丛枝菌根真菌修复农药污染土壤的潜力分析

<正>我国每年施用80-100多万吨化学农药(周春梅2001),主要是有机氯、有机磷、氨基甲酸酯类。例如,有机磷农药年用量约20万吨,其中剧毒     

真菌吸附铅锌的研究

正随着采矿业的迅速发展,越来越多的重金属通过多种途径进入土壤环境中,对生态环境造成了不可估量的破坏并严重威胁人类健康。铅锌在工业上具有非常重要的作用且其应用极为广泛,而他们具有的难去除、难迁移和生物累积等特性使得铅锌在环境中的污染尤为突出。通过微生物的生长代谢,有效降低土壤重金属毒性,是促进植物生长的重要步骤之一。同时也要求微生物自身具有抵抗重金属的功能,根际微生     

土壤中镉对丛枝菌根真菌Glomus mosseae生长的效应

采用分室培养法,在同一宿主植物生长的土壤中设含有0、5、25、50mg/kg4个不同浓度重金属镉的菌丝生长室(用30μm尼龙网与根系隔开)以期建立在宿主植物生长状况完全相同的条件下研究环境因素对AM真菌直接影响的新方法,并在此基础上探讨不同浓度的重金属镉对丛枝菌根真菌Glomus mosseae(BEG167)生长的直接影响。结果表明,与不施加镉的处理相比,土壤中施加低浓度镉(5mg/kg)刺激了G.mosseae的生长,其菌丝总长度最大;高浓度镉(大于25mg/kg)抑制了G.mosseae的生长,其菌丝总长度较小。AM真菌的代谢活性与土壤镉浓度的关系也表现出与菌丝生物量相同的规律。以上结果表明:G.mosseae在镉污染环境中有应激反应的特征,即:当G.mosseae受到轻微毒害时,为了适应其生存条件的改变而不断增加其代谢活性和生长量来降低镉的毒害。此外,本方法用于研究宿主植物生长状况相同的条件下,重金属毒害或其他环境因素对AM真菌生长代谢的直接影响是可行的。     

西藏高原草地生态系统丛枝菌根真菌的地理分布

西藏高原是地球上极具特色的地理单元,对生物物种的形成与演化具有重要影响。基于孢子形态学鉴定,对从藏东南到藏西北(海拔高差3500 m,年均温、年均降水量差异分别20℃、800 mm)高原热带、亚热带、温带、亚寒带和寒带环境下发育而成的热性草丛、暖性草丛、温性草原、温性荒漠、高寒草甸草原、高寒草原、高寒荒漠和高寒荒漠草原中的AM真菌群落进行研究,结果表明,不同类型草地间AM真菌的群落相似度普遍较低,环境对AM真菌群落具有重要影响。从藏东南到藏西北,不同类型草地间AM真菌的群落相似度呈下降趋势(Jaccard相似性系数从0.52降至0.20),AM真菌群落组成及结构变化渐趋加大,不同草地中的同种植物(包括广谱种、青藏高原特有种)AM真菌群落相似度亦不同。沿藏东南到藏西北环境梯度,随草地寒旱程度的逐步加剧,AM真菌种的丰度,特别是种数、Shannon-Weiner指数在总体上趋于显著(P0.05)下降,孢子密度则在总体上趋于显著提高,优势种比例、Shannon-Weiner指数亦表现出增加的趋势,表明AM真菌物种多样性虽趋于下降,但生存及对环境的适应能力趋于提高。海拔、土壤p H、有效磷和有机碳含量对AM真菌群落组成均具显著影响,但海拔对水热环境的影响决定着土壤环境的变化。因此,海拔和寒旱程度不断上升所导致的p H显著提高、土壤有机碳和有效磷含量显著下降的综合作用影响并决定着AM真菌的群落组成。研究结果对进一步理解西藏高原生物多样性的产生和维持机制等具有重要的参考价值。     

