镉在槐叶苹叶片中的蓄积及其生态毒理学分析

以分布广泛的浮水蕨类植物--槐叶苹为研究对象,用含不同浓度Cd(2.5,5,7.5 mg/L和10 mg/L)的10% Hoagland营养液培养7d,旨在分析Cd在蕨类植物中的蓄积及其诱导产生的毒理学作用.随着培养液中Cd浓度的增加,(1) 槐叶苹叶片中Cd含量极显著上升;(2) Cd处理造成槐叶苹叶片产生明显的矿质营养失衡症状,主要表现为显著增加了对Ca和降低了对P,K和Na的吸收;(3)叶绿素含量和叶绿素荧光Fv/Fm比值都逐渐降低;(4)抗氧化防御系统活性或含量紊乱,其中超氧化物岐化酶(SOD)活性下降最突出,过氧化物酶(POD)、过氧化氢酶(CAT)、还原型谷胱甘肽(GSH)、抗坏血酸(AsA)和类胡萝卜素(Car)也都先升后降,膜脂过氧化产物MDA含量则显著增多;(5)可溶性蛋白含量一直下降;(6)透射电镜观察发现细胞超微结构损伤明显,主要为叶绿体膨胀和解体、线粒体嵴突减少和空泡化、细胞核核仁解体、核膜破裂、核质消失,并有晶体出现.结果表明槐叶苹虽然对水体Cd有一定的净化作用,但Cd浓度与毒害之间的剂量-效应关系明显;MDA含量的明显上升以及叶绿素和可溶性蛋白含量的显著下降标志着槐叶苹遭受到明显的氧化损伤;Cd破坏了槐叶苹进行正常生理活动所必需的生理和结构基础;SOD可以作为Cd诱导产生氧化压力的分子生物标志物和水体Cd污染的灵敏生态毒理学指标,Cd的半效应浓度为2.41mg/L,最大允许浓度为0.241mg/L.     

Zn诱导的菹草叶抗氧化酶活性的变化和超微结构损伤

本文以培养在不同浓度梯度Zn 溶液中的菹草为材料, 研究Zn 对植物的影响。培养第5天, 测定叶内抗氧化酶系统活性等指标的变化, 并用透射电镜观察对细胞超微结构的损伤。结果表明:低浓度(<20mg/L)在短期内(5d)未对菹草产生影响, 各生理指标呈上升趋势。当培养浓度为50mg/L 时SOD 和CAT 活性达到峰值, 而其他指标则下降:其中POD 活性和叶绿素含量高于对照, 而可溶性蛋白含量则比对照低。100mg/L 培养浓度各指标均明显降低。同时电镜观察发现过量Zn 损伤了细胞的超微结构。当培养浓度大于50mg/L 时, 叶绿体被膜断裂, 叶绿体解体。线粒体脊突膨大, 线粒体空泡化。细胞核核膜断裂, 核仁散开。这说明过量Zn 削弱了细胞抗氧化酶的活性, 同时对细胞超微结构产生致死性损伤, 从而导致细胞死亡。     

Hg2+和Cd2+胁迫对满江红生理和细胞超微结构的影响

研究了在梯度浓度Hg2+和Cd2+胁迫下,满江红(Azolla imbricata (Roxb.) Nakai)的叶绿素含量、叶绿素a/b比值、光合放氧速率、呼吸速率、抗氧化酶系(超氧化物歧化酶(SOD)、过氧化氢酶(CAT)、过氧化物酶(POD))和细胞超微结构受Hg2+和Cd2+的毒害影响.结果显示:随着胁迫程度的增大,叶绿素含量、叶绿素a/b比值、光合放氧速率明显下降,呼吸速率均在2 mg/L浓度下达到峰值,尔后下降; SOD、CAT、POD的活性均出现不同程度的应激性升高(除POD在Cd2+处理时下降),尔后下降.电镜观察发现,随着污染物浓度的增加和胁迫时间的延长,叶绿体出现膨大、破损和解体;线粒体嵴突膨胀和线粒体变形及空泡化;核染色质凝集,核仁消失,核膜破裂.实验结果表明: Hg2+和Cd2+污染不仅损害植物的生理活性,而且也破坏细胞的超微结构,最终导致植物死亡;随着Hg2+和Cd2+胁迫的增大,细胞超微结构的损伤程度和植物的生理变化是同步的;植物受毒害的程度表现出明显的剂量效应关系;在同一处理时间和浓度下,Cd2+对满江红的毒性大于Hg2+.Hg2+对满江红的致死浓度为3.5～4.0 mg/L,Cd2+为3.0～3.5 mg/L.对满江红鱼腥藻(Anabaena azollae Strasburger)细胞的超微结构变化观察表明,满江红鱼腥藻对Hg2+和Cd2+的耐受性明显高于满江红.     

