Comparative 113Cd-n.m.r. studies on rabbit 113Cd7-, (Zn1,Cd6)- and partially metal-depleted 113Cd6-metallothionein-2a.

Rabbit 113Cd7-metallothionein-2a (MT) contains two metal-thiolate clusters of three (cluster B) and four (cluster A) metal ions. The 113Cd-n.m.r. spectrum of 113Cd6-MT, isolated from 113Cd7-MT upon treatment with EDTA, is similar to that of 113Cd7-MT, but the cluster B resonances are lower in intensity, suggesting its co-operative metal depletion. (Zn1,113Cd6)-MT, formed upon addition of the Zn(II) ions to 113Cd6-MT, shows 113Cd-n.m.r. features characteristic of cluster B populations containing both Cd(II) and Zn(II) ions. The overall intensity gain of the mixed cluster B resonances per Cd as to those in 113Cd6- and 113Cd7-MT suggests a stabilization effect of the bound Zn(II) ions upon the previously established intramolecular 113Cd exchange within this cluster.     

Trophic transfer of trace metals: Subcellular compartmentalisation in bivalve prey and comparative assimilation efficiencies of two invertebrate predators

We test the hypothesis that accumulated metal in prey that is trophically available to one predator is not necessarily equally trophically available to another predator feeding on the same prey, given the variability between invertebrate digestive systems. We provided two predators, the neogastropod mollusc Hinia reticulata and the palaemonid decapod crustacean Palaemonetes varians, with the digestive glands and adductor muscles of four bivalves radiolabelled with Zn, Cd or Ag. The bivalves (the mussel Mytilus edulis, the clam Ruditapes philippinarum, the scallop Aequipecten opercularis, the oyster Crassostrea gigas) have different metal accumulation patterns with differential dependence on soluble and insoluble detoxification, as confirmed by fractionation of the prey tissues. We found no consistent significant difference between the AE of the two predators for the three trace metals accumulated in the same prey tissues. There were no significant correlations for either predator between percentages of metal in soluble form (or soluble form with organelle-associated metal) and percentage AE for any of the three metals, allowing the conclusion that both predators are assimilating each metal from more than the soluble and organelle-associated metal fractions. For neither predator did an increased percentage of Zn in the form of metal rich granules (MRG) affect its Zn AE, but increases in the percentages of both Cd and Ag bound to MRG decreased the AE of the relevant metal in P. varians but not H. reticulata. Thus the Cd and Ag in some Cd-rich and Ag-rich granules in the bivalve tissues are not as trophically available to P. varians as they are to H. reticulata. This interspecific difference confirms that the neogastropod has the stronger digestive and assimilative powers involving Cd and Ag bound in prey than the palaemonid decapod.     

Zinc sequestration by earthworm (Annelida: Oligochaeta) chloragocytes. An in vivo investigation using fully quantitative electron probe X-ray micro-analysis

The elemental compositions of chloragosome "granules" in the earthworm Lumbricus rubellus living in non-polluted and heavily Zn-polluted soils were determined by fully quantitative electron probe X-ray microanalysis. P, Ca, S and Zn were the major elemental components of the chloragosomes. The in vivo accumulation of Zn by the chloragosomes was accompanied by diminished chloragosomal Ca concentrations. Zn was apparently bound by at least two ligand pools (Pool 1 = uncharacterised; Pool 2 = P-containing ligands, binding approximately 45% and 55% of the Zn, respectively) in the "control" chloragosomes. In Zn-contaminated chloragosomes, most (approximately 70%) was bound by P-containing ligand(s) but some (less than 1%) was also bound by S-containing ligands. It is suggested that the sequestration of Zn in chloragosomes results in the detoxification of the metal by accumulative immobilisation.     

A proposal for the metal geometry in yeast superoxide dismutase based on results from EXAFS spectroscopy

Extended x-ray absorption fine structure (EXAFS) spectra have been recorded at the Cu edge and Zn edge in native yeast superoxide dismutase and at the Cu edge and Cd edge in the yeast superoxide dismutase derivative, where Zn has been substituted with Cd. Two different metal ligand distances in the range 1.9-2.0 A and 2.3-2.4 are determined for the Cu and Zn metals. For Cd in the Zn site two different metal ligand distances about 2.2 A and 2.6 A, respectively, were found. The striking feature is the similarity between the amplitude and radii determined for both the Cu and Zn sites. The increased distances for Cd can be explained by the increased ionic radius of Cd relative to Cu and Zn. Based on these EXAFS results and other relevant knowledge about the metal geometries, we propose that histidine 61 (63) positioned between the Cu and Zn metals are in one subunit bound to Zn and in the other to Cu. This model explains the recently observed difference between the two metal sites in each subunit.     

