Spectroscopic properties of the metalloregulatory Cd(II) and Pb(II) sites of S. aureus pI258 CadC

Staphylococcus aureus pI258 CadC is an extrachromosomally encoded metalloregulatory repressor protein from the ArsR superfamily which negatively regulates the expression of the cad operon in a metal-dependent fashion. The metalloregulatory hypothesis holds that direct binding of thiophilic divalent cations including Cd(II), Pb(II), and Zn(II) by CadC allosterically regulates the DNA binding activity of CadC to the cad operator/promoter (O/P). This report presents a detailed characterization of the metal binding and DNA binding properties of wild-type CadC. The results of analytical ultracentrifugation experiments suggest that both apo- and Cd(1)-CadC are stable or weakly dissociable homodimers characterized by a K(dimer) = 3.0 x 10(6) M(-1) (pH 7.0, 0.20 M NaCl, 25.0 degrees C) with little detectable effect of Cd(II) on the dimerization equilibrium. As determined by optical spectroscopy, the stoichiometry of Cd(II) and Pb(II) binding is approximately 0.7-0.8 mol/mol of wild-type CadC monomer. Chelator (EDTA) competition binding isotherms reveal that Cd(II) binds very tightly, with K(Cd) = 4.3 (+/-1.8) x 10(12) M(-1). The results of UV-Vis and X-ray absorption spectroscopy of the Cd(1) complex are consistent with a tetrathiolate (S(4)) complex formed by four cysteine ligands. The (113)Cd NMR spectrum reveals a single resonance of delta = 622 ppm, consistent with an S(3)(N,O) or unusual upfield-shifted S(4) complex. The Pb(II) complex reveals two prominent absorption bands at 350 nm (epsilon = 4000 M(-1) cm(-1)) and 250 nm (epsilon = 41 000 M(-1) cm(-1)), spectral properties consistent with three or four thiolate ligands to the Pb(II) ion. The change in the anisotropy of a fluorescein-labeled oligonucleotide containing the cad O/P upon binding CadC and analyzed using a dissociable CadC dimer binding model reveals that apo-CadC forms a high-affinity complex [K(a) = (1.1 +/- 0.3) x 10(9) M(-1); pH 7.0, 0.40 M NaCl, 25 degrees C], the affinity of which is reduced approximately 300-fold upon the binding of a single molar equivalent of Cd(II) or Pb(II). The implications of these findings on the mechanism of metalloregulation are discussed.     

Activation of pine cone using Fenton oxidation for Cd(II) and Pb(II) removal

This paper describes activation of pine cone with Fenton reagent and determines the removal of Cd(II) and Pb(II) ions from aqueous solution. Changes of the surface properties of adsorbent materials were determined by the FT-IR and SEM analysis after activation of pine cone. The effect of Fe(2+)/H(2)O(2) ratio, ORP, pH and contact time were determined. Different adsorption isotherms were also obtained using concentrations of heavy metal ions ranging from 0.1 to 150mgL(-1). The adsorption process follows pseudo-first-order reaction kinetics and follows the Langmuir adsorption isotherm. The study discusses thermodynamic parameters, including changes in Gibbs free energy, entropy, and enthalpy, for the adsorption of Cd(II) and Pb(II) on activated cone, and revealed that the adsorption process was spontaneous and exothermic under natural conditions. The maximum removal efficiencies were obtained as 91% and 89% at pH 7 with 90 and 105-min contact time for Cd(II) and Pb(II), respectively.     

德国鸢尾对Cd胁迫的生理生态响应及积累特性

通过盆栽研究了Cd胁迫下德国鸢尾的生长状况、生态效应、生理特性及吸收和富集Cd的能力.结果表明:德国鸢尾对小于5 mg/kg的Cd有较强的耐性,适用于城区土壤修复;Cd浓度大于5 mg/kg时抑制德国鸢尾生长,降低了其生态效应.随着Cd浓度的增大,德国鸢尾根系活力、叶绿素含量和含水量逐渐降低,游离脯氨酸和可溶性糖含量先升高后降低,细胞膜透性逐渐升高.Cd在德国鸢尾体内分布为根系＞地上部分,随着Cd浓度的增大,德国鸢尾根系和地上部分Cd积累浓度逐渐升高、富集系数和转运系数逐渐降低;Cd浓度为20 mg/kg时德国鸢尾对Cd的积累量最大,为2.122 mg/plant.     