Hg^2＋和Cd^2＋胁迫对满江红生理和细胞超微结构的影响

研究了在梯度浓度Hg^2 和Cd^2 胁迫下,满江红（Azolla imbricata(Roxb.)Nakai)的叶绿素含量,叶绿素a/b比值,光合放氧速率,呼吸速率,抗氧化酶系（超氧化物歧化酶（SOD）,过氧化氢酶（CAT）,过氧化物酶（POD）和细胞超微结构受He^2 和Cd^2 的毒害影响。结果显示：随着胁迫程度的增大,叶绿素含量,叶绿素a/b比值,光合放氧速率明显下降,呼吸速率均在2mg/L浓度下达到峰值,尔后下降;SOD,CAT,POD的活性均出现不同程度的应激性升高（除POD在Cd^2 处理时下降）,尔后下降,电镜观察发现,随着污染物浓度的增加和胁迫时间的延长,叶绿体出现膨大,破损和解体;线粒体嵴突膨胀和线粒体变形及空泡化;核染色质凝集,核仁消失。核膜破裂,实验结果表明：Hg^2 和Cd^2 污染不仅损害植物的生理活性,而且也破坏细胞的超微结构,最终导致植物死亡,随着Hg^2 和Cd^2 为3.0-3.5mg/L。对满江红鱼腥藻（Anabaena azollae Strasburger)细胞的超微结构变化观察表明,满江红鱼腥藻对Hg^2 和Cd^2 的耐受性明显高于满江红。     

锌胁迫下水车前叶细胞自由基过氧化损伤与超微结构变化之间关系的研究

主要研究了模拟锌污染对水车前叶细胞的自由基过氧化损伤和超微结构的变化,并对二者之间的关系作了初步探讨。随锌胁迫程度的增大,叶绿素含量、SOD（超氧化物歧化酶）活性和可溶性蛋白含量呈下降趋势;而POD（过氧化物酶）和CAT（过氧化氢酶）活性则先升后降;MDA（丙二醛）含量上升。超微结构的变化也呈现加重趋势,低浓度处理的变化为细胞核变形、叶绿体膨胀、类囊体排列紊乱;严重的超微结构的损伤是核仁散开、染色质凝集,细胞核几乎成为空核和核膜破裂,核质散出;线粒体脊突膨胀和部分溶解;叶绿体膜断裂、消失和部分类囊体溶解和散到细胞质中。实验结果表明,锌胁迫下叶细胞超微结构的变化 反映了内膜系统遭到严重伤害,这可能是自由基过氧化损伤的结果。     

锌胁迫下水车前叶细胞自由基过氧化损伤与超微结构变化之间关系的研究

主要研究了模拟锌污染对水车前叶细胞的自由基过氧化损伤和超微结构的变化,并对二者之间的关系作了初步探讨,随锌胁迫程度的增大,叶绿素含量,SOD（超氧化物歧化酶）活性和可溶性蛋白含量呈下降趋势;而POD（过氧化物酶）和CAT（过氧化氢酶）活性则先升后降;MDA（丙二醛）含量上升,超微结构的变化也呈现加重趋势,低浓度处理的变化为细胞核变形,叶绿体膨胀,类囊体排列紊乱,严重的超微结构的损伤是核仁散开,染色质凝集,细胞核几乎成为空核和核膜破裂,核质散出;线粒体脊突膨胀和部分溶解;叶绿体膜断裂,消失和部分类囊体溶解和散到细胞质中,实验结果表明,锌胁迫下叶细胞超微结构的变化反映了内膜系统遭到严重伤害,这可能是自由基过氧化损伤的结果。     

