紫色非硫细菌的砷代谢机制

[目的]系统阐述紫色非硫细菌(PNSB)砷代谢机制和砷代谢基因簇的进化关系.[方法]通过生物信息学方法分析了PNSB砷代谢基因簇的分布、组成、排布方式.采用UV-Vis和HPLC-ICP-MS方法,研究了3个PNSB种类对砷的抗性、砷形态及价态的转化、砷在细胞中的积累和分布以及磷酸盐对As细胞毒性的影响.[结果]砷基因簇分析表明:已公布全基因组序列的17个PNSB菌株基因组中均含有以ars operon为核心的砷代谢基因簇,由1-4个操纵子组成,主要含有与细胞质砷还原和砷甲基化代谢相关的基因,但基因的组成和排列方式因种和菌株而异,尤其是arsM和两类进化来源不同的arsC.实验结果表明:光照厌氧条件下,3个PNSB种类对As(V)和As(Ⅲ)均具有抗性,As(V)和As(Ⅲ)均能进入细胞 ;在胞内As(V)能够还原为As(Ⅲ)并被排出胞外,但不能将As(Ⅲ)氧化为As(V),也未检测到甲基砷化物 ;磷酸盐浓度升高,能够抑制As(V)进入细胞,降低As(V)对细胞的毒性,而不能抑制As(Ⅲ)进入细胞.[结论]PNSB砷代谢机制主体为细胞质As(V)还原,也还有砷甲基化途径.通过对砷代谢基因簇结构多样性特点和进化方式分析,提出了与Rosen不同的ars operon进化途径.这对深入开展PNSB砷代谢和基因之间的相互作用研究奠定基础.     

淹水条件对土壤砷形态转化的影响

通过淹水条件下的培养试验, 探讨了外源二甲基砷酸（DMA）、一甲基砷酸（MMA）、砷酸盐［As(V)］在土壤中的动态转化规律. 结果表明: 随着培养时间的推移, 加入土壤中的DMA和MMA均主要转化为As(V), 且土壤中As(V)含量均呈增加趋势, 培养到150 d时土壤中As(V)含量均显著高于1 d时的含量(P<0.01). 外源DMA通过脱甲基化作用, 在30 d内即基本转化为As(V), 且有少量的亚砷酸盐［As(Ⅲ)］生成; 而外源MMA的转化速度相对较慢, 培养60 d后才基本完成向As(V)的转化, 同时伴随少量DMA和As(Ⅲ)的生成; 在淹水条件下外源As(V)含量随培养时间的增加而逐渐降低,该过程中除有少量As(Ⅲ)生成外,其形态基本未发生改变.     

抗砷性微生物及其抗砷分子机制研究进展

砷(Arsenic, As)是一种剧毒类金属(Metalloid), 在自然环境中主要以三价亚砷酸盐[Arsenite, AsO2-, As(III)]和五价砷酸盐[Arsenate, AsO43-, As(V)]的无机形式广泛存在。许多微生物在含砷环境的长期适应过程中, 进化了多种不同的砷解毒抗性机制。目前研究发现主要存在4种类型的砷抗性机理, 包括: As(III)氧化, 细胞质As(V)还原, 呼吸性As(V)还原, As(III)甲基化, 这些机制赋予微生物砷抗性并在砷的转化和地球化学循环中起着极     

微生物耐砷机理及其在砷地球化学循环中的作用北大核心CSCD

砷是一种无处不在的有毒类金属,其强致癌性引起了人类的广泛关注。在自然环境中,砷的转化存在物理化学过程和生物过程,其中微生物介导的砷转化是环境砷行为的主要影响因素。微生物的耐砷特性与砷吸收、氧化还原、甲基化、区隔化和外排等过程密切相关。砷在微生物体内的转运转化主要与砷解毒有关,但某些微生物可利用氧化还原过程产生的能量以维持其生长需求。本文综述了微生物介导的砷吸收、转化、区隔化和外排机制,这对阐明砷的地球化学循环过程及指导砷污染土壤和水体修复、阻控农作物砷吸收等方面具有重要意义。     

