Inhibition of Na+/K(+)-ATPase and Mg(2+)-ATPase by metal ions and prevention and recovery of inhibited activities by chelators

Kinetics and inhibition of Na(+)/K(+)-ATPase and Mg(2+)-ATPase activity from rat synaptic plasma membrane (SPM), by separate and simultaneous exposure to transition (Cu(2+), Zn(2+), Fe(2+) and Co(2+)) and heavy metals (Hg(2+) and Pb(2+)) ions were studied. All investigated metals produced a larger maximum inhibition of Na(+)/K(+)-ATPase than Mg(2+)-ATPase activity. The free concentrations of the key species (inhibitor, MgATP(2-), MeATP(2-)) in the medium assay were calculated and discussed. Simultaneous exposure to the combinations Cu(2+)/Fe(2+) or Hg(2+)/Pb(2+) caused additive inhibition, while Cu(2+)/Zn(2+) or Fe(2+)/Zn(2+) inhibited Na(+)/K(+)-ATPase activity synergistically (i.e., greater than the sum metal-induced inhibition assayed separately). Simultaneous exposure to Cu(2+)/Fe(2+) or Cu(2+)/Zn(2+) inhibited Mg(2+)-ATPase activity synergistically, while Hg(2+)/Pb(2+) or Fe(2+)/Zn(2+) induced antagonistic inhibition of this enzyme. Kinetic analysis showed that all investigated metals inhibited Na(+)/K(+)-ATPase activity by reducing the maximum velocities (V(max)) rather than the apparent affinity (Km) for substrate MgATP(2-), implying the noncompetitive nature of the inhibition. The incomplete inhibition of Mg(2+)-ATPase activity by Zn(2+), Fe(2+) and Co(2+) as well as kinetic analysis indicated two distinct Mg(2+)-ATPase subtypes activated in the presence of low and high MgATP(2-) concentration. EDTA, L-cysteine and gluthathione (GSH) prevented metal ion-induced inhibition of Na(+)/K(+)-ATPase with various potencies. Furthermore, these ligands also reversed Na(+)/K(+)-ATPase activity inhibited by transition metals in a concentration-dependent manner, but a recovery effect by any ligand on Hg(2+)-induced inhibition was not obtained.     

Co2+, Cu2+, and Zn2+ accumulation by cyanobacterium Spirulina platensis

The Spirulina platensis biomass was characterized for its metal accumulation as a function of pH, external metal concentration, equilibrium isotherms, kinetics, effect of co-ions under free (living cells, lyophilized, and oven-dried) and immobilized (Ca-alginate and polyacrylamide gel) conditions. The maximum metal biosorption by S. platensis biomass was observed at pH 6.0 with free and immobilized biomass. The studies on equilibrium isotherm experiments showed highest maximum metal loading by living cells (181.0 +/- 13.1 mg Co(2+)/g, 272.1 +/- 29.4 mg Cu(2+)/g and 250.3 +/- 26.4 mg Zn(2+)/g) followed by lyophilized (79.7 +/- 9.6 mg Co(2+)/g, 250.0 +/- 22.4 mg Cu(2+)/g and 111.2 +/- 9.8 mg Zn(2+)/g) and oven-dried (25.9 +/- 1.9 mg Co(2+)/g, 160.0 +/- 14.2 mg Cu(2+)/g and 35.1 +/- 2.7 mg Zn(2+)/g) biomass of S. platensis on a dry weight basis. The polyacrylamide gel (PAG) immobilization of lyophilized biomass found to be superior over Ca-alginate (Ca-Alg) and did not interfere with the S. platensis biomass biosorption capacity, yielding 25% of metal loading after PAG entrapment. The time-dependent metal biosorption in both the free and immobilized form revealed existence of two phases involving an initial rapid phase (which lasted for 1-2 min) contributing 63-77% of total biosorption, followed by a slower phase that continued for 2 h. The metal elution studies conducted using various reagents showed more than 90% elution with mineral acids, calcium salts, and Na(2)EDTA with free (lyophilized or oven-dried) as well as immobilized biomass. The experiments conducted to examine the suitability of PAG-immobilized S. platensis biomass over multiple cycles of Co(2+), Cu(2+), and Zn(2+) sorption and elution showed that the same PAG cubes can be reused for at least seven cycles with high efficiency.     

