Screening of heavy metal-tolerant actinomycetes isolated from the Salí River

Fifty-three strains of actinomycetes resistant to heavy metals were isolated from the Salí River in northwest Argentina. Screening procedures that involve solid and liquid synthetic media containing Cd(2+), Cu(2+), or Hg(2+) allowed the selection of six strains. These strains showed a quantitative sorption of Cd(2+) and Cu(2+) by more than 98% of the initial metal concentrations (0.1, 0.5, and 1.0 mM) tested.     

Novel synthetic phytochelatin-based capacitive biosensor for heavy metal ion detection

A novel capacitance biosensor based on synthetic phytochelatins for sensitive detection of heavy metals is described. Synthetic phytochelatin (Glu-Cys)(20)Gly (EC20) fused to the maltose binding domain protein was expressed in Escherichia coli and purified for construction of the biosensor. The new biosensor was able to detect Hg(2+), Cd(2+), Pb(2+), Cu(2+) and Zn(2+) ions in concentration range of 100 fM-10 mM, and the order of sensitivity was S(Zn)>S(Cu)>S(Hg)>S(Cd) congruent with S(Pb). The biological sensing element of the sensor could be regenerated using EDTA and the storage stability of the biosensor was 15 days.     

Metal ions may suppress or enhance cellular differentiation in Candida albicans and Candida tropicalis biofilms

Candida albicans and Candida tropicalis are polymorphic fungi that develop antimicrobial-resistant biofilm communities that are characterized by multiple cell morphotypes. This study investigated cell type interconversion and drug and metal resistance as well as community organization in biofilms of these microorganisms that were exposed to metal ions. To study this, Candida biofilms were grown either in microtiter plates containing gradient arrays of metal ions or in the Calgary Biofilm Device for high-throughput susceptibility testing. Biofilm formation and antifungal resistance were evaluated by viable cell counts, tetrazolium salt reduction, light microscopy, and confocal laser scanning microscopy in conjunction with three-dimensional visualization. We discovered that subinhibitory concentrations of certain metal ions (CrO(4)(2-), Co(2+), Cu(2+), Ag(+), Zn(2+), Cd(2+), Hg(2+), Pb(2+), AsO(2)(-), and SeO(3)(2-)) caused changes in biofilm structure by blocking or eliciting the transition between yeast and hyphal cell types. Four distinct biofilm community structure types were discerned from these data, which were designated "domed," "layer cake," "flat," and "mycelial." This study suggests that Candida biofilm populations may respond to metal ions to form cell-cell and solid-surface-attached assemblages with distinct patterns of cellular differentiation.     

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.     

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.     

Heavy Metal Resistance Patterns of Frankia Strains

The sensitivity of 12 Frankia strains to heavy metals was determined by a growth inhibition assay. In general, all of the strains were sensitive to low concentrations (<0.5 mM) of Ag¹⁺, AsO₂¹⁻, Cd²⁺, SbO₂¹⁻, and Ni²⁺, but most of the strains were less sensitive to Pb²⁺ (6 to 8 mM), CrO₄²⁻ (1.0 to 1.75 mM), AsO₄³⁻ (>50 mM), and SeO₂²⁻ (1.5 to 3.5 mM). While most strains were sensitive to 0.1 mM Cu²⁺, four strains were resistant to elevated levels of Cu²⁺ (2 to 5 mM and concentrations as high as 20 mM). The mechanism of SeO₂²⁻ resistance seems to involve reduction of the selenite oxyanion to insoluble elemental selenium, whereas Pb²⁺ resistance and Cu²⁺ resistance may involve sequestration or binding mechanisms. Indications of the resistance mechanisms for the other heavy metals were not as clear.     