超富集植物蜈蚣草中砷化学形态的EXAFS研究

采用同步辐射扩展X射线吸收精细结构(SREXAFS)技术研究了超富集植物蜈蚣草(PterisvittataL.)中As的化学形态及其在转运过程中的变化。结果表明,蜈蚣草中的As主要以As(Ⅲ)与O配位的形态存在。As(V)被植物吸收后,很快转化为As(Ⅲ),其转化过程主要发生在根部。As(Ⅲ)向地上部转运的过程中价态基本不变。在植物的根部和部分叶柄中存在少量与As-GSH相似的As-S结合方式,但是在As含量最高的羽叶中基本上未发现这种结合方式。与需要提取和分离过程的化学方法相比,采用EXAFS方法研究植物中的砷形态不需经过预分离或化学预处理就可以直接测定植物样品中元素的化学形态,因此可以避免样品预处理过程对As形态的干扰,并获得可靠的砷化学形态方面的信息。     

超富集植物蜈蚣草中砷化学形态的EXAFS研究

采用同步辐射扩展X射线吸收精细结构(SR EXAFS)技术研究了超富集植物蜈蚣草(Pteris vittata L.)中As的化学形态及其在转运过程中的变化.结果表明,蜈蚣草中的As主要以As(Ⅲ)与O配位的形态存在.As(Ⅴ)被植物吸收后,很快转化为As(Ⅲ),其转化过程主要发生在根部.As(Ⅲ)向地上部转运的过程中价态基本不变.在植物的根部和部分叶柄中存在少量与As-GSH相似的As-S结合方式,但是在As含量最高的羽叶中基本上未发现这种结合方式.与需要提取和分离过程的化学方法相比,采用EXAFS方法研究植物中的砷形态不需经过预分离或化学预处理就可以直接测定植物样品中元素的化学形态,因此可以避免样品预处理过程对As形态的干扰,并获得可靠的砷化学形态方面的信息.     

好气条件下不同形态外源砷在土壤中的转化

在35%的田间持水量下,通过模拟试验研究了外源二甲基砷酸盐（DMA）、一甲基砷酸盐（MMA）、五价无机砷［As(V)］在土壤中的形态转化.结果表明: 外源砷进入土壤后,其含量均有随时间推延而逐渐下降的趋势,两种不同形态的有机砷DMA和MMA在土壤中主要发生脱甲基化过程,经150 d的恒温恒湿培养,其在土壤中主要转化为As(V),DMA处理仅在120 d时检测到少量MMA,而MMA处理则在7～60 d内均有少量的DMA生成.培养结束时土壤中DMA和MMA含量均显著降低(P<0.01),降幅分别为99.5%、94.3%,而两者的主要转化产物As(V)的含量则分别显著增加了4.61和5.15倍.表明外源有机态砷在土壤中基本上被转化为无机形态;与有机态外源砷相比,外源As(V)进入土壤后其形态基本上没有发生转化.     

中国莲（Nelumbo nucifera）幼苗抗氧化系统对砷胁迫的响应

为了研究中国莲（Nelumbo nucifera）抗氧化系统对砷胁迫的响应,研究比较了两种不同价态无机砷As（Ⅲ）和砷As（V）对中国莲幼苗可溶性蛋白含量、丙二醛（MDA）含量以及抗氧化系统的影响。结果表明,中国莲幼苗中MDA和可溶性蛋白质含量随砷浓度的增加呈现先升高后降低的趋势。中国莲幼苗的MDA和蛋白质含量受As（V）的影响不如As（11]）敏感。抗氧化系统酶中,超氧化物歧化酶（SOD）对砷处理最敏感,当As（11I）浓度在2．5pmol／L和As（V）浓度在100μmol／L时,SOD酶活性显著高于对照组。过氧化物酶（POD）在As（Ⅲ）处理浓度为10umol／L时就出现显著上升,相对而言,过氧化氢酶（CAT）对As（V）比较敏感。实验结果表明,随着浓度的增加,砷对幼苗产生的氧化胁迫导致SOD、CAT和POD三种酶活性有所增加,以配合清除细胞内的活性氧自由基（ROS）,维持细胞代谢的稳定。本研究为进一步研究砷胁迫下莲的生理和生长变化、以及莲的培育和移植提供了部分基础数据。     