泰山丛枝菌根真菌群落结构特征

2007年对泰山植被根围内丛枝菌根(arbuscular mycorrhiza,AM)真菌群落组成、数量、分布及其与植物多样性的关系进行了研究。从泰山傲徕峰、黑龙潭库区等样地共分离出4属16种AM真菌:球囊霉属Glomus 9种、无梗囊霉属Acaulospora 4种、巨孢囊霉属Gigaspora 2种和盾巨孢囊霉属Scutellospora1种。其中,球囊霉属Glomus及聚球囊霉Glomus fasciculatum的孢子密度、相对多度、分布频度和重要值均最高,分别为泰山植被区根围内AM真菌优势属和优势种。各样地之间Sorenson相似系数在0.60和0.85之间。植被数量与孢子密度(r=0.80,p0.01)、植物种的丰富度与AM真菌种的丰富度(r=0.77,p0.01)以及与孢子密度(r=0.59,p0.01)均呈极显著正相关关系。研究结果表明植物多样性对于提高AM真菌多样性发挥极为重要的作用。     

土壤中镉对丛枝菌根真菌Glomus mosseae生长的效应

采用分室培养法,在同一宿主植物生长的土壤中设含有0、5、25、50mg/kg4个不同浓度重金属镉的菌丝生长室(用30μm尼龙网与根系隔开)以期建立在宿主植物生长状况完全相同的条件下研究环境因素对AM真菌直接影响的新方法,并在此基础上探讨不同浓度的重金属镉对丛枝菌根真菌Glomus mosseae(BEG167)生长的直接影响。结果表明,与不施加镉的处理相比,土壤中施加低浓度镉(5mg/kg)刺激了G.mosseae的生长,其菌丝总长度最大;高浓度镉(大于25mg/kg)抑制了G.mosseae的生长,其菌丝总长度较小。AM真菌的代谢活性与土壤镉浓度的关系也表现出与菌丝生物量相同的规律。以上结果表明:G.mosseae在镉污染环境中有应激反应的特征,即:当G.mosseae受到轻微毒害时,为了适应其生存条件的改变而不断增加其代谢活性和生长量来降低镉的毒害。此外,本方法用于研究宿主植物生长状况相同的条件下,重金属毒害或其他环境因素对AM真菌生长代谢的直接影响是可行的。     

五种丛枝菌根真菌对枳实生苗耐锌污染的影响

通过盆栽实验研究丛枝菌根(AM)真菌Glomus versiforme(G.v)、G.mosseae(G.m)、G.intraradices(G.i)、G.aggregatum(G.a)和G.etunicatum(G.e)在锌污染条件下枳实生苗的菌根侵染、生长、叶片和根系锌、磷含量及部分生理指标的影响.结果表明:锌污染...     

丛枝菌根真菌的生态分布及其影响因子研究进展

丛枝菌根(arbuscular mycorrhiza,AM)共生体系对于植物适应各种逆境胁迫具有重要积极作用。AM真菌还能够通过根外菌丝网络调节植物群落结构和演替,深刻影响生态系统结构和功能的稳定性。AM真菌生态生理功能的发挥主要取决于其生态适应性,明确AM真菌在不同环境中的多样性、生态适应性以及对各种生态因子的响应机制,是AM真菌资源管理、功能发掘与利用的前提。迄今为止,有关各种生态因子对AM真菌多样性的影响已有不少研究,但是AM真菌生态分布及其形成机制仍缺乏系统的研究和理论分析。综述了生物因子和非生物因子对AM真菌生态分布的影响,结合大型生物空间分布理论探讨了AM真菌生态分布规律和建成机制,分析了当前本研究领域所存在的问题和动向,以期推动相关研究进展。     

黄檗丛枝菌根真菌鉴定

目的：利用形态学特征与Nested-PCR技术鉴定黄檗丛枝菌根真菌。方法：采用酸性品红染色法挑选黄檗丛枝菌根。同时,利用湿筛法获得AM真菌孢子,进行形态学鉴定。运用Nested-PCR技术,对黄檗粗提DNA进行特异性扩增,采用blastn进行序列相似性比较。并构建系统进化树,确定侵染黄檗根系的AM真菌。结果：编号为HDAM-1的AM真菌孢子,形态特征与G．intraradices的特征描述一致。Nested-PCR检测到约455bp的目的片段,其序列与G．intraradices（DQ469118）相似性最高,达97．8％,有11个碱基的差异。系统进化树显示该序列在基于25S rDNA的进化树中与G．intraradices（DQ469118．1）处于同一分支,确定G．intraradices侵染黄檗根系。结论：将形态学特征与Nested-PCR技术相结合鉴定AM真菌,不仅简易、经济,而且能够提高研究结果的可靠性。     