Impact of Humin on Soil Adsorption and Remediation of Cd(II), Pb(II), and Cu(II)

In situ immobilization constitutes a promising technology for the mitigation of contaminants, through the reduction of metal bioavailability and mobility. This study investigated the adsorption isotherms and kinetic characteristics of humin extracted from peat soils. We also studied the influences of the pH, ionic strengths, and soluble organic matter concentrations of soil solutions on the adsorptive properties of humin, and compared its ability to detoxify potentially toxic metals in both actual and simulated soil solutions. The study results indicated that humin contains a massive population of oxygen-containing functional groups. Its adsorption capacity for Pb(II) was greater than that for Cu(II), which exceeded that for Cd(II). The adsorption of humin for Pb(II) conformed to the Freundlich model, while the adsorption of humin for Cd(II) and Cu(II) followed the Langmuir model. The adsorption kinetics of humin with respect to potentially toxic metals aligned well with second-order kinetics equations. As the pH was elevated, the potentially toxic metal adsorption by humin increased rapidly. Electrolyte ions and tartaric acids in solution both inhibited the adsorption of potentially toxic metals by humin, and its ability to inactivate potentially toxic metals. This was shown to be improved in actual field soil solutions in contrast to simulated soil solutions.     

Cd(II), Pb(II) and Zn(II) ions regulate expression of the metal-transporting P-type ATPase ZntA in Escherichia coli

Feeding bioassay results established that the soybean cysteine proteinase inhibitor N (soyacystatin N, scN) substantially inhibits growth and development of western corn rootworm (WCR), by attenuating digestive proteolysis [Zhao, Y. et al. (1996) Plant Physiol. 111, 1299-1306]. Recombinant scN was more inhibitory than the potent and broad specificity cysteine proteinase inhibitor E-64. WCR digestive proteolytic activity was separated by mildly denaturing SDS-PAGE into two fractions and in-gel assays confirmed that the proteinase activities of each were largely scN-sensitive. Since binding affinity to the target proteinase [Koiwa, H. et al. (1998) Plant J. 14, 371-380] governs the effectiveness of scN as a proteinase inhibitor and an insecticide, five peptides (28-33 kDa) were isolated from WCR gut extracts by scN affinity chromatographic separation. Analysis of the N-terminal sequence of these peptides revealed similarity to a cathepsin L-like cysteine proteinase (DvCAL1, Diabrotica virgifera virgifera cathepsin L) encoded by a WCR cDNA. Our results indicate that cathepsin L orthologs are pivotal digestive proteinases of WCR larvae, and are targets of plant defensive cystatins (phytocystatins), like scN.     

Physiological responses,tolerance efficiency,and phytoextraction potential of Hylotelephium spectabile (Boreau) H. Ohba under Cd stress in hydroponic condition

Abstract

A sand hydroponic experiment with different concentrations of 0, 5, 10, 20, 40?mg L^?1 Cd was used to study the growth and physiological response of Hylotelephium spectabile (Boreau) H. Ohba. and its phytoextraction potential for Cd. The results showed that total plant biomass under 5?mg L^?1 Cd treatment was slightly affected. The content of malondialdehyde (MDA) in leaf exposed to Cd was higher, and the POD and CAT activity exhibited a positive response to the low level of Cd addition (5?mg·L^?1). The photosynthesis pigments were slightly inhibited, and the ultrastructure of chloroplast remained intact after treatment with 10?mg L^?1 Cd. The maximum leaf Cd content (603?mg·kg^?1) was found in 5?mg L^?1 Cd treatment, then decreased with the Cd level increased. The maximum Cd content in the shoots far exceeds the threshold level (100?mg kg^?1) for a Cd-hyperaccumulator plant with the value of translocation factor (TF_shoot/root) for Cd reaching up to 5.62. In conclusion, H. spectabile showed normal growth and physiological response and high shoot Cd accumulation under 5?mg L^?1 Cd stress, which made it to be a good candidate for phytoextraction of low-level Cd polluted environment.     

