砷超富集植物蜈蚣草原生质体的分离及其抗砷性分析

蜈蚣草(Pteris vittata)是一种砷超富集植物, 能够通过根从土壤中吸收砷, 并将其输送至羽叶中富集。为了探索蜈蚣草单个细胞在砷积累和砷抗性中的特性, 本文首次通过酶解方法获得了这一砷超富集蕨类植物的原生质体, 并研究了原生质体在不同浓度砷胁迫下的生活力。结果显示, 蜈蚣草原生质体的抗砷性远高于烟草原生质体的抗砷性, 与其整体植株的抗性一致。这为探索砷抗性和超富集机理提供了一个新的研究体系。     

蜈蚣草中砷超富集的分子机制研究进展

砷是一种毒性很强的类金属元素,土壤砷污染可引发一系列食品安全问题,进而威胁人类健康。蜈蚣草具有极强的富集砷的能力,在砷污染土壤的植物修复中具有重要的应用价值。深入阐释蜈蚣草超富集砷的分子机制是植物修复技术的核心理论基础。文中综述了蜈蚣草超富集砷的组学研究进展,以及目前鉴定到的砷富集过程中的重要分子元件,并对未来的研究方向和趋势进行了展望。     

砷超富集植物蜈蚣草原生质体的分离及其抗砷性分析

蜈蚣草（Pteris vittata）是一种砷超富集植物,能够通过根从土壤中吸收砷,并将其输送至羽叶中富集.为了探索蜈蚣草单个细胞在砷积累和砷抗性中的特性,本文首次通过酶解方法获得了这一砷超富集蕨类植物的原生质体,并研究了原生质体在不同浓度砷胁迫下的生活力.结果显示,蜈蚣草原生质体的抗砷性远高于烟草原生质体的抗砷性,与其整体植株的抗性一致.这为探索砷抗性和超富集机理提供了一个新的研究体系.     

大叶井口边草——一种新发现的富集砷的植物

自 1 999年以来对位于湖南省一些高砷区的植物和土壤进行了一系列的野外调查 ,以着力寻找砷的超富集植物。结果表明 ,与砷超富集植物蜈蚣草同属的另一种植物——大叶井口边草 ,对砷也具有显著的富集特征。这一发现为研究揭示砷在植物中的超富集机理提供了一种新的材料。建议深入开展蜈蚣草与大叶井口边草这两种砷富集植物的对比研究。     

大叶井边草——一种新发现的富集砷的植物

自1999年以来对位于湖南省一些高砷区的植物和土壤进行了一系列的野外调查,以着力寻找砷的超富集植物。结果表明,与砷超富集植物蜈蚣草同属的另一种植物－－大叶井口边草,对砷也具有显著的富集特征。这一发现为研究揭示砷在植物中的超富集机理提供了一种新的材料,建议深入开展蜈蚣草与大叶井口边草这两种砷富集植物的对比研究。     

不同生态型摩西球囊霉菌株对蜈蚣草砷吸收的影响

砷超富集植物——蜈蚣草无论是在野外或是在室内均能被丛枝菌根真菌(AM真菌)侵染,但其对蜈蚣草砷吸收及转运的机理尚不清晰.本研究将分离于湖南省郴州市金川塘某铅锌尾矿蜈蚣草根际土壤(Glomus mosseae BGC GD01,简称污染菌株)和云南省未污染土壤(G.mosseae BGC YN05,简称非污染菌株)的2种摩西球囊霉菌株分别接种于非污染生态型和污染生态型蜈蚣草根际,8周后利用菌根化蜈蚣草幼苗在浓度为100 μmol·L-1砷(Na2HAsO4·7H2O)营养液中进行为期24 h的水培试验.结果表明,2种生态型摩西球囊霉菌株分别与蜈蚣草形成中等程度侵染,侵染率为25.2％ ～31.3％.无论是接种污染菌株或是非污染菌株,均明显促进了蜈蚣草根部对磷的吸收.在24 h水培试验期间,接种非污染菌株显著促进了蜈蚣草根部砷的吸收,但接种污染菌株对蜈蚣草根部砷吸收的促进作用有限,说明AM真菌对蜈蚣草砷吸收存在种内差异.     