Antioxidant defenses and biochemical changes in pacu (Piaractus mesopotamicus) in response to single and combined copper and hypoxia exposure

The effect of combined-factors (hypoxia+copper) on the biochemical parameters and antioxidant defenses were studied in the neotropical fish Piaractus mesopotamicus. Fish were exposed for 48 h to 0.4 mg Cu(2+) L(-1) (0.4Cu), hypoxia=50 mm Hg (Hpx), and 0.4 mg Cu(2) L(-1)+hypoxia=50 mm Hg (0.4CuHpx). The exposure to 0.4Cu increased the reactive oxygen species (ROS) in the liver, accompanied by increases in superoxide dismutase (SOD) and decreases in catalase (CAT) activity, showing the influence of copper in this protection. The exposure to Hpx decreased the activity of glutathione peroxidase (GSH-Px) and CAT. Exposure to a combined-factor caused an increase in the ROS production followed by an increase in SOD and a decrease in GSH-Px and CAT. At 0.4Cu, fish presented a reduction in CAT, while in Hpx decreases in SOD, CAT and GSH-Px were observed in red muscles. Single-factors were insufficient to cause ROS production. In combined-factors, increased ROS formation and decreased SOD, CAT and GSH-Px were observed. RBC increased in all groups, but only under combined-factors was there an increase in hemoglobin. Copper plasma concentration increased in groups exposed to copper. Na(+)/K(+)-ATPase activity in gills decreased in 0.4Cu and 0.4CuHpx, and increased in Hpx. Metallothionein concentration in gills increased under combined-factors. Combined-factors caused significant disturbances in the antioxidant defenses and biochemical parameters than single-factors.     

Oxidative stress and genotoxic effects in gill and kidney of Anguilla anguilla L. exposed to chromium with or without pre-exposure to beta-naphthoflavone

Fish in the aquatic environment can be subjected to a multipollution state and the occurrence of sequential exposures is an important aspect of eco-toxicological research. In this context, a preceding exposure can affect a toxic response to a subsequent exposure. Therefore, the current study was based on sequential exposures, viz. to a PAH-like compound (beta-naphthoflavone, BNF) followed by a heavy metal (chromium, Cr), focusing on the assessment of oxidative stress responses and their role in induction of genotoxicity. Oxidative stress responses in gill and kidney were investigated in European eel (Anguilla anguilla L.), and measured as lipid peroxidation (LPO), glutathione peroxidase (GPX), catalase (CAT) and glutathione S-transferase (GST) activity, and reduced glutathione (GSH) concentration, whereas genotoxicity was measured as DNA strand breakage. Fish were exposed for 24 h to two Cr concentrations (100 microM, 1 mM), with or without pre-exposure to BNF (2.7 microM, 24 h). In gill, a GSH decrease was observed along with loss of DNA integrity at all exposure conditions except at the lowest Cr concentration, showing a crucial role of GSH over genotoxicity. Moreover, sporadic induction of antioxidant enzymes was not effective in the protection against genotoxicity. However, a different mechanism seems to occur in kidney, since the loss of DNA integrity detected for all exposed groups was not accompanied by alterations in antioxidant levels. With regards to peroxidative damage, both organs showed an LPO increase after sequential exposure to BNF and 100 microM Cr. However, no association between LPO induction and antioxidant responses could be established, showing that LPO is not predictable solely on the basis of antioxidant depletion. The interference of BNF pre-exposure with the response of organs to Cr showed a marked dependence on the Cr concentration. Gill showed synergistic effects on LPO and GPX increase, as well as on CAT and GSH decrease for the lowest Cr concentration. However, for the highest concentration an additive effect on decrease of DNA integrity and an antagonistic effect on the increase of GPX were observed. In kidney, synergistic effects were evident on LPO increase and GSH decrease for the lowest Cr concentration, as well as on CAT and GST decrease for the highest concentration. In contrast, an antagonistic action was observed on DNA integrity loss for both Cr concentrations. The current results are relevant in assessing the interactions of PAHs and metals and contribute to a better knowledge about oxidative stress and mechanisms of genotoxicity in fish.     