Membrane topology of the p1258 CadA Cd(II)/Pb(II)/Zn(II)-translocating P-type ATPase

Plasmid pl258 carries the cadA gene that confers resistance to cadmium, lead, and zinc. CadA catalyzes ATP-dependent cadmium efflux from cells of Staphylococcus aureus. It is a member of the superfamily of P-type ATPases and belongs to the subfamily of soft metal ion pumps. In this study the membrane topology of this P-type ATPase was determined by constructing fusions with the topological reporter genes phoA or lacZ. A series of 44 C-terminal truncated CadAs were fused with one or the other reporter gene, and the activity of each chimeric protein was determined. In addition, the location of the first transmembrane segment was determined by immunoblot analysis. The results are consistent with the pl258 CadA ATPase having eight transmembrane segments. The first 109 residues is a cytosolic domain that includes the Cys(X)₂Cys motif that distinguishes soft metal ion-translocating P-type ATPases from their hard metal ion-translocating homologues. Another feature of soft metal ion P-type ATPases is the CysProCys motif, which is found in the sixth transmembrane segment of CadA. The phosphorylation site and ATP binding domain conserved in all P-type ATPases are situated within the large cytoplasmic loop between the sixth and seventh transmembrane segments.     

Formation of binary complexes of Pb(II), Cd(II) and Hg(II) with maleic acid in CTAB-water mixtures

Abstract

Complexation of toxic metal ions with maleic acid in (0.0–2.5% w/v) cetyltrimethylammonium bromide (CTAB)–water mixtures has been studied pH-metrically at ambient conditions and an ionic strength of 0.16 mol L^-1. The existence of different binary species was established from modelling studies using the computer program MINIQUAD75. The best-fit chemical models were selected based on statistical parameters such as the crystallographic R factor and sum of the squares of residuals in mass-balance equations. The models for binary complex systems contain the chemical species ML₂, ML₂H and ML₃ for Pb(II), Cd(II) and Hg(II) in CTAB–water mixtures. The trend in the variation of stability constants with change in the mole fraction of the medium was explained based on electrostatic and non-electrostatic forces. Distribution of the species with pH at different compositions of CTAB–water mixtures was also presented.     

Zn(II)-113Cd(II) and Zn(II)-Mg(II) hybrids of alkaline phosphatase. 31P and 113Cd NMR

Methods have been developed for the addition of different metal ion species to the three distinct pairs of metal sites (A, B, and C) found in the dimer of apoalkaline phosphatase. This allows the preparation of hybrid alkaline phosphatases in which A and B sites of each monomer contain two different species of metal ion or the A and B sites of one monomer contain the same species of metal ion, while the adjacent monomer contains a second species. The following hybrids have been characterized in detail: (Zn(II)ACd(II)B)2 alkaline phosphatase, (Zn(II)AMg(II)B)2 alkaline phosphatase, (Cd(II)AZn(II)B)2 alkaline phosphatase, and (Zn(II)AZn(II]B)(Cd(II)ACd(II)B) alkaline phosphatase. 31P and, where appropriate, 113Cd NMR have been used to monitor the behavior of the covalent (E-P) and noncovalent (E X P) phosphointermediates and of the A and B metal ions. From the pH dependencies of the E-P in equilibrium E X P in equilibrium E + Pi equilibria, it is clear that A site metal is the dominant influence in dephosphorylation of E-P and may have a coordinated water molecule, which ionizes to ZnOH- at a low pH providing the nucleophile for dephosphorylation. A site metal also serves to coordinate phosphate in the E X P complex. B site metal has a much smaller effect on dephosphorylation rates, although it does dramatically alter the Pi dissociation rate, which is the rate-limiting step for the native enzyme at alkaline pH, and is probably important in neutralizing the charge on the phosphoseryl residue, thus potentiating the nucleophilic attack of the OH- bound at A site. Phosphate dissociation is slowed markedly by replacement of B site zinc by cadmium. There is clear evidence for long range effects of subunit-subunit interactions, since metal ion and phosphate binding at one active center alters the environments of A and B site metal ions and phosphoserine at the other active site.     