砷对土壤-蜈蚣草系统中磷生物有效性的影响

磷是植物必需的大量营养元素,而其同族元素砷却不是植物生长发育所必需的。通过等温吸附平衡实验发现土壤中存在的砷可以降低褐土对磷的吸附,褐土对砷的吸附率大于等于褐土对磷的吸附率。对砷超富集植物蜈蚣草而言,土壤中砷的添加量不超过800mg／kg时,蜈蚣草地上部和地下部磷含量显著提高,结果初步表明,砷可以提高土壤中磷的生物有效性。     

蜈蚣草毛状体对砷的富集作用及其意义

利用配备EDX的环境扫描电子显微镜等手段研究了蜈蚣草羽叶的微形态及砷元素在蜈蚣草中的微区分布. 结果表明, 在羽叶的正反表皮观察到大量的毛状体, 其结构为多细胞组成, 呈匍匐状, 平均长度为160 μm, 平均直径28 μm. X射线能谱分析表明, 在加砷处理中, 蜈蚣草的表皮、羽叶毛状体存在有明显的砷峰, 并且毛状体中砷的含量分别为表皮细胞与叶肉细胞的2.4, 3.9倍, 在同一毛状体中, 帽细胞中的砷含量较低, 而在节细胞和基细胞中的砷含量较高. 这一发现为揭示蜈蚣草富集砷和耐砷毒的机理提供了新的线索.     

AM真菌对蜈蚣草根围土壤砷形态及其砷吸收的影响

为探明AM真菌对蜈蚣草Pteris vittata根围土壤砷形态及其吸收砷的效应,采用盆栽实验,接种摩西管柄囊霉Funneliformis mosseae(Fm)、幼套近明球囊霉Claroideoglomus etunicatum(Ce)和变形球囊霉Glomus versiforme(Gv)。实验结果表明:接种Ce处理对蜈蚣草根围p H影响不显著,但提高了根围土壤中非专性吸附态砷、结晶水合铁铝氧化物结合态砷比例,分别达35%和13%,同时降低了无定形和弱结晶水合铁铝氧化物结合态砷、残渣态砷比例,分别达3%和11%。蜈蚣草生物量及其体内砷浓度分别提高了111%和15%。研究表明接种Fm或Ce处理相比接种Gv处理对提高根围土壤中弱吸附态砷比例或降低较强吸附态砷比例的效果更好。而与接种Fm和Gv处理相比,接种Ce处理对提高蜈蚣草生物量及砷浓度、砷累积量的效果更显著。接种Ce可显著提高蜈蚣草对砷的提取效率,研究结果为蜈蚣草-AM真菌联合修复As污染土壤提供了技术指导。     

砷、钙对蜈蚣草中金属元素吸收和转运的影响

蜈蚣草是砷的超富集植物和钙质土壤的指示植物。本试验在砂培条件下,研究砷、钙对蜈蚣草吸收和转运必需金属元素K、Mg、Mn、Fe、Zn和Cu的影响。结果表明。提高营养液中的砷浓度显著降低根部Mg和Zn的吸收。但对根部其它元素的浓度没有明显影响;叶柄中的Mn和地上部的Fe浓度因介质中添加砷而显著减少。其它元素在地上部的分布不受抑制。添加砷限制Fe从地下部向地上部转运,但促进其从叶柄向羽叶中运输;另外,还显著促进Mn由叶柄向羽叶和Zn由根向羽叶的转运。提高钙处理浓度对蜈蚣草吸收Fe、Zn、Cu无显著影响,但显著限制K、Mg和Mn的吸收。Mn是研究的6种金属元素中惟一一种明显向地上部转运富集的元素。从根部到羽叶中。金属元素间的相关性增强,在根部Ca与各种金属元素都无相关性;叶柄中Ca和Fe浓度呈极显著正相关;在羽叶中,Ca与K、Mg、Mn和Zn浓度呈显著负相关。     

Antioxidant responses of hyper-accumulator and sensitive fern species to arsenic

Plant species capable of hyper-accumulating heavy metals are of considerable interest for phytoremediation, and differ in their ability to accumulate metals from the environment. This work aims to examine (i) arsenic accumulation in three fern species [Chinese brake fern (Pteris vittata L.), slender brake fern (Pteris ensiformis Burm. f.), and Boston fern (Nephrolepis exaltata L.)], which were exposed to 0, 150, or 300 muM of arsenic (Na(2)HAsO(4).7H(2)O), and (ii) the role of anti-oxidative metabolism in arsenic tolerance in these fern species. Arsenic accumulation increased with an increase in arsenic concentration in the growth medium, the most being found in P. vittata fronds showing no toxicity symptoms. In addition, accumulation was highest in the fronds, followed by the rhizome, and finally the roots, in all three fern species. Thiobarbituric acid-reacting substances, indicators of stress in plants, were found to be lowest in P. vittata, which corresponds with its observed tolerance to arsenic. All three ferns responded differentially to arsenic exposure in terms of anti-oxidative defence. Higher levels of superoxide dismutase, catalase, and ascorbate peroxidase were observed in P. vittata than in P. ensiformis and N. exaltata, showing their active involvement in the arsenic detoxification mechanism. However, no significant increase was observed in either guaiacol peroxides or glutathione reductase in arsenic-treated P. vittata. Higher activity of anti-oxidative enzymes and lower thiobarbituric acid-reacting substances in arsenic-treated P. vittata correspond with its arsenic hyper-accumulation and no symptoms of toxicity.     

