外源磷对苗期小麦和水稻根际砷形态及其生物有效性的影响

采用土(中度砷污染土)-土根袋培养的方法研究了两个浓度的外源磷(P)对苗期小麦和水稻根际砷(As)形态分布及其生物有效性的影响.结果表明:(1)两种作物生长的土壤中各砷形态的分配比例依次为:结晶铁锰或铁铝水化氧化物结合态(45%～52%)＞无定形和弱结晶铁铝或铁锰水化氧化物结合态(26%～34%)＞专性吸附态(12%～14%)＞残渣态(4%～7%)＞非专性吸附态(0.09%～0.25%).(2)添加外源磷浓度为100 mg·kg-1与不施磷处理相比显著提高了两种作物地上部的生物量(p＜0.01).(3)苗期小麦在添加100 mg·kg-1外源磷时,不仅促进了作物生长而且抑制根中砷向地上部的转运.(4)任何磷处理下,水稻对砷的吸收能力以及由根系向地上部转移能力均高于小麦.因此,在轻中度砷污染土壤上与水稻相比更适宜种植小麦(或其他旱作植物);而在水稻种植季,可以通过添加适量磷肥(100 mg·kg-1)来减弱砷在水稻体内的累积.     

不同AMF组合提高黄瓜抗根结线虫效果的比较

本研究旨在评价不同组合丛枝菌根真菌(arbuscular mycorrhizal fungi,AMF)抑制根结线虫和降低根结线虫病害的效应,以获得抗病作用较大的AMF组合。将由AMF光壁无梗囊霉Acaulospora laevis(Al)、摩西管柄囊霉Funneliformis mosseae(Fm)、幼套近明球囊霉Claroideoglomus etunicatum(Ce)、根内根孢囊霉Rhizophagus intraradices(Ri)、变形球囊霉Glomus versiforme(Gv)、珠状巨孢囊霉Gigaspora margarita(GIm)和全球盾巨孢囊霉Scutellospora aurigloba(SCa)组成的12个组合分别接种"津优35号"黄瓜,接种南方根结线虫Meloidogyne incognita并设置不接种对照。盆栽试验结果表明,接种AMF组合均能显著降低线虫卵囊数和每个卵囊的含卵数量,但Fm+Ri+GIm+SCa组合则增加根内二龄幼虫数、根内雌虫数和根内线虫总数;其他大多数组合能够抑制线虫的繁殖数量,其中,以Al+Fm+GIm及Fm+Ce+Gv组合抑制线虫生长发育的作用最大;除GIm+SCa组合外,其他AMF组合均能不同程度地降低线虫为害,防效达31%–83%,以Al+Fm+GIm组合处理的根结指数最低,防效最大。设施田间试验结果表明,以Al+Fm+GIm组合抗病作用最强。本研究表明,不同组合AMF防病效应差异显著,Al+Fm+Ce+Gv组合及Al+Fm+GIm是本试验条件下防治根结线虫病害效应最好的AMF组合,具有较大的应用潜力。     

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.     

接种丛枝菌根真菌对青冈栎幼苗生长和光合作用的影响

利用菌根真菌摩西球囊霉和根内球囊霉,对喀斯特地区造林树种青冈栎进行接种试验,测定菌根真菌对青冈栎幼苗生长、生物量和光合作用的影响。结果表明:接种丛枝菌根真菌能显著促进青冈栎幼苗株高、地径、叶面积和幼苗生物量的增长,并且能提高幼苗成活率和改善幼苗的光合能力。摩西球囊霉和根内球囊霉处理的青冈栎幼苗生物量分别是未接种处理的2.1和1.9倍;摩西球囊霉和根内球囊霉处理下的水分利用效率分别比对照处理提高了33.6%和8.8%;摩西球囊霉对青冈栎幼苗株高、地径、生物量的促进作用好于根内球囊霉,而根内球囊霉处理的幼苗叶面积、主根长、根冠比大于摩西球囊霉处理。总体而言,接种丛枝菌根真菌特别是摩西球囊霉能促进青冈栎幼苗的生长和生物量增长,在石漠化植被恢复中具有潜在应用价值。     

接种AM真菌和施加铁可协同降低水稻砷累积

采用外源添加砷(As)的土培模拟试验探究了接种丛枝菌根真菌(AMF)异形根孢囊霉Rhizophagus irregularis和外源添加铁(Fe)对水稻Oryza sativa根表铁膜形成以及水稻累积砷的影响。结果表明,根表铁膜能够吸附大量的磷和砷。添加砷促进了根表铁膜的形成,而接种AMF后铁膜厚度显著降低。接种AMF改善了植物的磷营养状况,显著提高了水稻根系砷浓度,但降低了地上部砷浓度;砷污染情况下施加铁显著降低了接种处理水稻地上部的砷浓度。接种AMF+施加铁处理降低水稻地上部砷浓度的效果最大。这表明AMF+施加铁可协同抑制水稻地上部砷积累。该研究结果为在高砷背景值土壤中种植粮食作物并保障食品安全提供了一条可供选择的技术途径。     