Peptidic models for the binding of Pb(II), Bi(III) and Cd(II) to mononuclear thiolate binding sites

Herein, we evaluate the binding of Pb(II) and Bi(III) to cysteine-substituted versions of the TRI peptides [AcG-(LKALEEK)₄G-NH₂] which have previously been shown to bind Hg(II) and Cd(II) in unusual geometries as compared with small-molecule thiol ligands in aqueous solutions. Studies of Pb(II) and Bi(III) with the peptides give rise to complexes consistent with the metal ions bound to three sulfur atoms with M–S distances of 2.63 and 2.54 Å, respectively. Competition experiments between the metal ions Pb(II), Cd(II), Hg(II) and Bi(III) for the peptides show that Hg(II) has the highest affinity, owing to the initial formation of the extremely strong HgS₂ bond. Cd(II) and Pb(II) have comparable binding affinities at pH > 8, while Bi(III) displays the weakest affinity, following the model, M(II) + (TRI LXC)₃ ^3? → M(II)(TRI LXC)₃ ^?. While the relevant equilibria for Hg(II) binding to the TRI peptides corresponds to a strong first step forming Hg(TRI LXC)₂(HTRI LXC), followed by a single deprotonation to give Hg(TRI LXC)₃ ^?, the binding of Cd(II) and Pb(II) is consistent with initial formation of M(II)(TRI LXC)(HTRI LXC)₂ ⁺ at pH < 5 followed by a two-proton dissociation step (pK _a2) yielding M(II)(TRI LXC)₃ ^?. Pb(II)(TRI LXC)(HTRI LXC)₂ ⁺ converts to Pb(II)(TRI LXC)₃ ^? at slightly lower pH values than the corresponding Cd(II)–peptide complexes. In addition, Pb(II) displays a lower pK _a of binding to the “d”-substituted peptide, (TRI L12C, pK _a2 = 12.0) compared with the “a”-substituted peptide, (TRI L16C, pK _a2 = 12.6), the reverse of the order seen for Hg(II) and Cd(II). Pb(II) also showed a stronger binding affinity for TRI L12C (K _bind = 3.2 × 10⁷ M^?1) compared with that with TRI L16C (K _bind = 1.2 × 10⁷ M^?1) at pH > 8.     

Characterization of Aqueous Pb(II) and Cd(II) Biosorption on Native and Chemically Modified Alstonia macrophylla Saw Dust

This study was conducted in order to understand the mechanism of Cd and Pb adsorption in aqueous solutions by raw and modified saw dust (SD) of Alstonia macrophylla. The biosorbent was characterized by Boehm titration, specific surface area, scanning electron microscopy (SEM), X-ray energy dispersion (EDAX), and Fourier transform infrared (FTIR) analyses. SD was treated using organic acids and bases. Batch studies were conducted for raw and modified SD to determine the effect of initial concentration, pH, ionic strength, and contact time on metal adsorption. The specific surface area and total basic and acidic groups of SD were 77 m²/g and 1521 and 2312 μmol/g, respectively. The adsorption of both metals onto SD was pH dependent. No ionic strength dependency was observed in adsorption of Cd and Pb at pH >6, indicating inner sphere surface complexation. Monolayer adsorption is dominant in both metal sorptions by SD. Furthermore, there is no competition between metals on adsorption and raw SD was found to be suitable for removal of Cd and Pb as compared to organic acid– or base-treated SD. Maximum adsorption capacity of SD for Cd and Pb were 30.6 and 204.2 mg/g, respectively. Results indicate that the A. macrophylla SD can be considered as a potential material for metal ion removal from wastewater.     