Expression of a Pteris vittata glutaredoxin PvGRX5 in transgenic Arabidopsis thaliana increases plant arsenic tolerance and decreases arsenic accumulation in the leaves

Chinese brake fern Pteris vittata hyperaccumulates arsenic in its fronds. In a study to identify brake fern cDNAs in arsenic resistance, we implicated a glutaredoxin, PvGRX5, because when expressed in Escherichia coli , it improved arsenic tolerance in recombinant bacteria. Here, we asked whether PvGRX5 transgenic expression would alter plant arsenic tolerance and metabolism. Two lines of Arabidopsis thaliana constitutively expressing PvGrx5 cDNA were compared with vector control and wild-type lines. PvGRX5-expressors were significantly more tolerant to arsenic compared with control lines based on germination, root growth and whole plant growth under imposed arsenic stress. PvGRX5-expressors contained significantly lower total arsenic compared with control lines following treatment with arsenate. Additionally, PvGRX5-expressors were significantly more efficient in their arsenate reduction in vivo . Together, our results indicate that PvGRX5 has a role in arsenic tolerance via improving arsenate reduction and regulating cellular arsenic levels. Paradoxically, our results suggest that PvGRX5 from the arsenic hyperaccumulator fern can be used in a novel biotechnological solution to decrease arsenic in crops.     

Phytoremediation of arsenic-contaminated groundwater by the arsenic hyperaccumulating fern Pteris vittata L

Arsenic concentrations in a much larger fraction of U.S. groundwater sources will exceed the maximum contaminant limit when the new 10 microg L(-1) EPA standard for drinking water takes effect in 2006. Thus, it is important to develop remediation technologies that can meet this new standard. Phytoremediation of arsenic-contaminated groundwater is a relatively new idea. In this research, an arsenic-hyperaccumulating fern, commonly known as Chinese Brake fern (Pteris vittata L.), was grown hydroponically to examine its effectiveness in arsenic removal from what is believed to be herbicide-contaminated groundwater. One plant grown in 600 mL of groundwater effectively reduced the arsenic concentration from 46 to less than 10 microg L(-1) in 3 days. Re-used plants continued to take up arsenic from the groundwater, albeit at a slower rate (from 46 to 20 microg L(-1) during the same time). Young fern plants were more efficient in removing arsenic than were older fern plants of similar size. The addition of a supplement of phosphate-free Hoagland nutrition to the groundwater had little effect on arsenic removal, but the addition of phosphate nutrition significantly reduced its arsenic affinity and, thus, inhibited the arsenic removal. This study suggested that Chinese Brake has some potential to remove arsenic from groundwater.     

Phytoremediation of arsenic contaminated soil by Pteris vittata L. II. Effect on arsenic uptake and rice yield

A greenhouse experiment evaluated the effect of phytoextraction of arsenic from a contaminated soil by Chinese Brake Fern (Pteris vittata L.) and its subsequent effects on growth and uptake of arsenic by rice (Oryza sativa L.) crop. Pteris vittata was grown for one or two growing cycles of four months each with two phosphate sources, using single super phosphate (SSP) and di-ammonium phosphate (DAP). Rice was grown on phytoextracted soils followed by measurements of biomass yield (grain, straw, and root), arsenic concentration and, uptake by individual plant parts. The biomass yield (grain, straw and rice) of rice was highest in soil phytoextracted with Pteris vittata grown for two cycles and fertilized with diammonium phosphate (DAP). Total arsenic uptake in contaminated soil ranged from 8.2 to 16.9 mg pot(-1) in first growing cycle and 5.5 to 12.0 mg pot(-1) in second growing cycle of Pteris vittata. There was thus a mean reduction of 52% in arsenic content of rice grain after two growing cycle of Pteris vittata and 29% after the one growing cycle. The phytoextraction of arsenic contaminated soil by Pteris vittata was beneficial for growing rice resulted in decreased arsenic content in rice grain of <1 ppm. There was a mean improvement in rice grain yield 14% after two growing cycle and 8% after the one growing cycle of brake fern.     