Disturbances on delta aminolevulinate dehydratase (ALA-D) enzyme activity by Pb2+, Cd2+, Cu2+, Mg2+, Zn2+, Na+, K+ and Li+: analysis based on coordination geometry and acid-base Lewis capacity

ALA-D (EC 4.2.1.24) is the first cytosolic enzyme in the haem metabolic pathway. Some metals compete with its major cofactor Zn(2+), modifying both enzyme structure and function. Our purpose was to contribute to the understanding of the biochemical role of metals such as Pb(2+), Cd(2+), Cu(2+), Mg(2+), Zn(2+), Na(+), K(+) and Li(+) on ALA-D, using chicken embryos as experimental model. Mg(2+) and Zn(2+) showed enzyme activation in yolk sac membrane (YSM) (113% at 10(-5) M Mg(2+) and from 10(-4) M Zn(2+)), and slight inactivation in liver. Cd(2+) and Cu(2+) caused a non allosteric inhibition in both tissues (100% from 10(-4) M). Surprisingly Pb(2+) was not such a strong inhibitor. Interference of cations during the Schiff base formation in enzymatic catalysis process is explained considering their Lewis acid-base capacity, coordination geometry and electron configuration of valence. Interactions among monovalent cations and biochemical substances are governed chiefly by its electrostatic potential. 0.1 M K(+) and 0.4 M Na(+) produced 30% of enzymatic inhibition by the interference on interactions among the functional subunits. Li(+) activated the YSM enzyme (130% at 10(-5) M) due to a more specific interaction. This study may contribute to elucidate for the first time the possible structural differences between the YSM and liver enzymes from chicken embryo.     

青菜幼苗体内几种保护酶的活性对Pb、Cd、Cr胁迫的反应研究

1 引言自从McCord在1969年第一次从牛红血细胞中发现超氧化物歧化酶(SOD)并且证明其功能是清除超氧化物以后,研究者们在植物细胞中也发现了这种酶,并且证明具有同样的功能.后来又发现植物细胞通过多种途径产生活性氧自由基,同时细胞也存在清除这些自由基的多种途径[5],两者形成平衡体系.但是,许多逆境因子如寒冷、干旱、干燥、水淹、重金属Al等都能影响植物体内活性氧代谢系统的平衡,产生大量的氧自由基,它们能够启动膜脂过氧化或膜脂脱脂作     

Removal of Pb2+ and Ni2+ by bio-sludge in sequencing batch reactor (SBR) and granular activated carbon-SBR (GAC-SBR) systems

Living bio-sludge from domestic wastewater treatment plant was used as adsorbent of heavy metals (Pb(2+), Ni(2+)) and its adsorption capacity was about 10-30% reduced by autoclaving at 110 degrees C for 10 min. The living bio-sludge acclimatized in synthetic industrial estate wastewater (SIEWW) without heavy metals showed the highest Pb(2+) and Ni(2+) adsorption capacities at 840+/-20 and 720+/-10 mg/g bio-sludge, respectively. The adsorbed Pb(2+) and Ni(2+) were easily eluted (70-77%) from bio-sludge by washing with 0.1 mol/l HNO(3) solution. The heavy metals (Pb(2+), Ni(2+)) removal efficiency of both SBR and GAC-SBR systems were increased with the increase of hydraulic retention time (HRT), or the decrease of organic loading. The SBR system showed higher heavy metals removal efficiency than GAC-SBR system at the same organic loading or HRT. The Pb(2+), Ni(2+), BOD(5), COD and TKN removal efficiencies of GAC-SBR system were 88.6+/-0.9%, 94.6+/-0.1%, 91.3+/-1.0%, 81.9+/-1.0% and 62.9+/-0.5%, respectively with industrial estate wastewater (IEWW) with 410 mg/l glucose, 5 mg/l Pb(2+) and 5 mg/l Ni(2+) under organic loading of 1.25 kg BOD(5)/m(3) d (HRT of 3 days). The bio-sludge quality (sludge volume index: SVI) of the system was less than 80 ml/g. The excess sludge from both SBR and GAC-SBR systems with SIEWW under the organic loading of 1.25-2.50 kg BOD(5)/m(3) d contained Pb(2+) and Ni(2+) at concentrations of 240-250 mg Pb(2+)/g bio-sludge and 180-210 mg Ni(2+)/g bio-sludge, respectively.     