AM真菌对紫花苜蓿细根生长及其生物量动态特征的影响

细根对植物功能的发挥和土壤碳库及全球碳循环具有重要意义。采用容器法和微根管法于2013年6~10月整个生长季内对紫花苜蓿的细根生物量、生产以及周转规律进行研究。结果表明:(1)紫花苜蓿活细根现存生物量平均值以接种摩西球囊霉(Gm)处理最高(12.46g·m-2),未接种对照最低(7.31g·m-2),并且活细根现存量在9月中旬达到峰值;死细根现存生物量呈先增加后降低再增加的变化趋势,在整个生长过程中未接种处理高于接种处理,接种根内球囊霉(Gi)处理死细根现存平均生物量(3.11g·m-2)又较接种组其他处理低。(2)苜蓿植株细根生长量以接种幼套球囊霉(Ge)处理最大(0.045 mm·cm-2·d-1),接种Gm处理和未接种对照最低(均为0.027mm·cm-2·d-1);而未接菌植株细根死亡量(0.044mm·cm-2·d-1)显著高于接种植株,接种组又以Gi处理最低(0.021mm·cm-2·d-1)。(3)紫花苜蓿在生长季节内细根生产和死亡的高峰分别出现在8月底和10月份,低谷出现在9月底到10月中旬和6月底到8月;接种地表球囊霉(Gv)后细根现存量和年生长量显著高于对照和接种其他菌种处理,细根的周转以对照组最大,而接种Gv和Gm处理较低。研究发现,通过接种丛植菌根真菌可以提高苜蓿细根生物量,降低细根的死亡,增加细根寿命。     

AMF和PGPR对生姜青枯病的影响

丛枝菌根真菌(Arbuscular mycorrhizal fungi,AMF)与植物根围促生细菌(Plant growth-promoting rhizobacteria,PGPR)占据相近的生态位,对植物病原物及其所致病害的发生与发展具有重要影响。本试验旨在于温室盆栽条件下探索AMF摩西管柄囊霉(Funneliformis mosseae,Fm)、根内球囊霉(Glomus intraradices,Gi)和地表球囊霉(Glomus versiforme,Gv)与PGPR假单胞菌(Pseudomonus sp.)S1-10菌株和S3-11菌株的相互作用及其对生姜(Zingiber officinale)青枯病(Ralstonia solanacearum,RS1)的影响。试验结果表明Gv显著增加假单胞菌S3-11菌株在生姜根围的定殖数量(P0.05),除生姜幼苗期外Fm则能促进S3-11菌株和S1-10菌株在根围内的定殖。PGPR S1-10和S3-11显著促进发棵期和块茎膨大期生姜AMF的侵染;发棵期S1-10显著提高了Gi的侵染率,但显著降低了Gv的侵染率(P0.05);块茎膨大期S3-11对Gv侵染(64%)的促进作用最大。AMF或/和PGPR(除S1-10外)接种处理均不同程度地促进了生姜的生长,其中Gv+S3-11组合处理的生姜生长量最大,其次为Fm+S3-11组合。无论是单接种还是双接种,供试PGPR和AMF均显著提高叶片防御性酶超氧物歧化酶(SOD)、过氧化物酶(POD)、苯丙氨酸(PAL)和过氧化氢酶(CAT)活性,降低丙二醛(MDA)含量和生姜青枯病的病情指数,其中,以Gv+S3-11组合处理的病情指数最低(25.5),且防效最高(71%)。研究结果表明AMF地表球囊霉与PGPR假单胞菌S3-11菌株组合能够相互促进、协同抑制生姜青枯病菌、诱导生姜抗病性、促进生姜生和增加产量,是适宜生姜生长的优良AMF+PGPR组合。     

丛枝菌根真菌对刺槐热值、碳和灰分含量的影响北大核心CSCD

该试验以根内球囊霉(Glomus intraradices)和地表球囊霉(G.versiforme)为接种剂,研究了丛枝菌根真菌对刺槐(Robinia pseudoacacia)生物量、热值、含碳量、灰分、能量积累和碳素积累的影响。结果表明,接种根内球囊霉和地表球囊霉对提高刺槐生物量、热值、能量积累和碳素积累都起到了重要作用。接种根内球囊霉和地表球囊霉后刺槐的总生物量比对照分别增加了89.61%和91.34%,能量积累分别比对照增加102.20%和94.19%,碳素积累分别比对照增加93.30%和77.21%;同时发现刺槐的能量和碳主要分布在根系和叶,而茎中能量和碳所占的比例较小。接种根内球囊霉提高了刺槐的干重热值,其根、茎、叶的干重热值分别比对照增加7.72%、8.94%和8.41%;接种地表球囊霉也显著(p<0.05)提高了刺槐的干重热值,但其效果低于根内球囊霉。接种根内球囊霉显著(p<0.05)提高了刺槐根的含碳量,对茎和叶的含碳量影响不明显。接种根内球囊霉和地表球囊霉都显著(p<0.05)提高了刺槐茎和叶的去灰分热值。     