Detection of two Zn-finger proteins ofXenopus laevis,TFIIIA, and p43, by probing western blots of ovary cytosol with65Zn2+,63Ni2+, or109Cd2+

Two Zn-finger proteins, TFIIIA (a constituent of 7S RNP particles) and p43 (a constituent of 42S RNP particles), were detected in ovary extracts of juvenile Xenopus laevis females by in vitro binding of radiolabeled divalent metals. Proteins fractionated by SDS-PAGE (sodium dodecylsulfate-polyacrylamide gel electrophoresis) were transferred by Western blotting onto nitrocellulose membranes, probed with 65Zn2+, 63Ni2+, or 109Cd2+, and visualized by autoradiography. Detection limits for TFIIIA were approx 0.07 micrograms/well by 109Cd(2+)-probing, 0.13 micrograms/well by 65Zn(2+)-probing, and 0.26 mu/well by 63Ni(2+)-probing. Protein p43 was more clearly visualized by probing with 63Ni2+ than with 65Zn2+ or 109Cd2+. After purified TFIIIA was cleaved with cyanogen bromide, 65Zn2+, 109Cd2+, and 63Ni2+ distinctly labeled the 22 kDa middle fragment; 65Zn2+ and 109Cd2+ also labeled the 11 kDa N-terminal fragment, but did not label the 13 kDa C-terminal fragment. These results are consistent with the notion that the radioligands were bound to finger-loop domains of TFIIIA, which occur in the middle and N-terminal fragments. Based on the abilities of nonradioactive metal ions to compete with 65Zn2+ for binding to TFIIIA on Western blots, the relative affinities of the metals for TFIIIA were ranked as follows: Zn2+ = Cu2+ greater than or equal to Hg2+ greater than Cd2+ greater than Co2+ greater than or equal to Ni2+. Even at a 1000-fold molar excess, Mn2+ did not compete with 65Zn2+ for binding to TFIIIA. Probing Western blots with the radiolabeled metal ions greatly facilitates the detection, isolation, and quantitation of TFIIIA and p43.     

Differential effects of AM fungal isolates on Medicago truncatula growth and metal uptake in a multimetallic (Cd, Zn, Pb) contaminated agricultural soil

Toxic metal accumulation in soils of agricultural interest is a serious problem needing more attention, and investigations on soil–plant metal transfer must be pursued to better understand the processes involved in metal uptake. Arbuscular mycorrhizal (AM) fungi are known to influence metal transfer in plants by increasing plant biomass and reducing metal toxicity to plants even if diverging results were reported. The effects of five AM fungi isolated from metal contaminated or non-contaminated soils on metal (Cd, Zn) uptake by plant and transfer to leachates was assessed with Medicago truncatula grown in a multimetallic contaminated agricultural soil. Fungi isolated from metal-contaminated soils were more effective to reduce shoot Cd concentration. Metal uptake capacity differed between AM fungi and depended on the origin of the isolate. Not only fungal tolerance and ability to reduce metal concentrations in plant but also interactions with rhizobacteria affected heavy metal transfer and plant growth. Indeed, thanks to association with nodulating rhizobacteria, one Glomus intraradices inoculum increased particularly plant biomass which allowed exporting twofold more Cd and Zn in shoots as compared to non-mycorrhizal treatment. Cd concentrations in leachates were variable among fungal treatments, but can be significantly influenced by AM inoculation. The differential strategies of AM fungal colonisation in metal stress conditions are also discussed.     

Metal selectivity of clusters in rabbit liver metallothionein.

In mammalian metallothioneins the metals are organized in two adamantane-type clusters with three and four metal ions which are tetrahedrally coordinated by thiolate ligands. The metal selectivity of the metal-thiolate clusters in rabbit liver metallothionein has been studied by offering two ions, i.e. Co(II)/Cd(II), Zn(II)/Cd(II) or Co(II)/Zn(II), to the metal-free protein. The heterogeneous metal complexes thus formed were characterized by electronic absorption, magnetic circular dichroism. 113Cd-NMR and EPR spectroscopy. In the case of Co/Cd-metallothionein, homometallic cluster occupation occurs, with the Cd(II) ions bound exclusively to the four-metal cluster. In contrast, heterometallic clusters were formed for both Zn/Cd- and Co/Zn-metallothionein. Based on evidence from corresponding inorganic structures of adamantane metal-thiolate cages, it is suggested that the major factor governing the cluster type is the protein structure perturbation due to the cluster volume variations. Thus, while metal thiolate affinities are important in the folding process, size-match selectivity is the dominant factor in the metal-loaded protein.     