砷超富集植物中砷化学形态其转化的EXAFS研究

通过同步辐射扩展X射线吸收精细结构(SR EXAFS)研究砷超富集植物大叶井口边草(Pteris nervosa)中砷的化学形态及其在植物体中的转化. 结果表明, 在大叶井口边草中砷主要与O配位, 根部存在与谷胱苷肽(GSH)结合的砷, 但是在羽叶中没有发现与GSH结合的砷. 在NaAsO2和Na2HAsO4处理中, 植物根系的砷分别以As(Ⅲ)和 As(Ⅴ)为主, 但是在叶柄和羽叶中砷都以As(Ⅲ)的形态为主. 植物根系吸收的As(Ⅴ)在向上转运的过程中具有向As(Ⅲ)转化的趋势, 其转化过程主要发生在根部. 实验证明, 与GSH结合并不是大叶井口边草中砷解毒的主要机理, 超富集植物可能具有与一般耐性植物不同的重金属解毒机制.     

一株芽孢杆菌对含砷矿物中砷的还原作用

在自然环境中,砷通常吸附于铁氧化物、铝氧化物等金属氧化物矿物上,或与这些氧化物矿物形成共沉淀。厌氧条件下,微生物可能通过直接还原砷或者还原铁氧化物等载砷矿物从而影响砷的迁移转化。本研究筛选得到芽孢杆菌属的一株细菌DX-04,并研究了该菌株对不同形态砷酸盐的还原作用和还原途径。厌氧条件下,在12~24 h内菌株DX-04对溶解态砷的还原能力最强,溶解态砷对提高细菌生物量具有明显的促进作用。接种菌株DX-04的铁砷共沉淀培养基中液相As(III)浓度呈先升高后降低的趋势,砷发生还原与释放,进而发生二次沉淀再次被固持。当以载砷氧化铝矿物为载砷的模型矿物时,在DX-04菌株的还原作用下,吸附的As(V)首先从氢氧化铝矿物上释放到液相,进一步被还原为As(III)。微生物的这一作用能够引起含砷矿物中的砷向水体、沉积物环境中释放,成为人类健康的潜在威胁。     

EXAFS study on arsenic species and transformation in arsenic hyperaccumulator

As a cost-effective, efficient and environmental friendly method for the remediation of contaminated soils and waters, phytoremediation of arsenic-con- taminated soils has drawn more and more attention[1]. The plants with the special ability to accumulate arse-nic (hyperaccumulators) are a prerequisite for phy-toremediation. Cretan brake (Pteris cretica L. var nervosa Thunb) has been shown to accumulate arsenic as much as 694 mg/kg in pinna in field investigation[2], and such elevated arsenic…     

EXAFS study on arsenic species and transformation in arsenic hyperaccumulator

Synchrotron radiation extended X-ray absorption fine structure (SR EXAFS) was employed to study the transformation of coordination environment and the redox speciation of arsenic in a newly discovered arsenic hyperaccumulator, Cretan brake (Pteris cretica L. var nervosa Thunb). It showed that the arsenic in the plant mainly coordinated with oxygen, except that some arsenic coordinated with S as As-GSH in root. The complexation of arsenic with GSH might not be the predominant detoxification mechanism in Cretan brake. Although some arsenic in root presented as As(V) in Na₂HAsO₄ treatments, most of arsenic in plant presented as As(III)-O in both treatments, indicating that As(V) tended to be reduced to As(III) after it was taken up into the root, and arsenic was kept as As(III) when it was transported to the above-ground tissues. The reduction of As(V) primarily proceeded in the root.     