Biosorption of cadmium and chromium in duckweed Wolffia globosa

The biosorption of cadmium (Cd) and chromium (Cr) by using dried Wolffia globosa biomass were investigated using batch technique. The effects of concentration and pH solution on the adsorption isotherm were measured by determining the adsorption isotherm at initial metal concentrations from 10 to 400 mg/L and pH 4 to 7 for Cd, and pH 1.5 to 6 for Cr. The adsorption equilibria were found to follow Langmuir models. The maximum adsorption capacity (Xm) at pH 7 in W. globosa-Cd system was estimated to be 80.7 mg/g, while the maximum removal achieved at pH 4, pH 5, and pH 6 were 35.1, 48.8, and 65.4 mg/g, respectively. The Xm at pH 1.5 in W. globosa--Cr system was estimated to be 73.5 mg/g, while the maximum removal achieved at pH 3, pH 5, and pH 6 were 47.4, 33.1, and 12.9 mg/g, respectively. The effects of contact times on Cd and Cr sorption indicated that they were absorbed rapidly and more efficiently at lower concentrations.     

Cadmium uptake by Spirulina maxima: toxicity and mechanism

Cadmium uptake by Spirulina maxima cells was more pronounced in living than in dead cells, with a maximum recovery of 47.63mg Cd/g cells for living cells and 37.00mg Cd/g cells for inactivated cells. When in the medium at 1.2mg/l, cadmium affected cell growth and diminished cell productivity. Cadmium was detected in the outer and inner faces of the external membrane, essentially in the lipid layer.     

The effects of cadmium and the cadmium-zinc interaction on the axenic growth of ectomycorrhizal fungi

Eleven strains of ectomycorrhizal fungi belonging to seven species have been cultured on a cadmium-contaminated growth medium in order to determine their in vitro cadmium tolerance. Four strains were collected from a zinc and cadmium-polluted soil. Radial growth rate was a sensitive parameter to detect Cd toxicity. A wide differential response to Cd was obtained between the individual species. A clear relation between Cd tolerance and site origin of the isolates did not exist, although such a relationship was found when strains are compared within one species. Cd-sensitive and Cd-tolerant strains of Suillus bovinus were studied in more detail. Two isolates were grown on media with combinations of two non-toxic zinc concentrations and three cadmium levels. Adding a higher Zn concentration to the medium resulted in a reduction of the toxic effect of Cd. This antagonistic effect also resulted in a lowered Cd concentration in the mycelium.     

Effect of zinc on cadmium influx and toxicity in cultured CHO cells

Addition of zinc lowers the toxicity level of cadmium in cultured CHO cells. Cell survival and protein synthesis were used to measure the cellular toxicity of cadmium.¹⁰⁹Cd was used to measure cadmium uptake by the cells. The results suggest that these class IIB transition metals, zinc and cadmium, share a common transport mechanism. Thus, the antagonism appears to involve a reduction in the influx of cadmium due to the presence of zinc.     

Biological function of metallothionein. VI. Metabolic interaction of cadmium and zinc in rats

The accumulation and depletion of cadmium in liver and kidney metallothionein (MT) and the effects of dietary zinc deficiency on cadmium metabolism were studied in rats. The accumulation of cadmium in liver MT started to plateau after 80 days, but there was a linear accumulation of this element in kidney MT over the entire 300-day experiment. Cadmium in MT fractions was depleted very slowly when rats were changed to a diet without cadmium. The accumulation of cadmium in MT also caused zinc to accumulate in this protein, even in rats fed zinc-deficient diets. However, the reverse situation was found not to be true; zinc did not cause cadmium to accumulate in MT. Dietary zinc deficiency limited the binding of injected¹⁰⁹Cd to MT of liver, but not of kidneys or testes. However, zinc-deficient rats fed cadmium in their diets metabolized cadmium similarly to zinc-supplemented rats, suggesting that zinc deficiency does not limit the ability of cadmium to stimulate MT synthesis.     