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 Cu(2+) and Pb(2+) on different fish species: liver cytochrome P450-dependent monooxygenase activities and FTIR spectra

The effects of Cu(2+)-sulfate and Pb(2+)-acetate on carp (Cyprinus carpio L.), silver carp (Hypopthalmichtys molitrix V.) and wels (Silurus glanis L.) were studied. The liver microsomal Cyt P450 content, the EROD, ECOD and APND monooxygenase activities were measured. In vivo treatment with 1 mg L(-1) Cu(2+) significantly elevated the activities of these enzymes and Cyt P450 content in silver carp livers. The high-dose Cu(2+) treatment (10 mg L(-1)) on silver carp caused two-fold higher induction in the P450 dependent monooxygenase isoensymes than in wels. Although the 2 mg kg(-1) treatment with Pb(2+) in carp elevated significantly the P450 content, the EROD isoenzyme activities were significantly decreased after 1 day, showing the destructive effect of metal ion on the enzyme system. In vitro, Cu(2+) and Pb(2+) decreased the Cyt P450 content in the carp liver microsomes and the absorption peak shifted to higher wavelength. Fourier Transform Infrared (FTIR) spectroscopy was used to detect the damaging effects of the heavy metals. According to the inhibitory potency to Cu(2+), the most sensitive isoenzyme was the EROD in wels, the least was the silver carp's isoenzyme. The investigated fish P450 isoenzymes showed, that the Cu(2+) was a stronger inhibitor than Pb(2+).     

Biosorption behavior and mechanism of heavy metals by the fruiting body of jelly fungus (Auricularia polytricha) from aqueous solutions

The aim of this study was to investigate the biosorption characteristics of Cd(2+), Cu(2+), and Pb(2+) by the fruiting body of jelly fungus Auricularia polytricha. Batch experiments were conducted to characterize the kinetics, equilibrium, and mechanisms of the biosorption process. Optimum values of pH?5, biomass dosage 4?g?L(-1), and contact time 60?min provided maximum biosorption capacities of A. polytricha for Cd(2+), Cu(2+), and Pb(2+) of 63.3, 73.7, and 221?mg?g(-1), respectively. The maximum desorption was achieved using 0.05?mol?L(-1) HNO(3) as an elute. The fruiting body was reusable at least for six cycles of operations. The pseudo-second-order model was the best to describe the biosorption processes among the three kinetic models tested. Freundlich and Dubinin-Radushkevich models fitted the equilibrium data well, indicating a heterogeneous biosorbent surface and the favorable chemisorption nature of the biosorption process. A Fourier transform infrared spectroscopy analysis indicated that carboxyl, amine/hydroxyl, amino, phosphoryl, and C-N-C were the main functional groups to affect the biosorption process. Synergistic ion exchange and surface complexation were the dominant mechanisms in the biosorption process. The present work revealed the potential of jelly fungus (fruiting body of A. polytricha) to remove toxic heavy metals from contaminated water.     

Copper induces apoptosis in Aedes C6/36 cells

The Aedes albopictus C6/36 cell clone is used as a model system to study the effects of heavy metals on insect cells. Here we report on the effects of Cu(2+) on these cells. Similar to Cd(2+) and Hg(2+), Cu(2+) induces hyperpolymerization of the microtubules; moreover, with Cu(2+) this is followed by cell aggregation and massive apoptosis. This process, which is cell density dependent, is maximal between 0.75 and 1 mM; this is just under the LC(50) as determined by a membrane integrity test. At higher Cu(2+) concentrations, cell death occurs by necrosis. Apoptosis was ascertained by fluorescence and electron microscopy and by agarose gel electrophoresis. At 0.75 mM, apoptosis started at 18-hr exposure time and the amount of apoptotic cells increased almost linearly until 42 hr; then a plateau was reached with 70-80% apoptotic cells. This is the first report on Cu(2+)-induced apoptosis in insect cells. Possible induction mechanisms are discussed in the light of existing literature on vertebrate cells.     