A subgroup of plant aquaporins facilitate the bi-directional diffusion of As(OH)<Subscript>3</Subscript> and Sb(OH)<Subscript>3</Subscript>across membranes

Background  

Arsenic is a toxic and highly abundant metalloid that endangers human health through drinking water and the food chain. The most common forms of arsenic in the environment are arsenate (As(V)) and arsenite (As(III)). As(V) is a non-functional phosphate analog that enters the food chain via plant phosphate transporters. Inside cells, As(V) becomes reduced to As(III) for subsequent extrusion or compartmentation. Although much is known about As(III) transport and handling in microbes and mammals, the transport systems for As(III) have not yet been characterized in plants.     

Arsenic induced oxidative stress in plants

Arsenic is a highly toxic metalloid for all forms of life including plants. Arsenic enters in the plants through phosphate transporters as a phosphate analogue or through aquaglycoporins. Uptake of arsenic in plant tissues adversely affects the plant metabolism and leads to various physiological and structural disorders. Photosynthetic apparatus, cell division machinery, energy production, and redox status are the major section of plant system that are badly affected by As (V). Similarly As (III) can react with thiol (-SH) groups of enzymes and inhibits various metabolic processes. Arsenic is also known to induce oxidative stress directly by generating reactive oxygen species (ROS) during conversion of its valence forms or indirectly by inactivating antioxidant molecules through binding with their -SH groups. As-mediated oxidative stress causes cellular, molecular and physiological disturbances in various plant species. Activation of enzymatic antioxidants namely, superoxide dismutase (SOD), ascorbate peroxidase (APX), catalase (CAT) and glutathione reductase (GR), Glutathione s-transferase, glutathione peroxidase (GPX) as well as non antioxidant compounds such as, ascorbate, glutathione, carotenoids are reported to neutralize arsenic mediated oxidative stress. Understanding of biochemistry of arsenic toxicity would be beneficial for the development of arsenic tolerant crops and other economically important plants.     

Arsenic tolerance in mesquite (Prosopis sp.): Low molecular weight thiols synthesis and glutathione activity in response to arsenic

The effects of arsenic stress on the production of low molecular weight thiols (LMWT), glutathione S-transferase activity (GST) and sulfur metabolism of mesquite plant (Prosopis sp.) were examined in hydroponic culture at different arsenic [As(III) and (V)] concentrations. The production of LMWT was dependent on As speciation and concentration in the growth medium. The roots of As(III) treated plants produced significantly higher LMWT levels than As(V) treated roots at the same concentration of As applied. In leaves, the thiols content increased with increasing As(III) and (V) concentrations in the medium. Hypersensitivity of the plant to high As concentrations was observed by a significant decrease of LMWT produced in the roots at 50 mg/L treatment in both As(III) and (V) treatments. Sulfur was translocated from roots and accumulated mainly in the shoots. In response to As-induced phytotoxicity, the plants slightly increased the sulfur content in the roots at the highest As treatment. Compared with As(V)-treated plants, As(III)-treated roots and leaves showed significantly higher GST activity. The roots of both As(III) and (V) treated plants showed an initial increase in GST at low As concentration (5 mg/L), followed by significant inhibition up to 50 mg/L. The leaves had the highest GST activity, an indication of the ability of the plant to detoxify As in the leaves than in the roots. The correlation between LMWT content, S content and GST activity may be an indication these parameters may be used as biomarkers of As stress in mesquite.     