Cd2+处理对菹草叶片保护酶活性和细胞超微结构的毒害影响

以不同浓度Cd^2 处理5d的菹草为实验材料,测定了叶片SOD,POD,CAT等生理生化指标的变化,并用透射电镜观察了Cd^2 对叶细胞超微结构,尤其是对叶绿体,线粒体和细胞核的损伤情况。结果表明：SOD活性,叶绿素含量随Cd^2 处理浓度的增加而下降,而CAT和POD活性都是在1mg／L浓度下达到峰值,而后降低。SOD对Cd^2 毒害最敏感,其次为POD和CAT。电镜观察发现：随Cd^2 浓度的增加,对细胞超微结构的损伤程度也加剧。表现为叶绿体膨大,被膜断裂、消失和叶绿体解体;线粒体变形,脊突膨大和空泡化;细胞核核仁分散,核膜断裂,核空泡化。并探讨了Cd^2 对植物的毒害机制。     

镉污染对水鳖的毒害影响

研究分析了不同浓度Cd^2 对水鳖叶片叶绿素含量、SOD、CAT、POD活性以及超微结构的影响。结果表明,叶绿素含量、SOD、CAT、POD添生均随Cd^2 浓度的增加而先升后降。电镜观察发现,Cd^2 处理下,细胞核变形,核仁解体,染色质凝集;类囊体片层膨胀,叶绿体双层膜破裂,线粒体中嵴突减少或消失,线粒体空泡化。     

铜胁迫对竹叶眼子菜叶片生理指标和超微结构的影响

通过溶液培养试验,研究了不同Cu2 浓度(0、2、4、6和8 mg.L-1)胁迫对沉水植物竹叶眼子菜叶片叶绿素含量、可溶性蛋白含量、保护酶活性、活性氧产生以及细胞超微结构的影响.结果表明:随着Cu2 浓度的增加,竹叶眼子菜叶片总叶绿素、类胡萝卜素和可溶性蛋白含量逐渐下降;超氧化物歧化酶、过氧化物酶逐渐下降,而过氧化氢酶则呈先升后降趋势;超氧阴离子产生速率、过氧化氢、丙二醛和可溶性糖含量均呈上升趋势;不连续聚丙烯酰胺凝胶电泳(SDS-PAGE)显示,Cu2 处理后,引起分子量为60.9、18.8、15.7、22.3和30.0 kDa多肽的表达量减少或消失;电镜观察发现,Cu2 对叶片细胞器的超微结构特别是叶绿体、线粒体和细胞核造成严重损伤;Cu2 对竹叶眼子菜的致死浓度范围在2~4 mg.L-1.     

外源色氨酸对海水胁迫长春花幼苗根CCO活性和叶绿体超微结构的影响

以长春花[Catharanthus roseus (L.) G.Don]幼苗为材料,在温室条件下研究了不同浓度色氨酸对20%海水处理14 d后长春花幼苗生长、线粒体细胞色素c氧化酶(CCO)活性、细胞超微结构及长春碱含量的影响.结果显示:(1)与对照相比,20%海水中加入不同浓度的色氨酸,长春花幼苗生长均受到进一步显著抑制,线粒体细胞色素c氧化酶活性下降,但幼苗长春碱含量显著增加.(2) 在20%海水中增加250和500 mg/L色氨酸时,叶绿体片层松散、变稀,色氨酸浓度增大到750 mg/L时,叶绿体变形,片层扭曲、变形,叶绿体模糊、濒临解体.研究表明,在20%海水中增加500 mg/L的色氨酸时,长春花生长受到抑制较小,叶绿体超微结构受损伤程度较轻,而长春碱含量提高幅度最大,从而较有利于长春花幼苗的生长和长春碱的积累.     