Cooperative cluster formation in metallothionein

An ion-exchange chromatography procedure was used to resolve apometallothionein from the metallo- form in a study of metal-thiolate cluster formation. Chromatography of metallothionein reconstituted with Cd(II), Zn(II), or Cu(I) at neutral pH on carboxymethyl-cellulose led to removal of apoprotein from a solution without effect on recovery of the metalloprotein. Analysis of the effluent revealed apparent cooperative binding of these metal ions to the protein. Addition of 1-4 mol eq Cd(II) ions led to the recovery of metallothionein with around 4 mol eq Cd bound. The yield of this form increased with increasing starting metal ion equivalency. These results were obtained with two different ion-exchange resins. The cooperativity of binding was not total, but was initially confined to the carboxyl-terminal alpha domain. The results of metal and protein yields are inconsistent with random, noninteractive binding. Similar data were obtained with Zn(II) and Cu(I) ions although Cu(I) exhibited initial cooperative binding within the amino-terminal beta domain with over 5 mol eq Cu(I) bound.     

Bioavailability of sediment-bound Cd, Cr and Zn to the green mussel Perna viridis and the Manila clam Ruditapes philippinarum

We assessed the degree to which Cd, Cr and Zn bound with sediment were assimilated by the green mussel Perna viridis and the Manila clam Ruditapes philippinarum. The influences of the metal concentration in the sediment, the presence of phytoplankton, and the oxidation condition of the sediment on metal assimilation were examined. No major difference was found for metal assimilation efficiency (AE) in sediment with different metal concentrations, except for Cd in the green mussels, in which the AE increased by 1.7x when the Cd concentration in sediment was elevated to 15x the natural background level. The higher assimilation of Cd with increasing Cd load in ingested sediment may be due to the higher desorption of Cd in the acidic gut of the bivalves. Both mussels and clams assimilated metals at a higher efficiency from the diatom diet (Thalassiosira pseudonana) than from inorganic sediment particles. The presence of algal particles had little influence on metal assimilation from ingested sediment, and conversely, the presence of sedimentary particles had little effect on metal assimilation from ingested diatom (except for Cd in the mussels). In the mussels, AEs were higher from oxic sediment than from anoxic sediment by 3.1x for Cd, 2.0x for Cr, and 1.4x for Zn, and in the clams AEs were higher from oxic sediment by 2.8x for Cd, 2.0x for Cr, and 2.0x for Zn. Our study suggested that metals associated with anoxic sediment can be potentially available to marine bivalves, and that metal AEs determined for a single diet were probably not affected by the presence of other food particles.     

Domain-specificity of Cd2+ and Zn2+ binding to rabbit liver metallothionein 2. Metal ion mobility in the formation of Cd4-metallothionein alpha-fragment.

The yield of the alpha-fragment of rabbit liver metallothionein 2 was used to test the domain-specificity and mobility of Cd2+ and Zn2+ when bound to metallothionein. Increasing molar ratios of Cd2+ were added to either Zn7-metallothionein or the metal-ion-free apo-metallothionein. The enzyme subtilisin was used to digest those parts of the peptide chain that were not bound to Cd2+. Analysis of the digestion products was carried out by separation by polyacrylamide-gel electrophoresis. The chelation agent EDTA was used as a competitive chelator. It was found that the presence of excess EDTA greatly enhances the formation of the Cd4-metallothionein alpha-fragment, and catalyses the complete digestion of all other the metal-ion-containing peptides, so that even Cd7-metallothionein, formed when 7 molar equivalents of Cd2+ are added to Zn7-metallothionein, is digested to the alpha-fragment. These results suggest that the Cd2+ bound in the beta-sites is very labile, much more labile than the kinetics of the off-reaction would suggest. The observation of significant amounts of alpha-fragment on the gels, even when the stoichiometry of the metal ions initially present in the protein should not have resulted in much concentration of Cd4-alpha-fragment clusters, indicates that as the digestion proceeds the metal ions move to sites that form complete clusters and therefore selectively protect that part of the peptide chain from digestion. We also find that rabbit Cd4-metallothionein 2 alpha-fragment stains near to the top of the gel, in complete contrast with the location of rat Cd4-metallothionein 2 alpha-fragment. This difference in the mobilities suggests that the alpha-fragment prepared from rabbit metallothionein 2 is much less negatively charged than the analogous protein fragment prepared from rat liver metallothionein 2.     