Characterization of stress responses of heavy metal and metalloid inducible promoters in synechocystis PCC6803

In several biotechnological applications of living bacterial cells with inducible gene expression systems, the extent of overexpression and the specificity to the inducer are key elements. In the present study, we established the concentration ranges of Zn(2+), Ni(2+), Co(2+), AsO(2)(-), and Cd(2+) ions that caused significant activation of the respective promoters of Synechocystis sp. without concomitant unspecific stress responses. The low expression levels can be increased up to 10-100-fold upon treatments with Cd(2+), AsO(2)(-), Zn(2+), and Co(2+) ions and up to 800-fold upon Ni(2+) treatment. These results facilitate the development of conditional gene expression systems in cyanobacteria.     

Emerging mechanisms for heavy metal transport in plants

Heavy metal ions such as Cu(2+), Zn(2+), Mn(2+), Fe(2+), Ni(2+) and Co(2+) are essential micronutrients for plant metabolism but when present in excess, these, and non-essential metals such as Cd(2+), Hg(2+) and Pb(2+), can become extremely toxic. Thus mechanisms must exist to satisfy the requirements of cellular metabolism but also to protect cells from toxic effects. The mechanisms deployed in the acquisition of essential heavy metal micronutrients have not been clearly defined although a number of genes have now been identified which encode potential transporters. This review concentrates on three classes of membrane transporters that have been implicated in the transport of heavy metals in a variety of organisms and could serve such a role in plants: the heavy metal (CPx-type) ATPases, the natural resistance-associated macrophage protein (Nramp) family and members of the cation diffusion facilitator (CDF) family. We aim to give an overview of the main features of these transporters in plants in terms of structure, function and regulation drawing on information from studies in a wide variety of organisms.     

Kinetic analysis of metal binding to the amino-terminal domain of ZntA by monitoring metal-thiolate charge-transfer complexes

ZntA, a P(1B)-ATPase transporter from Escherichia coli, mediates resistance specifically to Pb(2+), Zn(2+), and Cd(2+) by active efflux. ZntA has a hydrophilic N-terminal domain that binds one metal ion. This domain, approximately 120 residues long, contains the GXXCXXC motif that has been shown to be the binding site for metal ions such as Cu(+) and Zn(2+) in P(1B)-type ATPases, and an additional cysteine-rich motif, CCCDGAC. We report here that binding of Pb(2+) and Cd(2+) to this domain produces changes in the absorbance spectrum in the 250-400 nm range indicative of metal-thiolate charge-transfer complexes. The spectral changes indicate that only two cysteines are ligands to Cd(2+), but three or more cysteines are involved in binding Pb(2+); this confirms earlier results that the GXXCXXC sequence is not sufficient to bind Pb(2+), which likely involves residues from the CCCDGAC motif. The absorbance changes were used to measure metal binding kinetics of the N-terminal domain using stopped-flow techniques. Binding was described by simple second-order kinetics with a rate constant, k(on), of approximately 10(6)-10(7) M(-)(1) s(-)(1), at 4 degrees C. The activation energy of binding is similar for both Pb(2+) and Cd(2+); however, the entropy change is greater for Pb(2+). The surprisingly large rate constant for metal binding to the N-terminal domain of ZntA, compared to its low turnover rate, indicates that this step is not rate limiting in the overall transport mechanism. These results, in conjunction with earlier studies, suggest that metal binding to the transmembrane site in ZntA or metal release from the transporter is the slow step in the reaction cycle.     

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.     

Interplay of different transporters in the mediation of divalent heavy metal resistance in Pseudomonas putida KT2440