Pb、Cd污染胁迫对大羽藓超微结构的影响

大羽藓在Ph、Cd溶液中培养7d后,观察其超微结构的变化发现：Pb、Cd胁迫使得细胞的超微结构遭到破坏,如叶绿体的外膜破裂,不连续,甚至完全消失;类囊体片层膨胀,或高浓度培养中叶绿体完全解体;线粒体外膜断裂或消失;细胞核被膜破坏,染色质凝聚,核质解体。仅在Cd100mg／L的培养中观察到内质网断裂呈片段状。同时在Pb的培养中发现了大量的黑色颗粒,而在Cd的培养中却未发现。     

Influence of nickel (II) and chromium (VI) on the laboratory scale rotating biological contactor

High concentration of heavy metals is toxic for most microorganisms and cause strict damage in wastewater treatment operations and often a physico-chemical pretreatment prior to biological treatment is considered necessary. However, in this study it has been shown that biological systems can adapt to Ni (II) and Cr (VI) when their concentration is below 10 and 20 mg/L, respectively. The aim of this study was to evaluate the effect of Ni (II) and Cr (VI) on the lab-scale rotating biological contactor process. It was found that, addition of Ni (II) up to 10 mg/L did not reduce the chemical oxygen demand removal efficiency and on the contrary concentrations below 10 mg/L improved the performance. The influent Ni (II) concentration of 1 mg/L was the concentration where the treatment efficiency produced a maximum COD removal of 86.5%. Moreover, Ni (II) concentration above 10 mg/L was relatively toxic to the system and produced lower treatment efficiencies than the baseline study without Ni (II). Turbidity and suspended solids removals were not stimulated to a great extent with nickel. Addition of Ni (II) did not seem to affect the pH of the system during treatment. The dissolved oxygen concentration did not drop below 4 mg/L at all concentrations of Ni (II) indicating aerobic conditions prevailed in the system. Experiments conducted with Cr (VI) revealed that addition of Cr (VI) up to 20 mg/L did not reduce the COD removal efficiency and on the contrary concentrations below 20 mg/L improved the performance. The influent Cr (VI) concentration of 1 mg/L was the concentration where the treatment efficiency produced a maximum COD removal of 88%. Turbidity and SS removals were more efficient at 5 mg/L Cr (VI) concentration, rather than 1 mg/L, which lead to the conclusion that 5 mg/L Cr (VI) concentration is the optimum concentration, in terms of COD, turbidity and SS removals. Similar with Ni (II) experiments, addition of Cr (VI) did not significantly affect the pH value of the effluent. The DO concentration remained above 5 mg/L.     

Effects of Pb<Superscript>2+</Superscript> on the active oxygen-scavenging enzyme activities and ultrastructure in <Emphasis Type="Italic">Potamogeton crispus</Emphasis> leaves

The effects of various concentrations of Pb²⁺ on the antioxidant enzyme activities and the ultrastructure in Potamogeton crispus leaves were studied. Peroxidase (POD) activity and malondialdehyde (MDA) content peaks were observed with an increase in Pb²⁺ concentration, whereas superoxide dismutase (SOD) and catalase (CAT) activities decreased firstly and then rose. Meantime, the chlorophyll content declined with increasing Pb²⁺ concentration. Simultaneously, high concentrations of Pb²⁺ aggravated ultrastructural damage to the leaf cells including swelling of chloroplasts, disruption and disappearance of chloroplast envelopes; swelling of mitochondrial cristae, deformation and vacuolation of mitochondria; condensation of chromatin, dispersion of nucleoli, and disruption of nuclear membrane. Changes in antioxidant enzyme activities and damage to fine structure are the results of lead-induced ROS accumulation. The estimated lethal concentration to P. crispus ranged from 10 to 15 mg/l lead. Published in Russian in Fiziologiya Rastenii, 2007, Vol. 54, No. 3, pp. 469–474. The text was submitted by the authors in English.     