Enzymatic responses to metal exposures in a freshwater fish Oreochromis niloticus

Freshwater fish Oreochromis niloticus were exposed to 5, 10 and 20 microM concentrations of Cd, Cu, Zn and Pb for 14 days and responses of several enzymes were determined subsequently. Liver catalase (CAT) activity was influenced by Cd and Pb exposures, while it was inhibited by Zn exposure. Copper, on the other hand, did not cause significant changes in CAT activity. Liver alkaline phosphatase (AP) activity was first stimulated at lowest (5 microM) exposure concentration, while there were significant inhibitions at higher (10 microM) exposure concentration. At the highest (20 microM) exposure concentration, AP activity was compensated coming to the control level, except Pb exposure. Intestine and serum AP activities were stimulated by all Zn exposures and 10 microM Cu exposure, while other exposures did not cause significant changes on AP activity. Na,K-ATPase activity in the gill and intestine was inhibited by all the metal exposures, except 20 microM Pb exposure that resulted in an increase in the activity in the gill. Similarly, muscle Ca-ATPase activity was inhibited by all the metal exposures, except Cu exposures. This study indicated that enzymatic systems may be used as a sensitive bioindicator of metal contamination in aquatic systems. Nevertheless, the results also stress the importance of addressing the sensitivity of these enzymes when they are used as a bioindicator for metal contamination, because the responses of the enzymes varied considerably according to metal types and concentrations.     

铜对梨形环棱螺抗氧化酶活性和金属硫蛋白含量的影响

本实验采用暴露重金属的方法,研究了不同浓度硫酸铜（Cu2+ 分别为0、0.005、0.01、0.02、0.05 mg/L）在不同暴露时间（0—14d）下对梨形环棱螺（Bellamya purificata）过氧化氢酶(CAT)、超氧化物歧化酶（SOD）、谷胱甘肽硫转移酶（GST）的活性、还原性谷胱甘肽（GSH）和金属硫蛋白（MT）含量的影响,以探讨Cu2+ 对梨形环棱螺的氧化损伤及其防御作用的机理,并为水环境Cu2+ 污染的早期诊断及生态风险评价提供科学的依据。结果表明：Cu2+对梨形环棱螺肝脏和鳃中CAT、SOD、GST、GSH 和MT 均有明显影响,表现出时间剂量效应。SOD在前4天、CAT在前3天酶活性总体上表现出诱导趋势, GST在前4天酶活性处于诱导状态,随着暴露时间的延长,酶活性下降,到第5天时表现出抑制趋势;随着时间的进一步增长,至14d时, 0.005 mg/L剂量组酶活性维持在正常值附近波动, 0.01 mg/L剂量组酶活性被诱导, 0.02 mg/L剂量组酶活性在肝脏中表现为诱导而在鳃中则被抑制,0.05 mg/L剂量组酶活性被抑制。肝脏和鳃GSH含量的变化与GST相似,在短时间内表现出诱导效应,肝脏GSH在暴露的前5天、鳃GSH在暴露的前4天均处于诱导状态,随着暴露时间的延长,0.005 mg/L剂量组表现出诱导,0.05 mg/L剂量组则受到抑制。MT在整个实验期间均处于诱导状态,各剂量组在0.5d被极显著诱导,随后MT含量出现起伏波动,有上升和下降,至第14天时达到一稳定水平。其中,0.01 mg/L剂量组肝脏的MT在整个实验期间均被极显著地诱导（P <0.01）,0.01 mg/L 剂量组的鳃组织MT除第10天外也被极显著诱导（P <0.01）。在暴露14d时,除0.05 mg/L剂量组的肝脏MT外,其余处于极显著诱导状态（P <0.01）。     

The effects of copper and other ions on the ribonucleic acid polymerase activity of isolated rat liver nuclei

1. The effects of various ions on the Mg(2+)- and Mn(2+)/ammonium sulphate-activated RNA polymerase activities of isolated liver nuclei were studied. 2. The Mg(2+)-activated RNA polymerase reaction was inhibited by more than 60% by Cd(2+), SeO(3) (2-), Be(2+), Cu(2+), Co(2+), Ca(2+) and La(3+), all at 1mm concentrations. 3. The Mn(2+)/ammonium sulphate-activated RNA polymerase reaction was strongly inhibited by Hg(2+), Cd(2+), Cu(2+) and Ag(+). The effect of Hg(2+), Cd(2+) and Ag(+) was relieved by cysteine or mercaptoethanol. 4. Inhibition by Cu(2+) was not affected by addition of DNA, and was relieved only partially by EDTA or histidine. 5. No changes of RNA polymerase activities were observed in nuclei isolated from the liver of rats treated with copper albuminate.     