According to in silico analysis, the genome of Pseudomonas putida KT2440 encodes at least four Zn/Cd/Pb efflux transporters-two P-type ATPases (CadA1 and CadA2) and two czc chemiosmotic transporters (CzcCBA1 and CzcCBA2). In this study we showed that all these transporters are functional, but under laboratory conditions only two of them were involved in the mediation of heavy metal resistance in P. putida KT2440. CadA2 conferred Cd(2+) and Pb(2+) resistance, whereas CzcCBA1 was involved in export of Zn(2+), Cd(2+), and possibly Pb(2+). CadA1, although nonfunctional in P. putida, improved Zn(2+) resistance and slightly improved Cd(2+) resistance when it was expressed in Escherichia coli. CzcCBA2 contributed to Zn resistance of a czcA1-defective P. putida strain or when the CzcA2 subunit was overexpressed in a transporter-deficient strain. It seemed that CzcA2 could complex with CzcC1 and CzcB1 subunits and therefore complement the loss of CzcA1. The CzcCBA2 transporter itself, however, did not function. Expression of cadA1, cadA2, and czcCBA1 was induced by heavy metals, and the expression levels were dependent on the growth medium and growth phase. Expression of cadA2 and czcCBA1 was nonspecific; both genes were induced by Zn(2+), Cd(2+), Pb(2+), Ni(2+), Co(2+), and Hg(2+). On the other hand, remarkably, expression of cadA1 was induced only by Zn(2+). Possible roles of distinct but simultaneously functioning transporters are discussed.     

The ionophore nigericin transports Pb2+ with high activity and selectivity: a comparison to monensin and ionomycin

The K(+) ionophore nigericin is shown to be highly effective as an ionophore for Pb(2+) but not other divalent cations, including Cu(2+), Zn(2+), Cd(2+), Mn(2+), Co(2+), Ca(2+), Ni(2+), and Sr(2+). Among this group a minor activity for Cu(2+) transport is seen, while for the others activity is near or below the limit of detection. The selectivity of nigericin for Pb(2+) exceeds that of ionomycin or monensin and arises, at least in part, from a high stability of nigericin-Pb(2+) complexes. Plots of log rate vs log Pb(2+) or log ionophore concentration, together with the pH dependency, indicate that nigericin transports Pb(2+) via the species NigPbOH and by a mechanism that is predominately electroneutral. As with monensin and ionomycin, a minor fraction of activity may be electrogenic, based upon a stimulation of rate that is produced by agents which prevent the formation of transmembrane electrical potentials. Nigericin-catalyzed Pb(2+) transport is not inhibited by physiological concentrations of Ca(2+) or Mg(2+) and is only modestly affected by K(+) and Na(+) concentrations in the range of 0-100 mM. These characteristics, together with higher selectivity and efficiency, suggest that nigericin may be more useful than monensin in the treatment of Pb intoxication.     

Mechanism of arsenate resistance in the ericoid mycorrhizal fungus Hymenoscyphus ericae

Arsenate resistance is exhibited by the ericoid mycorrhizal fungus Hymenoscyphus ericae collected from As-contaminated mine soils. To investigate the mechanism of arsenate resistance, uptake kinetics for arsenate (H(2)AsO(4)(-)), arsenite (H(3)AsO(3)), and phosphate (H(2)PO(4)(-)) were determined in both arsenate-resistant and -non-resistant H. ericae. The uptake kinetics of H(2)AsO(4)(-), H(3)AsO(3), and H(2)PO(4)(-) in both resistant and non-resistant isolates were similar. The presence of 5.0 microM H(2)PO(4)(-) repressed uptake of H(2)AsO(4)(-) and exposure to 0.75 mM H(2)AsO(4)(-) repressed H(2)PO(4)(-) uptake in both H. ericae. Mine site H. ericae demonstrated an enhanced As efflux mechanism in comparison with non-resistant H. ericae and lost approximately 90% of preloaded cellular As (1-h uptake of 0.22 micromol g(-1) dry weight h(-1) H(2)AsO(4)(-)) over a 5-h period in comparison with non-resistant H. ericae, which lost 40% of their total absorbed H(2)AsO(4)(-). As lost from the fungal tissue was in the form of H(3)AsO(3). The results of the present study demonstrate an enhanced H(3)AsO(3) efflux system operating in mine site H. ericae as a mechanism for H(2)AsO(4)(-) resistance. The ecological significance of this mechanism of arsenate resistance is discussed.