Effectiveness of applying arsenate reducing bacteria to enhance arsenic removal from polluted soils by Pteris vittata L

Arsenic is a common contaminant in soils and water. It is well established that the fern Pteris vittata L. is an As hyperaccumulator and therefore has potential to phyroremediate As-polluted soils. Also, it is accepted that rhizosphere microflora play an enhancing role in plant uptake of metallic elements from soils. Studies showed that hydroponiclly grown P. Vittata accumulated arsenite more than the arsenate form of As apparently because arsenate and phosphate are analogues and therefore its absorption is inhibited by phosphate. The objective of this study was to determine whether addition of five different arsenate-reducing bacteria would enhance arsenic uptake by P. vittata grown in arsenic polluted soils in afield experiment. Results showed that addition of the As reducing bacteria promoted the growth of P. vittata, increased As accumulation, activated soil insoluble As, and reduced As leaching compared to the untreated control. Plant biomass increased by 53% and As uptake by 44%. As leaching was reduced by 29% to 71% depending on the As reducing bacterium. The results in their entirety permitted some insight into the mechanisms by which the arsenate reducing bacteria enhanced the effectiveness of P. vittata to remove As from the polluted soil.     

The potential of Thelypteris palustris and Asparagus sprengeri in phytoremediation of arsenic contamination

The potential of two plants, Thelypteris palustris (marsh fern) and Asparagus sprengeri (asparagus fern), for phytoremediation of arsenic contamination was evaluated. The plants were chosen for this study because of the discovery of the arsenic hyperaccumulating fern, Pteris vittata (Ma et al., 2001) and previous research indicating asparagus fern's ability to tolerate > 1200 ppm soil arsenic. Objectives were (1) to assess if selected plants are arsenic hyperaccumulators; and (2) to assess changes in the species of arsenic upon accumulation in selected plants. Greenhouse hydroponic experiments arsenic treatment levels were established by adding potassium arsenate to solution. All plants were placed into the hydroponic experiments while still potted in their growth media. Marsh fern and Asparagus fern can both accumulate arsenic. Marsh fern bioaccumulation factors (> 10) are in the range of known hyperaccumulator, Pteris vittata Therefore, Thelypteris palustris is may be a good candidate for remediation of arsenic soil contamination levels of < or = 500 microg/L arsenic. Total oxidation of As (III) to As (V) does not occur in asparagus fern. The asparagus fern is arsenic tolerant (bioaccumulation factors < 10), but is not considered a good potential phytoremediation candidate.     

Comparison of root absorption, translocation and tolerance of arsenic in the hyperaccumulator Pteris vittata and the nonhyperaccumulator Pteris tremula

* Several fern species can hyperaccumulate arsenic, although the mechanisms are not fully understood. Here we investigate the roles of root absorption, translocation and tolerance in As hyperaccumulation by comparing the hyperaccumulator Pteris vittata and the nonhyperaccumulator Pteris tremula. * The two species were grown in a pot experiment with 0-500 mg As kg-1 added as arsenate, and in a short-term (8 h) uptake experiment with 5 microM arsenate under phosphorus-sufficient conditions. * In the pot experiment, P. vittata accumulated up to 2500 mg As kg-1 frond d. wt and suffered no phytotoxicity. P. tremula accumulated<100 mg As kg-1 frond d. wt and suffered severe phytotoxicity with additions of >or=25 mg As kg-1. In the short-term uptake experiment, P. vittata had a 2.2-fold higher rate of arsenate uptake than P. tremula, and distributed more As taken up to the fronds (76%) than did P. tremula (9%). * Our results show that enhanced root uptake, efficient root-to-shoot translocation, and a much elevated tolerance through internal detoxification all contribute to As hyperaccumulation in P. vittata.     

Phytoremediation of an arsenic-contaminated site using Pteris vittata L.: a two-year study

A field study was conducted to determine the efficiency of Chinese brake fern (Pteris vittata L.), an arsenic hyperaccumulator, on removal of arsenic from soil at an arsenic-contaminated site. Chinese brake ferns were planted on a site previously used to treat wood with chromated copper arsenate (CCA). Arsenic concentrations in surface and profile soil samples were determined for 2000, 2001, and 2002. In both 2001 and 2002, senesced and senescing fronds only, as well as all fronds, were harvested. Frond arsenic concentrations were not significantly different between the three harvests. Compared to senesced fronds, live fronds resulted in the greatest amount of arsenic removal. There were no significant differences in soil arsenic concentrations between 2000, 2001, and 2002, primarily due to the extreme variability in soil arsenic concentrations. However, the mean surface soil arsenic was reduced from 190 to 140 mg kg(-1). Approximately 19.3 g of arsenic were removed from the soil by Chinese brake fern. Therefore, this fern is capable of accumulating arsenic from the CCA -contaminated site and may be competitive, in terms of cost, to conventional remediation systems. However, better agronomic practices are needed to enhance plant growth and arsenic uptake to obtain maximum soil arsenic removal and to minimize remediation time.