Effects of Cu2+, CrO4(2-), Co2+ and Pb2+ on the monovalent ion content of goldfish (Carassius auratus gibelio) tissues studied by X-ray microanalysis

Carassius auratus gibelio was chosen as an organism with a high level of tolerance against heavy metal to investigate changes in monovalent ions content in its tissues. Fish were kept in 10 ppm Cu2+ (3h), CrO4(2-) (96h), Co2+ (96h), Pb2+ (8h) and control (96h) solutions, then tissues were dissected and prepared for X-ray microanalysis. K+, Na+ and Cl- concentration was measured and calculated. Short periods of time of fish acclimation to Cu2+ (3h) and Pb2+ (8h) caused fish to suffocate as a consequence of heavy metal ions binding to gill mucopolisaccharides. Cl- and Na+ content decreased after Cu2+ treatment in kidney cells and muscle fibers, and so did K+ concentration in gill cells in comparison to control. After that CrO4(2-) ions acclimation changes in all tissues and in all measured ions were observed. Similar effects were observed in Co2+ ions treatment but not for muscle fibers. Pb2+ ions caused an elevation of Cl- and Na+ ions content in gill cells and muscle fibers but decreasing in liver and kidney cells in comparison to control. Changes in monovalent ions concentration are probably related to heavy metal ions influence on ionic pump activity, their interaction with metabolic enzymes, ATP production or membrane phospholipids.     

Characterization of the PIB-Type ATPases present in Thermus thermophilus

P(IB)-type ATPases transport heavy metals (Cu(2+), Cu(+), Ag(+), Zn(2+), Cd(2+), Co(2+)) across biomembranes, playing a key role in homeostasis and in the mechanisms of biotolerance of these metals. Three genes coding for putative P(IB)-type ATPases are present in the genome of Thermus thermophilus (HB8 and HB27): the TTC1358, TTC1371, and TTC0354 genes; these genes are annotated, respectively, as two copper transporter (CopA and CopB) genes and a zinc-cadmium transporter (Zn(2+)/Cd(2+)-ATPase) gene. We cloned and expressed the three proteins with 8His tags using a T. thermophilus expression system. After purification, each of the proteins was shown to have phosphodiesterase activity at 65°C with ATP and p-nitrophenyl phosphate (pNPP) as substrates. CopA was found to have greater activity in the presence of Cu(+), while CopB was found to have greater activity in the presence of Cu(2+). The putative Zn(2+)/Cd(2+)-ATPase was truncated at the N terminus and was, surprisingly, activated in vitro by copper but not by zinc or cadmium. When expressed in Escherichia coli, however, the putative Zn(2+)/Cd(2+)-ATPase could be isolated as a full-length protein and the ATPase activity was increased by the addition of Zn(2+) and Cd(2+) as well as by Cu(+). Mutant strains in which each of the three P-type ATPases was deleted singly were constructed. In each case, the deletion increased the sensitivity of the strain to growth in the presence of copper in the medium, indicating that each of the three can pump copper out of the cells and play a role in copper detoxification.     

Effect of chlorpyrifos on thiobarbituric acid reactive substances, scavenging enzymes and glutathione in rat tissues

The present study showed that exposure of chlorpyrifos, O,O'-diethyl-O-3,5,6-trichloro-2-pyridyl phosphorothionate (CPF), a widely used pesticide in rats caused significant inhibition of acetylcholinesterase (AChE) activity in different tissues viz., liver, kidney and spleen. CPF exposure also generated oxidative stress in the body, as evidenced by increase in thiobarbituric acid reactive substances (TBARS), decrease in the levels of superoxide scavenging enzymes viz., superoxide dismutase (SOD), catalase (CAT) and glutathione peroxidase (GPx) in liver, kidney and spleen at all doses. Malondialdehyde levels were increased by 14%, 31% and 76% in liver, 11%, 31% and 64% in kidney and 32%, 75% and 99.9% in spleen when 50 mg, 100 mg and 200 mg/kg body wt. CPF was administered for three days. SOD and CAT activities were decreased in liver, kidney and spleen, while GPx activity showed slight increase in kidney at 50 mg and 100 mg dose, and decreased on further increase in dose of CPF. Liver and spleen showed dose-dependent decrease in GPx activity. The levels of reduced glutathione (GSH) was decreased, while oxidized glutathione (GSSG) was increased, thus a marked fall in GSH/GSSG ratio was observed in all tissues. A maximum decrease of 83% was observed in liver, followed by kidney and spleen, which showed 78% and 57% decrease, respectively in group given 200 mg/kg CPF. The levels of glucose-6-phosphate dehydrogenase (G6PDH) and glutathione reductase (GR) were also decreased in liver and kidney, while spleen showed increase at lower doses, but decrease at high dose of CPF. The data provide evidence for induction of oxidative stress on CPF exposure.     

