多氯联苯污染土壤菌根真菌-紫花苜蓿-根瘤菌联合修复效应

选用紫花苜蓿（Medicago sativa L.）作为宿主植物,盆栽试验研究了丛枝菌根真菌（Glomus caledonium）和苜蓿根瘤菌(Rhizobium meliloti)单接种及双接种对PCBs复合污染土壤的联合修复效应.结果表明,在紫花苜蓿-菌根真菌-根瘤菌共生体系中,紫花苜蓿对土壤中PCBs的降低起到明显作用,使轻度污染和重度污染土壤中PCBs浓度分别下降了15.8%、 23.5%,紫花苜蓿单接种菌根真菌和苜蓿根瘤菌后轻度污染和重度污染土壤中PCBs浓度分别下降了14.8％、 24.1%和20.6%、 25.5%,双接种后土壤PCBs分别降低了23.2％、26.9%,而且也改变了紫花苜蓿根际土壤微生物群落的碳源利用程度,改善了微生物群落功能多样性.可见,紫花苜蓿豆科植物-菌根真菌-根瘤菌特殊共生体对PCBs污染土壤显示了较好的修复潜力.     

红绒盖牛肝菌菌丝对Cu(Ⅱ)和Cd(Ⅱ)生物吸附的影响因子

在离体条件下,研究了外生菌根真菌红绒盖牛肝菌(Xerocomus chrysenteron)菌丝对 Cu(Ⅱ)和 Cd(Ⅱ)生物吸附的影响因子,考察了X. chrysenteron菌丝对 Cu(Ⅱ)和 Cd(Ⅱ)的吸附能力、去除率和平衡吸附量在不同初始质量浓度和不同温度下所受影响,并采用Freundlich和Langmuir线性化吸附等温线模型拟合X. chrysenteron菌丝的生物吸附热力学特性. 结果表明:当菌丝的质量浓度为10g/L, 30 ℃时,X. chrysenteron非活性菌丝对 Cu(Ⅱ)和 Cd(Ⅱ)的最佳吸附量分别为47.11和11.72mg/g(以菌丝干质量计);X. chrysenteron非活性菌丝对 Cu(Ⅱ)和 Cd(Ⅱ)的吸附能力、去除率、平衡吸附量均优于活性菌丝;X. chrysenteron菌丝对 Cu(Ⅱ)和 Cd(Ⅱ)的吸附能力随其初始质量浓度的增加而增大,去除率随其初始质量浓度的增大而分别呈指数下降和线性下降;30 ℃时X. chrysenteron菌丝对 Cu(Ⅱ)和 Cd(Ⅱ)的吸附能力、去除率、平衡吸附量均比 25 ℃时大.     

Using the nematode Caenorhabditis elegans as a model animal for assessing the toxicity induced by microcystin-LR

Among more than 75 variants of microcystin(MC),microcystin-LR(MC-LR) is one of the most common toxins.In this study,the feasibility of using Caenorhabditis elegans to evaluate MC-LR toxicity was studied.C.elegans was treated with MC-LR at different concentrations ranging from 0.1 to 80 μg/L.The results showed that MC-LR could reduce lifespan,delay development,lengthen generation time,decrease brood size,suppress locomotion behavior,and decreases hsp-16-2-gfp expression.The endpoints of generation time,brood...     

Induction of chemotaxis to sodium chloride and diacetyl and thermotaxis defects by microcystin-LR exposure in nematode Caenorhabditis elegans

Apart from the liver disruption, embryotoxicity and genotoxicity, microcystin (MC)-LR also could cause neurotoxicity. Nematode Caenorhabditis elegans was explored as a model to study the neurotoxicity. In the present study, we provided evidence to indicate the neurotoxicity on chemotaxis to NaCl and diacetyl, and thermotaxis from MC-LR exposure to C. elegans. As a result, higher concentrations of MC-LR caused significantly severe defects of chemotaxis to NaC1 and diacetyl, and thermotaxis. The neurotoxicity on chemotaxis to NaCl and diacetyl, and thennotaxis from MC-LR exposure might be largely mediated by the damage on the corresponding sensory neurons (ASE, AWA, and AFD) and interneuron AIY. The expression levels of che-1 and odr-7 were significantly decreased (P<0.01) in animals exposed to MC-LR at concentrations lower than 10 μg/L, whereas the expression levels of ttx-1 and ttx-3 could be significantly (P<0.01) lowered in animals even exposed to 1 μg/L of MC-LR. Moreover, both the chemotaxis to NaCl and diacetyl and the thermotaxis were more significantly reduced m MC-LR exposed mutants of che-1(p674), odr-7(ky4), ttx-1(p767), and ttx-3(ks5) than those in exposed wild-type N2 animals at the same concentrations.     