Localization and speciation of arsenic in Glomus intraradices by synchrotron radiation spectroscopic analysis

The protective mechanisms employed by arbuscular mycorrhizal fungi (AMF) to reduce the toxic effects of arsenic on host plants remain partially unknown. The goal of this research was identifying the in situ localization and speciation of arsenic (As) in the AM fungus Rhizophagus intraradices [formerly named Glomus intraradices] exposed to arsenate [As(V)]. By using a two-compartment in vitro fungal cultures of R. intraradices-transformed carrot roots, microspectroscopic X-ray fluorescence (μ-XRF), and microspectroscopic X-ray absorption near edge structure (μ-XANES), we observed that As(V) is absorbed after 1 h in the hyphae of AMF. Three hours after exposure a decrease in the concentration of As was noticed and after 24 and 72 h no detectable As concentrations were perceived suggesting that As taken up was pumped out from the hyphae. No As was detected within the roots or hyphae in the root compartment zone three or 45 h after exposure. This suggests a dual protective mechanism to the plant by rapidly excluding As from the fungus and preventing As translocation to the plant root. μ-XANES data showed that gradual As(V) reduction occurred in the AM hyphae between 1 and 3 h after arsenic exposure and was completed after 6 h. Principal component analysis (PCA) and linear combination fitting (LCF) of μ-XANES data showed that the dominant species after reduction of As(V) by R. intraradices extra-radical hyphal was As(III) complexed with a reduced iron(II) carbonate compound. The second most abundant As species present was As(V)–iron hydroxides. The remaining As(III) compounds identified by the LCF analyses suggested these molecules were made of reduced As and S. These results increase our knowledge on the mechanism of As transport in AMF and validate our hypotheses that R. intraradices directly participates in arsenic detoxification. These fungal mechanisms may help AMF colonized plants to increase their tolerance to As at contaminated sites.     

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.     

Expressing ScACR3 in rice enhanced arsenite efflux and reduced arsenic accumulation in rice grains

Arsenic (As) accumulation in rice grain poses a serious health risk to populations with high rice consumption. Extrusion of arsenite [As(III)] by ScAcr3p is the major arsenic detoxification mechanism in Saccharomyces cerevisiae. However, ScAcr3p homolog is absent in higher plants, including rice. In this study, ScACR3 was introduced into rice and expressed under the control of the Cauliflower mosaic virus (CaMV) 35S promoter. In the transgenic lines, As concentrations in shoots and roots were about 30% lower than in the wild type, while the As translocation factors were similar between transgenic lines and the wild type. The roots of transgenic plants exhibited significantly higher As efflux activities than those of the wild type. Within 24 h exposure to 10 μM arsenate [As(V)], roots of ScACR3-expressing plants extruded 80% of absorbed As(V) to the external solution as As(III), while roots of the wild type extruded 50% of absorbed As(V). Additionally, by exposing the As-containing rice plants to an As-lacking solution for 24 h, about 30% of the total As derived from pre-treatment was extruded to the external solution by ScACR3-expressing plants, while about 15% of As was extruded by wild-type plants. Importantly, ScACR3 expression significantly reduced As accumulation in rice straws and grains. When grown in flooded soil irrigated with As(III)-containing water, the As concentration in husk and brown rice of the transgenic lines was reduced by 30 and 20%, respectively, compared with the wild type. This study reports a potential strategy to reduce As accumulation in the food chain by expressing heterologous genes in crops.     

The response of tomato (Lycopersicon esculentum) to different concentrations of inorganic and organic compounds of arsenic

Tomato plants were cultivated in greenhouse and water solutions of arsenite (As(III)), arsenate (As(V)), methylarsonic acid (MA) and dimethylarsinic acid (DMA) were applied individually into cultivation substrate at two As levels, 5 and 15 mg kg⁻¹ of the substrate. Comparing the availability of arsenic compounds increased in order arsenite = arsenate < MA < DMA where the arsenic contents in plants decreased during vegetation period. Within a single plant, the highest arsenic concentration was found in roots followed in decreasing order by leaves, stems, and fruits regardless of arsenic compound applied. Arsenic toxicity symptoms reflected in suppressed growth of plants and a lower number and size of fruits were most significant with DMA treatment. However, the highest accumulation of arsenic by plants growing in the soil containing DMA was caused by higher mobility of this compound in the soil due to its lower sorption affinity. Our results confirmed substantial role of transformation processes of arsenic compounds in soil in uptake and accumulation of arsenic by plants.