Antioxidant defenses and biochemical changes in the neotropical fish pacu, Piaractus mesopotamicus: Responses to single and combined copper and hypercarbia exposure

This study investigated the potentially detrimental effects of copper and elevated aquatic CO(2) (hypercarbia), alone or in combination, on pacu, Piaractus mesopotamicus. Fish were exposed for 48h to control (no copper addition in normocarbia), to 400μg Cu(2+)L(-1), to hypercarbic (1% CO(2); PCO(2)=6.9mm Hg) water and to 400μg Cu(2+)L(-1)+hypercarbia. In liver the single factors caused an increase in lipid hydroperoxide concentration that was not observed when the factors were combined. Copper exposure elicited increased hepatic superoxide dismutase activity, irrespective of aquatic CO(2) level. On the other hand, the effects of copper on hepatic glutathione peroxidase activity were dependent on water CO(2) levels. The two stressors combined did not affect hepatic catalase activity. Hypercarbic water caused a decline in plasma glucose concentration, but this was not observed when hypercarbia was combined with copper exposure. Copper caused a decrease in branchial Na(+)/K(+)-ATPase activity that was independent of water CO(2) level. Copper caused an increase in branchial metallothionein concentration that was independent of water CO(2) level. Thus, branchial metallothionein and Na(+)/K(+)-ATPase were effective biomarkers of copper exposure that were not affected by water CO(2) level.     

A general model for biosorption of Cd2+, Cu2+ and Zn2+ by aerobic granules

Aerobic granules are microbial aggregates with a strong and compact structure. This study looked into the feasibility of aerobic granules as a novel type of biosorbent for the removal of individual Cd(2+), Cu(2+) and Zn(2+) from aqueous solution. Based on the thermodynamics of biosorption reaction, a general model was developed to describe the equilibrium biosorption of individual Cd(2+), Cu(2+) and Zn(2+) by aerobic granules. This model provides good insights into the thermodynamic mechanisms of biosorption of heavy metals. The model prediction was in good agreement with the experimental data obtained. It was further demonstrated that the Langmuir, Freundlich and Sips or Hill equations were particular cases of the proposed model. The biosorption capacity of individual Cd(2+), Cu(2+) and Zn(2+) on aerobic granules was 172.7, 59.6 and 164.5 mgg(-1), respectively. These values may imply that aerobic granules are effective biosorbent for the removal of Cd(2+), Cu(2+) and Zn(2+) from industrial wastewater.     

Various responses to copper and manganese exposure of Carassius auratus gibelio from two populations

The aim of this study was to compare the effect of pro-oxidants copper (Cu(2+), 0.005 and 0.050mg L(-1)) or manganese (Mn(2+), 0.17 and 1.7mg L(-1)) on Carassius auratus gibelio from polluted (B) and unpolluted (Z) sites after exposure for fourteen days. Fish from site B showed high levels of lipid peroxidation (TBARS concentration), lower levels of metallothionein (MT)-related metal, total glutathione (GSH), its redox index, superoxide dismutase (Cu,Zn- and Mn-SOD), glutathione-S-transferase (GST) and cholinesterase (ChE) activities and also higher MT-related thiol concentration in the liver and gills. A common effect of exposure was related to genotoxicity, a decrease in GSH and an increase in microsomal ethoxyresorufin O-deethylase activity in the liver. However, the systems of oxidative stress and biotransformation were more efficient in fish from the polluted site, while the responsivity of MTs in this fish was impaired. Principle Component Analysis separated the subgroups from the unpolluted site and fish loaded by lesser concentrations of metals on the one side, and fish from the polluted site jointly with fish exposed to higher concentrations of metals on the other side. The main distinguishing indices of sites and exposures selected by classification and regression tree (CART) analysis were MT characteristics and genotoxicity.     