Ferritin—A general metal detoxicant

Binding of nonferrous metal ions to ferritin was compared to that of the phosphate-free or phosphate containing synthetic iron cores. The Scatchard plots for the synthetic cores reveal a high affinity site for Cd, Zn, Be, and Al, with K_D in the range 10^?5–10^?7 M. Preloading the cores with phosphate increased the number of metal ions bound without altering the K_D. The metal ions with smaller ionic radii (Be, Al) were bound in larger numbers than those with larger ionic radii (Cd, Zn). Ferritin isolated from soybean (Glycina max), horse spleen, and rat liver bound the metal ions in amounts larger than predicted from their iron core. Whereas the iron cores and their nonferrous metal ion complexes were insoluble, those in the protein shell remained in solution. Thus apoferritin precipitated with lower concentrations of aluminum than did holoferritin. Also, Al bound to apoferritin reduced the rate of iron loading into the protein.     

Binding of heparin to human high molecular weight kininogen

The binding of heparin to high molecular weight kininogen (H-kininogen) was analyzed by the effect of kininogen in decreasing the heparin-induced enhancement of the rate of inactivation of thrombin by antithrombin. The conditions were arranged so that the heparin-catalyzed antithrombin-thrombin reaction, monitored in the presence of the reversible thrombin inhibitor p-aminobenzamidine, followed pseudo-first-order kinetics and the observed rate constant (kappa obsd) varied linearly with the heparin concentration. In the absence of metal ions, H-kininogen minimally affected kappa obsd, measured at a constant concentration of heparin with high affinity for antithrombin (30 nM), at I = 0.15, pH 7.4 and 25 degrees C. However, at a saturating concentration of Zn2+ (10 microM), kappa obsd was reduced to 50% at approximately 20 nM H-kininogen and to that of the uncatalyzed reaction at greater than or equal to approximately 0.2 microM H-kininogen. Conversely, at a saturating concentration of H-kininogen (0.5 microM), kappa obsd was decreased to 50% at approximately 0.6 microM Zn2+ and to the kappa obsd of the uncatalyzed reaction at greater than or equal to 10 microM Zn2+. Other metal ions were effective in the order Zn2+ approximately Ni2+ greater than Cu2+ approximately Co2+ approximately Cd2+. The single-chain and two-chain forms of H-kininogen and the H-kininogen light chain reduced the heparin enhancement in the presence of Zn2+ to the same extent, whereas low molecular weight kininogen had no influence.(ABSTRACT TRUNCATED AT 250 WORDS)     

Metal thiolate coordination in the E7 proteins of human papilloma virus 16 and cottontail rabbit papilloma virus as expressed in Escherichia coli.

The oncogenic E7 proteins of human papilloma virus (HPV 16) and of cottontail rabbit papilloma virus (CRPV) have been purified from an expression system in Escherichia coli. The proteins as purified from E. coli contain one tightly bound Zn(II) ion per molecule. The metal site shows facile exchange with either Cd(II) or Cu(I). The HPV 16 E7 maximally bound one Cd(II) or two Cu(I) ions, while the CRPV E7 bound two Cd(II) or three Cu(I) ions. The Cd(II) and Cu(I) E7 molecules exhibited optical transitions in the ultraviolet suggestive of metal:thiolate coordination. E7 proteins from HPV 16 and CRPV contain 7 and 8 cysteines/molecule, respectively. Reaction of the E7 proteins with the sulfhydryl reagent, dithiodipyridine, revealed that all the cysteinyl sulfurs are present in the reduced thiol state. Cu(I)-E7 molecules are luminescent with maximal emission at 570 nm. The observed emission at room temperature is indicative of metal coordination within a compact protein environment shielded from solvent interactions. The emission maxima occurs at the same wavelength (570 nm) as Cu(I)-cysteinyl sulfur clusters in Cu(I)-metallothioneins. The single Zn(II) atom in each protein can be removed from E7 in the presence of EDTA. The resulting apoE7 molecules remain soluble and can be partially reconstituted with Cd(II) to regain the ultraviolet charge transfer transitions.     