Simultaneous Cr(VI) reduction and phenol degradation in pure cultures of Pseudomonas aeruginosa CCTCC AB91095

Simultaneous Cr(VI) reduction and phenol degradation were investigated in a reactor containing Pseudomonas aeruginosa CCTCC AB91095. Phenol was used as carbon source. P.aeruginosa utilized metabolites formed during phenol degradation as energy source for Cr(VI) reduction. Cr(VI) inhibited both Cr(VI) reduction and phenol degradation when Cr(VI) concentration exceeded the optimum value (20 mg/L), whereas phenol enhanced both Cr(VI) reduction and phenol degradation below the optimum initial concentration of 100 mg/L. Cr(III) was the predominant product of Cr(VI) reduction in cultures after incubation for 24 h. Both Cr(VI) reduction and phenol degradation were influenced by the amount of inocula. The concentration of Cr(VI) and phenol declined quickly from 20, 100 to 3.36, 29.51 mg/L in cultures containing of 5% (v/v) inoculum after incubation for 12 h, respectively. The whole study showed that P. aeruginosa is promising for the reduction of toxic Cr(VI) and degradation of organic pollutants simultaneously in the mineral liquid medium.     

异化铁还原细菌LQ25还原重金属Cr (VI)的特性研究

[背景] 异化铁还原细菌能够在还原Fe （III）的同时将毒性较大的Cr （VI）还原成毒性较小的Cr （III）,解决铬污染的问题。[目的] 基于丁酸梭菌（Clostridium butyricum） LQ25异化铁还原过程制备生物磁铁矿,开展异化铁还原细菌还原Cr （VI）的特性研究。[方法] 构建以氢氧化铁为电子受体和葡萄糖为电子供体的异化铁培养体系。菌株LQ25培养结束时制备生物磁铁矿。设置不同初始Cr （VI）浓度（5、10、15、25和30 mg/L）,分别测定菌株LQ25对Cr （VI）还原效率以及生物磁铁矿对Cr （VI）的还原效率。[结果] 菌株LQ25在设置的Cr （VI）浓度范围内都能良好生长。当Cr （VI）浓度为15 mg/L时,在异化铁培养条件下,菌株LQ25对Cr （VI）的还原率为63.45%±5.13%,生物磁铁矿对Cr （VI）的还原率为87.73%±9.12%,相比菌株还原Cr （VI）的效率提高38%。pH变化能影响生物磁铁矿对Cr （VI）的还原率,当pH 2.0时,生物磁铁矿对Cr （VI）的还原率最高,几乎达到100%。电子显微镜观察发现生物磁铁矿表面有许多孔隙,X-射线衍射图谱显示生物磁铁矿中Fe （II）的存在形式是Fe （OH）₂。[结论] 基于异化铁还原细菌制备生物磁铁矿可用于还原Cr （VI）,这是一种有效去除Cr （VI）的途径。     

Use of synchrotron- and plasma-based spectroscopic techniques to determine the uptake and biotransformation of chromium(III) and chromium(VI) by Parkinsonia aculeata

In this study, a combination of inductively coupled plasma optical emission spectroscopy and X-ray absorption spectroscopy (XAS) was used to study the uptake and speciation of chromium in Parkinsonia aculeata, commonly known as Mexican Palo Verde. Plants were treated for 14 days in a modified Hoagland solution containing chromium(III) or chromium(VI) at several concentrations. The results showed that plants treated with 70 mg Cr(III) L(-1) and 30 mg Cr(VI) L(-1) had similar Cr concentrations in leaves (～200 mg kg(-1) dry weight, DW). The results also showed that neither Cr(III) nor Cr(VI) affected the uptake of phosphorus and sulfur. However, the concentration of calcium in the stems of plants treated with Cr(VI) at 40 mg L(-1) (about 6000 mg Ca kg(-1) DW) was significantly higher compared to the Ca concentration (about 3000 mg kg(-1) DW) found in the stems of plants treated with 150 mg Cr(III) L(-1). However, no differences were observed in potassium and magnesium concentrations. The iron concentration (about 1000 mg kg(-1) DW) in roots treated with 40 mg Cr(VI) L(-1) was similar to the iron concentration found in the roots of plants treated with 110 mg Cr(III) L(-1). The XAS data showed that Cr(VI) was reduced to Cr(III) in/on the plant roots and transported as Cr(III) to the stems and leaves. The XAS studies also showed that Cr(III) within plants was present as an octahedral complex.