重金属离子对凡纳滨对虾肝胰脏、鳃丝和血液SOD活力的影响

研究了3种重金属离子(Cu²⁺、Zn²⁺、Cd²⁺)在96 h内对凡纳滨对虾(Litopenaeus vannamei)对肝胰脏、鳃丝和血液超氧化物歧化酶(SOD)活力的影响.结果表明,凡纳滨对虾SOD活力在3种重金属离子作用下随取样时间变化显著(P＜0.0),Cu²⁺在实验浓度范围内(0.1～1 mg·L^-1),肝胰脏、鳃丝和血液的SOD活力随时间延长呈一峰值变化,Zn²⁺在10 mg·L^-1时对肝胰脏表现为显著抑制作用,Cd²⁺在0. mg·L^-1时对肝胰脏和鳃丝起显著抑制作用,0.2 mg·L^-1对鳃丝SOD活力无显著变化(P＞0.0),其他浓度Zn²⁺(＜10 mg·L^-1)、Cd²⁺(＜0.2 mg·L^-1)对各组织器官SOD活力的影响随时间延长均呈现先升高后下降的趋势.3种重金属离子对凡纳滨对虾肝胰脏、鳃丝、血液SOD活力的影响呈现明显的剂量-时间效应关系.其SOD活力大小顺序为肝胰脏＞鳃丝＞血液,3种重金属离子对凡纳滨对虾伤害大小顺序为Cd²⁺＞Cu²⁺＞Zn²⁺.     

千屈菜无菌苗对重金属铜和铬的生理生化响应

实验以千屈菜(Lythrum salicaria Linnaeus)无菌苗为材料, 用含不同浓度Cu2+(0、5、10、20和40 mg/L)和Cr6+(0、5、10、20和40 mg/L)的1/10霍格兰溶液对千屈菜进行培养, 测定叶绿素、丙二醛(MDA)、可溶性蛋白和可溶性糖等含量及超氧化物歧化酶(SOD)、过氧化物酶(POD)和过氧化氢酶(CAT)等活性的变化, 以探讨Cu2+和Cr6+对千屈菜无菌苗生理生化特征指标的影响。研究表明: 随着Cu2+浓度的增加, 千屈菜无菌苗渗透调节物质(可溶性糖和可溶性蛋白)表现为低促高抑现象, 膜脂化程度加剧, 但叶绿素含量基本未受影响, 且抗氧化酶活性(SOD、POD和CAT)持续上升。随着Cr6+浓度的升高, 叶绿素含量也基本未受影响, 膜脂化程度在0—20 mg/L未受显著影响。CAT活性受到持续抑制, 但SOD和POD活性持续上升。综上, 千屈菜对重金属铜和铬具有一定的抗性, 其叶绿素含量基本未受影响, 抗氧化酶活性上升, 且具有一定的渗透调节能力。在Cu2+浓度低于5 mg/L和Cr6+浓度低于20 mg/L时千屈菜生理生化指标所受影响相对较小。实验结果为进一步研究千屈菜对铜、铬和其他重金属的响应, 及千屈菜在水体修复方面的生态应用提供一定的理论基础。     

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。     

Effects of zinc and cadmium on erythrocyte antioxidant systems of a freshwater fish Oreochromis niloticus

In this work to determine the effects of metals exposure of Oreochromis niloticus on erythrocyte antioxidant systems, fish were exposed to 5.0 mg/L Zn, 1.0 mg/L Cd, and 5.0 mg/L Zn + 1.0 mg/L Cd mixtures for 7 and 14 days and reduced glutathione (GSH) level, catalase (CAT), and glucose‐6‐phosphate dehydrogenase (G6PD) activities were investigated. In addition, Zn or Cd levels in whole blood were studied. Erythrocyte GSH level and CAT and G6PD enzyme activities increased in response to single and combined Zn and Cd exposure. The elevation observed in the CAT activity was higher in the Cd alone, and in combination with Zn, than in Zn alone. Time‐dependent alteration was not observed in all antioxidant parameters. Exposure to metals (alone and in mixture) resulted in elevatation of Zn and Cd levels in the blood. Concentration of metals in the blood of fish exposed to the Zn + Cd combination was lower than in fish exposed to the single metal. This study demonstrates that metals caused oxidative stress in fish erythrocytes, and an adaptation with an increase in CAT and G6PD activities and GSH level, which were important in the protection against metal damage, was observed. © 2010 Wiley Periodicals, Inc. J Biochem Mol Toxicol 24:223–229, 2010; View this article online at wileyonlinelibrary.com . DOI 10.1002/jbt.20327