构树(Broussonetia papyrifera)幼苗氮、磷吸收对接种AM真菌的响应

对石灰岩适生植物构树(Broussonetia papyrifera)进行菌根真菌摩西球囊霉(Glomus mosseea)、地表球囊霉(G.versiforme)、透光球囊霉(G.diaphanum)的单独接种、混合接种和不接种处理,幼苗生长3个月后测定其根茎叶N、P含量和土壤酶活性,结果表明:接种AM真菌后构树幼苗生物量显著增加,植株根茎叶N含量较对照组显著提高,其含量为根<茎<叶。各处理中除了透光球囊霉处理的茎含量与对照差异不显著外,其余各处理含量均呈显著或极显著差异。AM真菌对构树苗P的促进效应主要体现在根、茎的利用上,而叶片P含量除混合接种外则有所降低,但M (接种处理)与M-(非接种处理)间无显著差异。构树苗根茎叶等量干物质P含量依次为叶>根>茎。进一步研究表明,接种AM真菌显著提高了土壤酶活性,这种显著性主要体现在蛋白酶和碱性磷酸酶上,植株N含量与土壤蛋白酶和碱性磷酸酶活性有显著相关性,而P含量只是根部吸收与多酚氧化酶活性显著相关。结果表明,接种AM真菌促进了宿主植物构树生物量的积累,提高了根际土壤酶活性,增加了植株对N、P的吸收。     

Effects of arbuscular mycorrhizal fungi on calorific value and contents of carbon and ash in Robinia pseudoacacia

该试验以根内球囊霉(Glomus intraradices)和地表球囊霉(G. versiforme)为接种剂, 研究了丛枝菌根真菌对刺槐(Robinia pseudoacacia)生物量、热值、含碳量、灰分、能量积累和碳素积累的影响。结果表明, 接种根内球囊霉和地表球囊霉对提高刺槐生物量、热值、能量积累和碳素积累都起到了重要作用。接种根内球囊霉和地表球囊霉后刺槐的总生物量比对照分别增加了89.61%和91.34%, 能量积累分别比对照增加102.20%和94.19%, 碳素积累分别比对照增加93.30%和77.21%; 同时发现刺槐的能量和碳主要分布在根系和叶, 而茎中能量和碳所占的比例较小。接种根内球囊霉提高了刺槐的干重热值, 其根、茎、叶的干重热值分别比对照增加7.72%、8.94%和8.41%; 接种地表球囊霉也显著(p < 0.05)提高了刺槐的干重热值, 但其效果低于根内球囊霉。接种根内球囊霉显著(p < 0.05)提高了刺槐根的含碳量, 对茎和叶的含碳量影响不明显。接种根内球囊霉和地表球囊霉都显著(p < 0.05)提高了刺槐茎和叶的去灰分热值。     

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.     

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…     

Effects of selenium on arsenic uptake in arsenic hyperaccumulator Pteris vittata L

Selenium (Se) is a non-metallic element, which has the capability to increase the antioxidative capacity and stress tolerance of plants to heavy metals. Plants vary considerably in their physiological response to Se. The reported research investigated the effects of Se on arsenic (As) uptake by As hyperaccumulator Pteris vittata L. and determined possible mechanisms of interaction. Pteris vittata plants were exposed hydroponically to 0, 150 or 300 microM of Na(2)HAsO(4) in the presence of 0, 5 or 10 microM of Na(2)SeO(4) for 5 or 10d. Application of 5 microM Se enhanced As concentration by P. vittata fronds by 7-45%. At 5 microM, Se acted as an antioxidant, inhibiting lipid peroxidation (reduced by 26-42% in the fronds) via increased levels of thiols and glutathione (increased by 24% in the fronds). The results suggest that Se is either an antioxidant or it activates plant protective mechanisms, thereby alleviating oxidative stress and improving arsenic uptake in P. vittata.     

Biochemistry of arsenic detoxification

All living organisms have systems for arsenic detoxification. The common themes are (a) uptake of As(V) in the form of arsenate by phosphate transporters, (b) uptake of As(III) in the form of arsenite by aquaglyceroporins, (c) reduction of As(V) to As(III) by arsenate reductases, and (d) extrusion or sequestration of As(III). While the overall schemes for arsenic resistance are similar in prokaryotes and eukaryotes, some of the specific proteins are the products of separate evolutionary pathways.     