Adverse effects of metal exposure on chemotaxis towards water-soluble attractants regulated mainly by ASE sensory neuron in nematode Caenorhabditis elegans

Chemotaxis to water-soluble attractants is mainly controlled by ASE sensory neuron whose specification is regulated by che-1 in Caenorhabditis elegans. Our data suggested that exposure to high concentrations of metals, such as Pb, Cu, Ag, and Cr, would result in severe defects of chemotaxis to water-soluble attractants of NaCl, cAMP, and biotin. Moreover, the morphology of ASE neuron structures as observed by relative fluorescent intensities and relative size of fluorescent puncta of cell bodies, relative lengths of sensory endings in ASE neurons, and the expression patterns of che-1 were obviously altered in metal exposed animals when they meanwhile exhibited obvious chemotaxis defects to water-soluble attractants. In addition, the dendrite morphology could be noticeably changed in animals exposed to 150 mol/L of Pb, Cu, and Ag. Furthermore, we observed significant decreases of chemotaxis to water-soluble attractants in Pb exposed che-1 mutant at concentrations more than 2.5 mol/L, and in Cu, Ag, and Cr exposed che-1 mutant at concentrations more than 50 mol/L. Therefore, impairment of the ASE neuron structures and functions may largely contribute to the appearance of chemotaxis defects to water-soluble attractants in metal exposed nematodes.     

铆钉菇(Gomphidius viscidus)菌丝对Cu(Ⅱ)的生物吸附特性

在离体条件下研究了外生菌根真菌铆钉菇(Gomphidius viscidus)菌丝对Cu(Ⅱ)的吸附动力学和热力学特性,并采用二级动力学方程Freundlich和Langmuir吸附等温线模型拟合G.viscidus菌丝的生物吸附特性.同时,考察了G.viscidus菌丝在不同温度和Cu(Ⅱ)起始浓度下,各自对Cu(Ⅱ)吸附能力和吸附率所造成的影响.结果表明:G.viscidus活性菌丝在2h时达到最大吸附速率,16h时达到最大平衡吸附量,其主动吸附使得对Cu(Ⅱ)具有很高的平衡吸附比例;G.viscidus活性菌丝和非活性菌丝均对Cu(Ⅱ)具有很大的吸附量,分别为25℃时的15.12与36.13mg·g-1(以干重计)和30℃时的16.23与10.42mg·g-1(以干重计);G.viscidus非活性菌丝对Cu(Ⅱ)的吸附能力随温度升高而降低,G.viscidus活性菌丝则无显著变化;G.viscidus菌丝对Cu(Ⅱ)的吸附能力随Cu(Ⅱ)初始浓度增加而增大,吸附率随初始浓度增加而减小.     

两株耐铅镉真菌对土壤中铅镉赋存形态及小白菜吸收积累的影响

通过土培试验,研究接种耐铅镉真菌(产黄头孢霉Cephalosporium chrysogenum和头孢霉Cephalosporium SP.)对灭菌和未灭菌铅镉污染土壤上小白菜生长及铅镉赋存形态的影响.试验结果表明:接种两种耐重金属真菌可以降低或显著降低土壤中交换态铅镉、碳酸盐结合态铅镉和铁锰结合态铅镉,且显著增加土壤中有机结合态铅镉,因此降低了土壤中铅镉的活性;在灭菌和未灭菌铅镉污染土壤上接种两种真菌均能增加或显著增加小白菜的株高和鲜重,其中在未灭土壤中接种产黄头孢霉20 mL小白菜鲜重和株高最大,分别达到6.00 cm和3.22 g·株~(-1),在灭菌土壤上接种产黄头胞霉10 m L小白菜株高和鲜重最大,分别为10.66 cm和11.07 g·株~(-1);接种两种真菌可以显著降低未灭菌土壤上小白菜体内铅镉含量和累积量,在灭菌土壤上接种10 mL产黄头孢霉可以显著降低小白菜铅含量和累积量.     