A family of polyamino phenolic macrocyclic ligands. Acid-base and coordination properties towards Co(II), Ni(II), Cu(II), Zn(II), Cd(II) and Pb(II) ions

The acid-base and coordination properties towards Co(II), Ni(II), Cu(II), Zn(II), Cd(II) and Pb(II) of four polyamino-phenol macrocycles 15-hydroxy-3,6,9-triazabicyclo[9.3.1]pentadeca-11,13,1¹⁵-triene L1, 18-hydroxy-3,6,9,12-tetraazabicyclo[12.3.1]octadeca-14,16,1¹⁸-triene L2, 21-hydroxy-3,6,9,12,15-pentaazabicyclo[15.3.1]enaicosa-17,19,1²¹-triene L3 and 24-hydroxy-3,6,9,12,15,18-hexaazabicyclo[18.3.1]tetraicosa-20,22,1²⁴-triene L4 are reported. The protonation and stability constants were determined by means of potentiometric measurements in 0.15 mol dm⁻³ NMe₄Cl aqueous solution at 298.1 K. L1 forms highly unsaturated Co(II), Cu(II), Zn(II) and Cd(II) mononuclear complexes that are prone to give dimeric dinuclear species with [(MH₋₁L1)₂]²⁺ stoichiometry, in solution. L2 forms stable Co(II), Ni(II), Cu(II), Zn(II), Cd(II) and Pb(II) mononuclear complexes that can coordinate external species as OH⁻ anion, giving hydroxylated complexes at alkaline pH. L3 forms stable Co(II), Ni(II), Cu(II), Zn(II), Cd(II) and Pb(II) mononuclear complexes and Co(II), Ni(II), Cu(II) and Zn(II) dinuclear [M₂H₋₁L3]³⁺ species. L4 forms stable mono- and dinuclear Co(II), Cu(II), Zn(II) and Cd(II) complexes, but only mononuclear species with Pb(II). The effect of macrocyclic size is considered in the discussion of results.     

Cd (II) stress response during the growth of Aspergillus niger B 77

Aims:  To investigate the relationship between growth, heavy metal ions uptake and participation of the antioxidant enzymes superoxide dismutase (SOD) and catalase (CAT) in the protection of Apergillus niger B 77 against cadmium stress.
Methods and Results:  The stress response of the model fungal strain, under conditions of a wide range of Cd (II) ion concentrations, was investigated by determining the biomass formation, protein biosynthesis, SOD and CAT activities and heavy metal uptake in growing cells. Exposure to heavy metal ions induced an increase in protein content, heavy metal uptake and SOD activity, and a heavy decrease in CAT activity.
Conclusion:  The results obtained indicated that the tolerance of A. niger to Cd (II) was correlated with the heavy metal uptake, reactive oxygen species generation in the cells and the efficiency of antioxidative defence system.
Significance and Impact of the Study:  Evidence is provided for the possibility that oxidative stress plays a major role in the effect of Cd (II) ions on A. niger . These data could offer useful information when creating new strategies and methodological improvements for bioremediation with the participation of fungi.     

The cysteine-rich amino-terminal domain of ZntA, a Pb(II)/Zn(II)/Cd(II)-translocating ATPase from Escherichia coli, is not essential for its function.

Soft metal-translocating P1-type ATPases have a distinctive amino-terminal domain that contains one to six copies of the conserved metal-binding motif, GXXCXXC. ZntA from Escherichia coli, a Pb(II)-, Zn(II)-, and Cd(II)-transporting ATPase, has an approximately 120 residue amino-terminal domain with one copy of the GXXCXXC motif as well as four additional cysteine residues. The function of this domain was investigated by constructing a mutant of ZntA lacking the first approximately 100 residues. The mutant, DeltaN-ZntA, was able to confer resistance to Pb(II), Zn(II), and Cd(II) salts, in a manner similar to ZntA. The soft metal dependent ATP hydrolysis activity of purified DeltaN-ZntA was characterized. Purified DeltaN-ZntA and ZntA were both inactivated by oxidation. The K(m) for MgATP was unchanged for DeltaN-ZntA relative to ZntA. DeltaN-ZntA displayed the same metal ion specificity as ZntA. Thiolates increased the activities of both ZntA and DeltaN-ZntA. The V(max) values for DeltaN-ZntA were approximately 3-fold lower than for ZntA for all three metal ions. Thus, the amino-terminal domain is not essential for the function of ZntA or for conferring specificity toward particular soft metals. Its function may be to increase the overall catalytic rate by increasing the rate of metal ion binding to the transporter. Residues involved in the ATP-dependent soft metal ion-translocating mechanism as well as those responsible for recognition of specific metal ions must be part of the core structure of the P1-type ATPases.