Selective, quantitative detection of cadmium and/or zinc by use of BTAN (2-aminobenzothiazolylazo-beta-naphthol)

BTAN (Sumi Y et al. (1982) Histochemistry 73:481) was investigated as a histochemical Cd/Zn chelator. Cd-BTAN exhibits a main peak about 635 nm, while Zn-BTAN exhibits a main peak about 644 nm. The isobestic wavelength for Cd-BTAN and Zn-BTAN is 638 nm. The microscopical detection limit for Cd is about 25 amol/microns 2, and for Zn about 5 amol/microns 2. The relation between metal and bound chelator is fairly linear at a BTAN concentration more than 10-fold the metal concentration. Histochemical localization was fair to good, with a crystal size of up to 0.2-0.3 micron. The chelate was unaffected by hydrophilic and largely also by hydrophobic mounting media. The original staining procedure proved erratic and was modified. Posttreatment with oxine to selectively demonstrate Cd in the presence of Zn (Sumi Y et al. 1982) seriously reduced the staining intensity. Post-treatment for 8-15 min with HCl, 0.5 mol/l, in 50% ethanol removed Cd-BTAN completely with little reduction of Zn staining intensity, even from sites with 5x as much Cd as Zn. It is concluded that BTAN permits direct quantitative detection of (Zn + Cd). Provided certain precautions are taken quantitative detection of Zn and quantitation of Cd in mixed Zn/Cd sites is possible by microphotometry of the stained section before and after differentiation for 8-15 min with the HCl/50% ethanol medium.     

Metal pollution recorded in extinctDreissena polymorpha communities, Lake Breitling, Havel Lakes system, Germany: a laser ablation inductively coupled plasma mass spectrometry study

Shells of probable former living communities ofDreissena polymorpha were found within sediments of the shallow polytrophic to hypertrophic hard water Lake Breitling (Havel-Lake system, Germany). Corresponding sediments have been deposited between approximately 1940 and 1970 and reflect increasing eutrophication and heavy metal pollution of the Lake during this period (Schettler, 1992). Single shells from various sediment depths were analysed by laser ablation inductively coupled plasma mass spectrometry (LA-ICP-MS) along a line on the outer part of the shell. The response of these freshwater mussels to increasing heavy metal pollution is clearly reflected in the distribution of Pb, Cu, Cd and Zn within their valves. In general, Cd, Cu, Pb and Zn contents are lower, and the distribution more even, in the outer parts of the deepest (oldest) shells compared to shells from higher in the cored sediments. Notably higher contents of Cu, Pb and Zn were recorded from the central (umbonal) part of the more recent shells, but this behaviour is not recorded for Cd. Metabolic changes brought on by worsening environmental conditions are proposed to explain this phenomena. Acidity produced during anaerobic metabolism can be neutralised by dissolution of the carbonate part of the shell. Copper, Zn and Pb, which show an affinity for the organic component of the shell, may thus accumulate by repeated dissolution and reprecipitation of the shell during the lifetime of an individual organism. Cadmium, which is bound mainly in the aragonite of the shells, is released during the dissolution of carbonate and is not concentrated in the umbonal area of the shell.     

Raman spectroscopic study of the effects of Ca2+, Mg2+, Zn2+, and Cd2+ ions on calf thymus DNA: binding sites and conformational changes

The interaction of Mg2+, Ca2+, Zn2+, and Cd2+ with calf thymus DNA has been investigated by Raman spectroscopy. These spectra reveal that all of these ions, and particularly Zn2+, bind to phosphate groups of DNA, causing a slight structural change in the polynucleotide at very small metal: DNA (P) concentration ratio (ca. 1:30). This results in increased base-stacking interactions, with negligible change of the B conformation of DNA. Contrary to Zn2+ and Cd2+, which interact extensively with the nucleic bases (particularly at the N7 position of guanine), the alkaline-earth metal ions are bound almost exclusively to the phosphate groups. The affinity of both the Zn2+ and Cd2+ ions for G.C base pairs is comparable, but the Cd2+ ions interact more extensively with A.T pairs than Zn2+ ions. Interstrand cross-linking through the N3 atom of cytosine is suggested in the presence of Zn2+, but not Cd2+.     