施用沼渣和接种丛枝菌根真菌对甘草生长及矿质营养的影响

沼渣是厌氧发酵的残余物,可作为肥料施用,但因其含有一定量的重金属等有害物质可能导致环境污染风险.丛枝菌根(Arbuscular mycorrhiza,AM)真菌作为植物共生真菌,可以促进植物对矿质养分的吸收,同时能够通过不同途径减轻重金属对植物的毒害.本文采用甘草(Glycyrrhiza uralensis Fisch.)为供试植物开展盆栽试验,考察施用沼渣结合接种AM真菌对甘草生长和矿质营养的影响.试验结果表明,施用沼渣显著促进了植物生长,提高了植物生物量、磷含量和叶片叶绿素含量,与此同时提高了土壤有机质和磷、铬、铜、铅含量,并导致植物重金属含量显著升高.另一方面,AM真菌能够和甘草根系形成良好共生关系,但施用沼渣对菌根侵染表现出显著抑制作用.接种AM真菌促进了甘草生长、提高了根系磷含量及叶片叶绿素含量,同时显著降低了植株重金属含量至安全阈值以内.本试验表明,施用沼渣同时接种AM真菌可在促进甘草生长的同时阻控重金属污染风险,因而可作为沼渣安全利用的一种可行技术途径.     

重金属对秀丽隐杆线虫繁殖的影响

为了探究重金属单独及联合暴露对秀丽隐杆线虫(Caenorhabditis elegans)繁殖的影响及其作用机制,采用96孔板液相暴露试验,以环境相关浓度(0.1~50.0 μg/L)的Cd、Hg、Pb暴露同步化处理秀丽隐杆线虫,24 h后统计其怀卵数及阴门畸形率,以及连续记录72 h内子一代秀丽隐杆线虫的个体数,最后利用2×2析因设计方差分析阐明重金属的两两联合作用模式. 结果表明:与对照组相比,Cd、Hg、Pb单独及联合暴露对秀丽隐杆线虫的繁殖具有显著抑制作用,ρ(Cd)为50.0 μg/L、ρ(Hg)为10.0 μg/L、ρ(Pb)为50.0 μg/L暴露组秀丽隐杆线虫子一代数量分别降低了43.5%、33.8%、51.0%;Cd-Hg暴露组〔当ρ(Cd)、ρ(Hg)分别为50.0、10.0 μg/L时〕、Hg-Pb暴露组〔当ρ(Hg)、ρ(Pb)分别为10.0、50.0 μg/L时〕、Cd-Pb暴露组〔当ρ(Cd)、ρ(Pb)分别为50.0、50.0 μg/L时〕秀丽隐杆线虫子一代个体数分别降低了44.7%、61.0%、53.3%. 进一步研究发现,Cd、Hg、Pb单独及联合暴露会引起秀丽隐杆线虫子宫内受精卵数量降低以及产卵器阴门结构畸形率升高. 2×2析因设计方差分析结果发现,Cd、Hg、Pb两两联合暴露对秀丽隐杆线虫的繁殖表现为没有交互作用或者交互方式为拮抗. 研究显示,秀丽隐杆线虫子宫内怀卵数的降低是其子一代数量显著减少的主要原因,而阴门结构的损伤可能使产卵行为受损,从而进一步加剧重金属对秀丽隐杆线虫繁殖的抑制作用.      

降解褐煤菌种选育及降解产物研究

通过对分离自洗煤厂的一株青霉菌进行人工诱变,选育出一株具有较强降解褐煤能力的突变株．将褐煤加到平板培养的该菌株上,经过３６ ｈ 开始被降解．将该菌株用摇瓶培养３ ｄ ,其培养液也能降解褐煤．元素分析结果表明,降解物中 Ｈ、 Ｏ、 Ｎ 的元素质量分数（ ｗ／ ％ ） 比原煤均有所升高,而ｗ（ Ｃ）／ ％ 明显下降．降解产物的经验分子式可写为 Ｃ１００ Ｈ１４４ Ｏ５８ ．２ Ｎ１０ ．０ Ｓ１ ．１８ ,经凝胶过滤法测,定其 Ｍｒ 分布在（２ ～８） ×１０４ 之间; 其红外吸收光谱与原煤相比也有一定的变化． 这些结果说明生物降解过程中褐煤的组成和结构发生了一定的变化