Effects of nutrients on arsenic accumulation by arsenic hyperaccumulator Pteris vittata L.

This research investigated the effects of various nutrients on arsenic (As) removal by arsenic hyperaccumulator Pteris vittata L. in a Hoagland nutrient solution (HNS). The treatments included different concentrations of Ca and K in 20% strength of HNS, different strengths of HNS (10, 20 and 30%), different strengths of HNS (10 and 20%) with and without CaCO₃, and different concentrations of Ca, K, NO₃, NH₄, and P in 20% strength of HNS. The plants were grown in nutrient solution containing 1 mg As L^?1 for 4 weeks except the Ca/K experiment where the plants were grown in nutrient solution containing 10 or 50 mg As L^?1 for 1 week. Adding up to 4 mM Ca or 3 mM K to 20% strength HNS significantly (P < 0.05) increased plant arsenic accumulation when the solution contained 10 mg As L^?1. Plant arsenic removal was reduced with increasing Ca and K concentrations at 50 mg As L^?1. Lower strength of HNS (10%) resulted in the greatest plant arsenic removal (79%) due to lower competition of P with As for plant uptake. Addition of CaCO₃ to 20% strength of HNS significantly increased arsenic removal by P. vittata. Among the nutrients tested, NO₃ and CaCO₃ were beneficial to plant arsenic removal while NH₄, P and Cl had adverse effects. This experiment demonstrated that it is possible to optimize plant arsenic removal by adjusting nutrients in the growth medium.     

Effect of arsenic on visible symptom and arsenic concentration in hydroponic Japanese mustard spinach

Responses of Japanese mustard spinach (JM-spinach; Brassica rapa L. var. pervirdis) were investigated at elevated levels of arsenic (As). Plants were grown hydroponically in the greenhouse under 0, 6.7, 33.5 and 67 μM As (equal to 0, 0.5, 2.5 and 5 mg L^?1 As, respectively) for 14 days. Arsenic was used as sodium meta-arsenite (NaAsO₂). Toxicity symptom was solely shown as shoot growth repression at 33.5 and 67 μM As exposures. Dry weight (DW) enhanced by 19.4% in shoot and 38.9% in root in the 6.7 μM As level as compared to control but decreased by 48.1% and 72.1% DW in shoot and 24.1% and 61.1% DW in root in the 33.5 and 67 μM As levels, respectively. This result indicated that As at lower concentration might have slight stimulating effect on JM-spinach growth, but toxicity increased with increasing As. Based on the regression lines between growth and As concentration in the plant tissues, the critical toxicity level (CTL) of As in JM-spinach shoot was 7.85 μg g^?1 DW considering 10% DW reduction. The CTL for the root was almost 2110 μg As g^?1 DW, indicating that shoot of JM-spinach was more sensitive to As-toxicity than that of root. Arsenic concentrations increased in plant parts with increasing As in the medium. Arsenic concentrations were also compared in DW and fresh weight (FW) basis. The JM-spinach concentrated unaccepted level of As in shoots for human consumption in the higher As levels without showing visible toxicity symptom. In spite of decreasing iron (Fe) concentration in shoot in the highest As level, chlorophyll index did not decrease accordingly. Phosphorus (P) concentration also decreased. Phosphorus concentration decreased much more than Fe concentration. Low P might help to mobilize Fe in shoots, resulting in higher chlorophyll index at 67 μM As level. Phosphorus might compete with Fe in shoot tissues of As-stressed JM-spinach.     

Molecular mechanisms of arsenic carcinogenesis

Arsenic is a metalloid compound that is widely distributed in the environment. Human exposure of this compound has been associated with increased cancer incidence. Although the exact mechanisms remain to be investigated, numerous carcinogenic pathways have been proposed. Potential carcinogenic actions for arsenic include oxidative stress, genotoxic damage, DNA repair inhibition, epigenetic events, and activation of certain signal transduction pathways leading to abberrant gene expression. In this article, we summarize current knowledge on the molecular mechanisms of arsenic carcinogenesis with an emphasis on ROS and signal transduction pathways.     

Methanogenic inhibition by arsenic compounds

The acute acetoclastic methanogenic inhibition of several inorganic and organic arsenicals was assayed. Trivalent species, i.e., methylarsonous acid and arsenite, were highly inhibitory, with 50% inhibitory concentrations of 9.1 and 15.0 microM, respectively, whereas pentavalent species were generally nontoxic. The nitrophenylarsonate derivate, roxarsone, displayed moderate toxicity.