Root foraging for zinc and cadmium requirement in the Zn/Cd hyperaccumulator plant Sedum alfredii

Positive root response to metals may enhance metal accumulation for greater requirement in hyperaccumulators. The effects of spatially heterogeneous Zn/Cd addition on root allocation, metal accumulation, and growth of the Zn/Cd hyperaccumulator Sedum alfredii were assessed in a pot experiment. Young shoots of S. alfredii were grown with or without supplied Zn/Cd. Two concentrations were used of each metal, and each metal concentration had one homogeneous and two heterogeneous treatments. Growth increased by 1.6–3.2 times with the increasing overall dose of Zn/Cd addition, and shoot biomass was positively correlated with shoot Zn/Cd concentration (P?<?0.001). In all heterogeneous treatments, the plants consistently allocated approximately 90% of root biomass to the metal-enriched patches, and shoot Zn/Cd contents were greater than or similar to those in the homogeneous treatment at each metal concentration. Plants in the control treatment showed symptoms of Zn deficiency, although their shoots had Zn concentrations 100-fold higher than the critical deficiency value for most plants. We conclude that S. alfredii has evolved root foraging mechanisms associated with its greater requirements for Zn/Cd. These results could have important implications both for phytoremediation and for investigation of positive role of Cd in higher plants.     

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.     

Preference of Cd(II) and Zn(II) for the two metal sites in Bacillus cereus beta-lactamase II: A perturbed angular correlation of gamma-rays spectroscopic study

Cd-substituted forms of the Bacillus cereus metallo-beta-lactamases (BCII) were studied by perturbed angular correlation of gamma-rays (PAC) spectroscopy. At very low [Cd]:[apo-beta-lactamase] ratios, two nuclear quadrupole interactions (NQI) were detected. For [Cd]:[apo-beta-lactamase] ratios between 0.8 and 3.0, two new NQIs appear, and the spectra show that up to 2 cadmium ions can be bound per molecule of apoenzyme. These results show the existence of two interacting Cd-binding sites in BCII. The relative populations of the two NQIs found at low [Cd]:[apo-beta-lactamase] ratios yielded a 1:3 ratio for the microscopic dissociation constants of the two different metal sites (when only one cadmium ion is bound). X-ray diffraction data at pH 7.5 demonstrate that also for Zn(II) two binding sites exist, which may be bridged by a solvent molecule. The measured NQIs could be assigned to the site with three histidines as metal ligands (three-His site) and to the site with histidine, cysteine, and aspartic acid as metal ligands (Cys site), respectively, by PAC measurements on the Cys168Ala mutant enzyme. This assignment shows that cadmium ions preferentially bind to the Cys site. This is in contrast to the preference of Zn(II) in the hybrid Zn(II)Cd(II) enzyme, where an analysis of the corresponding PAC spectrum showed that Cd(II) occupied the Cys site, whereby Zn(II) occupied the site with three histidines. The difference between Zn(II) and Cd(II) in affinity for the two sites is combined with the kinetics of hydrolysis of nitrocefin for different metal ion substitutions (Zn(2)E, ZnE, Cd(2)E, CdE, and ZnCdE) to study the function of the two metal ion binding sites.     

Products of metal exchange reactions of metallothionein

Hepatic metallothionein (MT) isolated from Cd-exposed animals always contains Zn (2-3 mol/mol of protein) in addition to Cd (4-5 mol/mol of protein), and the two metals are distributed in a nonuniform, but reproducible, manner among the seven binding sites of the protein's two metal-thiolate clusters. Different methodologies of preparing rabbit liver Cd, Zn-MT in vitro were investigated to provide insight into why such a distinct mixture of mixed-metal clusters is produced in vivo and by what mechanism they form. 113Cd NMR spectra of the products of stepwise displacement of Zn2+ from Zn7-MT by 113Cd2+ show that Cd binding to the clusters is not cooperative (i.e., clusters containing exclusively Cd are not formed in preference to mixed-metal Cd, Zn clusters), there is no selective occupancy of one cluster before the other, and many clusters are produced with a nonnative metal distribution indicating that this pathway is probably not followed in vivo. In contrast, the surprising discovery was made that the native cluster compositions and their relative concentrations could be reproduced exactly by simply mixing together the appropriate amounts of Cd7-MT and Zn7-MT and allowing intermolecular metal exchange to occur. This heretofore unknown metal interchange reaction occurs readily, and the driving force appears to be the relative thermodynamic instability of three-metal clusters containing Cd. With this new insight into how Cd,Zn-MT is likely to be formed in vivo we are able for the first time to postulate rational explanations for previous observations regarding the response of hepatic Zn and metallothionein levels to Cd administration.