Response of Thlaspi caerulescens to nitrogen, phosphorus and sulfur fertilisation

The main limiting factor for cleaning-up contaminated soils with hyperaccumulator plants is the low production of aerial biomass and the number of successive crops needed to reach the objective of remediation. The aim of this study was to contribute to the determination of a fertilisation strategy to optimise soil metal phytoextraction by Thlaspi caerulescens. A pot experiment was conducted on an agricultural soil and on a contaminated soil from the vicinity of a former Pb/Zn smelter. The nitrogen (N) treatment consisted of 4 levels (0, 11, 21.5 and 31 mg N kg(-1) dry soil (DS)) added as NH4NO3. The highest N treatment was combined with 4 levels of phosphorus (P) (0, 20, 40 and 80 mg P kg(-1) DS as KH2PO4) and sulfur (S) additions (0, 10, 20 and 30 mg S kg(-1) DS as MgSO4). The highest N fertilisation contributed significantly to enhance biomass production of T. caerulescens and to decrease the concentration of Cd and Zn in the biomass. At constant N addition, P supply did not affect metal extraction by T. caerulescens but negatively affected plant health. Sulfur supply slightly increased phytoextraction of Cd. Our results show that N and S fertilisation might interact but further investigations on the effect of such interaction on Cd extraction efficiency are needed.     

The potential of Thlaspi caerulescens for phytoremediation of contaminated soils

Uptake of Cd, Zn, Pb and Mn by the hyperaccumulator Thlaspi caerulescens was studied by pot trials in plant growth units and in populations of wild plants growing over Pb/Zn base-metal mine wastes at Les Malines in the south of France. The pot trials utilised metal-contaminated soils from Auby in the Lille area. Zinc and Cd concentrations in wild plants averaged 1.16% and 0.16% (dry weight) respectively. The unfertilised biomass of the plants was 2.6 t/ha. A single fertilised crop with the above metal content could remove 60 kg of Zn and 8.4 kg Cd per hectare. Experiments with pot-grown and wild plants showed that metal concentrations (dry weight basis) were up to 1% Zn (4% Zn in the soil) and just over 0.1% Cd (0.02% Cd in the soil). The metal content of the plants was correlated strongly with the plant-available fraction in the soils as measured by extraction with ammonium acetate and was inversely correlated with pH. Bioaccumulation coefficients (plant/soil metal concentration quotients) were in general higher for Cd than for Zn except at low metal concentrations in the soil. There was a tendency for these coefficients to increase with decreasing metal concentrations in the soil. It is proposed that phytoremediation using Thlaspi caerulescens would be entirely feasible for low levels of Cd where only a single crop would be needed to halve a Cd content of 10 g/g in the soil. It will never be possible to remediate elevated Zn concentrations within an economic time frame (<10 yr) because of the lower bioaccumulation coefficient for this element coupled with the much higher Zn content of the soils.     

Competitive biosorption of Acid Blue 25 and Acid Red 337 onto unmodified and CDAB-modified biomass of Aspergillus oryzae

The performance of unmodified and cetyldimethylethyl ammonium bromide (CDAB) modified nonviable Aspergillus oryzae for removal of Acid Blue 25 (AB 25) and Acid Red 337 (AR 337) was investigated in single and binary systems. In single system, the biosorption capacities of CDAB-modified biosorbent reached 160.36 and 280.39 mg g⁻¹ for AB 25 and AR 337, respectively, which were 1.52 and 1.66 times higher than that of unmodified biosorbent. In binary system, the biosorption capacities of unmodified and CDAB-modified biosorbents for both dyes decreased significantly compared to that in single system. Relative competitiveness analysis demonstrated that there existed critical initial concentration ratio which determined the predominance of dyes during biosorption process. The biosorption of AB 25 was found to be in dominant position at initial concentration ratio of [AB 25]/[AR 337] above 0.63. Kinetic analysis indicated that intraparticle diffusion was the limiting step for biosorption of two dyes onto biosorbents.