity was sharply suppressed at 800 μmol/L CdCl2. However, the enhancement of POD activity was observed when CdCl2 concentration was higher than 400 μmol/L. In addition, its activity increased when treated with 600 μmol/L CdCl2 for more than 5 d. When sodium benzoate, a free radical scavenger, was added, S. alfredii was a little more sensitive to Cd toxicity than that exposed to Cd alone, and the Cd accumulation tended to decline with the increase of sodium benzoate concentration. It came to the conclusions that POD played an important role during Cd hyperaccumulation, and the accumulation of ROS induced by Cd treatment might be involved in Cd hyperaccumulation.     

Cd-Pb复合污染条件下3种花卉植物的生长反应及超积累特性研究

采用水培实验方法,研究了3种耐性较强的花卉植物在Cd-Pb复合污染条件下的生长反应及可能的超积累特性.结果表明,花卉植物种不同,其对复合污染的生长反应也不同,它们的耐性大小顺序为:蜀葵(Althaea rosea Cav.)＞凤仙花(Impatiens Balsamina L.)＞金盏菊(Calendula officinalis L.);Cd对植物生长的影响较大、Pb的影响相对较小.3种花卉植物对重金属的积累量都是根部大于地上部;蜀葵对重金属Cd具有很强的耐性和积累性,在Cd、Pb复合污染条件下极具植物修复的潜力.对于这3种花卉植物,Cd-Pb相互作用效应与多种因素有关,包括重金属之间的浓度组合、植物种和植株部位等,表现得极为复杂,不仅仅是单纯的加和、拮抗或协同作用.     

植物超富集砷机制研究的最新进展

砷污染是全球环境热点问题之一,土壤砷污染治理是一个急需解决的难题.随着不同砷超富集植物的发现,植物修复技术因其投资和维护成本低、不易造成二次污染等优点而成为国际学术界研究的热点和前沿领域.深入理解超富集植物体内砷代谢和富集机制是有效利用植物修复技术来治理砷污染土壤的关键.近年来,植物超富集砷机制的研究取得了很大进展.已有的研究结果证明,蜈蚣草(P.vittata)对砷的吸收和转运能力显著高于非超富集植物,转运到地上部的砷主要储存在羽叶细胞的液胞中;蜈蚣草具有很强的抗氧化胁迫能力和五价砷(As(Ⅴ))还原能力;菌根共生有利于蜈蚣草的生长和砷的富集.有关植物超富集砷机制的分子生物学研究也取得了可喜的进展.砷酸盐还原酶基因(PvACR2)和植络素合成酶基因(PvPCS1)都被克隆并表征,cTPI同源基因(PV4-8)也被证明具有将As(Ⅴ)还原成三价砷(As(Ⅲ))的功能.尽管植物超富集砷机制的研究取得了迅速进展,但至今学术界仍没有全面理解为什么这些蕨类植物具有超富集砷的功能,相关功能基因、酶和转运蛋白的研究有待进一步深入.     

Assessment of Ni accumulation capability by fungi for a possible approach to remove metals from soils and waters

ABSTRACT

Abandoned industrial sites and mines may constitute possible hazards for surrounding environment due to the presence of toxic compounds that may contaminate soils and waters. The possibility to remove metal contaminants, specifically nickel (Ni), by means of fungi was presented exploiting a set of fungal strains isolated from a Ligurian dismissed mine. The achieved results demonstrate the high Ni(II) tolerance, up to 500 mg Ni l^?1, and removal capability of a Trichoderma harzianum strain. This latter hyperaccumulates up to 11,000 mg Ni kg^?1, suggesting its possible use in a bioremediation protocol able to provide a sustainable reclamation of broad contaminated areas.     

应用植物重金属超富集机理修复土壤复合污染的研究现状与展望

超积累植物在修复土壤重金属污染中起着重要的作用,但由于重金属复合污染的存在,许多植物并未能完全适用于实际修复中。本文通过阐述土壤重金属复合污染,参考近年来国际上对超积累植物富集机理的研究,从土壤重金属复合污染自身的交互作用,超积累植物根系活化机理,吸收和运输通道机制,金属配位体的运输与解毒作用,以及细胞分室化现象等各个阶段探讨与展望土壤重金属复合污染修复研究问题。     

铅锌矿区植物对重金属吸收和富集特征研究

通过实地调查分析贵州都匀牛角塘铅锌矿区土壤中重金属Pb、Cu、Cd的含量,采集9种矿区常见优势植物,对比植物对Pb、Cu和Cd的吸收、转运和富集特征.结果表明,矿区土壤受Pb和Cd两种金属污染严重,植物体内Pb、Cd含量都超过正常范围;在调查的9种植物中,桑科的地果地上部分Pb、Cd的含量最高,富集系数1.32、0.9...