Toxic effects of mercury(II), cadmium(II) and lead(II) porphyrins on Trypanosoma brucei brucei growth

The effects of free mercury(II), cadmium(II) and lead(II) ions and their metalloporphyrin-derivatives on Trypanosoma brucei brucei growth in culture were studied. All experiments were conducted in the dark. IC(50) values on growth obtained in 24-h time-course experiments were 1.5 x 10(-7), 2.4 x 10(-6), 4.4 x 10(-6) and 2.6 x 10(-5) M for mercury(II) porphyrin, cadmium(II) porphyrin, lead(II) porphyrin and free base porphyrin, respectively. While the IC50 values for Hg2+, Cd2+ and Pb2+ were 3.6 x 10(-6), 1.5 x 10(-5) and 1.6 x 10(-5) M, respectively. These results clearly indicate that the toxicity of the metalloporphyrin complexes of mercury(II), cadmium(II) and lead(II) to T. b. brucei parasites was much higher compared to their free metal ions and free base porphyrin at low concentrations. It was also observed after 8 h incubation that the metalloporphyrins were effective in inhibiting the division of the parasites at concentrations >1.25 x 10(-7) M for mercury(II) porphyrin, concentrations >1.2 x 10(-6) M for cadmium(II) and lead(II) porphyrins and at concentrations >3.6 x 10(-6) M for Hg2+ ion. These observations were not detected in samples treated with the free metal ions and the free base porphyrin at the same concentrations. Interestingly, trypanosomes treated with metalloporphyrin complexes displayed different morphological features from those cells treated with free base porphyrin or metal ions. The chemotherapeutic potential of the metalloporphyrins of H2TMPyP for treatment of African trypanosomiasis is discussed.     

Speciation of ternary complexes of lead(II), cadmium(II) and mercury(II) with L-dopa and phenanthroline in propanediol-water mixtures

Abstract

The formation constants of ternary complexes of title systems have been determined pH-metrically in biologically relevant conditions at an ionic strength of 0.16 mol dm^-3 and 303 K. The overall stability constants have been evaluated using MINIQUAD75 computer program. The complexation equilibria have been derived on the basis of species distribution diagram. In the present study L-Dopa and 1, 10-phenanthroline are found to be compatible ligands, proving greater stability of ternary complexes as compared to binary ones. The trend in variation of stability constants with change in dielectric constant of medium is explained on the basis of electrostatic and non-electrostatic forces. Distributions of the species with pH at different compositions of propanediol-water mixtures are also presented. The factors responsible for the compatibility of both the ligands have also been discussed.     

Biosorption of lead(II), cadmium(II), copper(II) and nickel(II) by anaerobic granular biomass

Biosorption is potentially an attractive technology for treatment of wastewater for retaining heavy metals from dilute solutions. This study investigated the feasibility of anaerobic granules as a novel type of biosorbent, for lead, copper, cadmium, and nickel removal from aqueous solutions. Anaerobic sludge supplied from a wastewater treatment plant in the province of Quebec was used. Anaerobic granules are microbial aggregates with a strong, compact and porous structure and excellent settling ability. After treatment of the biomass with Ca ions, the cation exchange capacity of the biomass was approximately 111 meq/100 g of biomass dry weight which is comparable to the metal binding capacities of commercial ion exchange resins. This work investigated the equilibrium, batch dynamics for the biosorption process. Binding capacity experiments using viable biomass revealed a higher value than those for nonviable biomass. Binding capacity experiments using non-viable biomass treated with Ca revealed a high value of metals uptake. The solution initial pH value affected metal sorption. Over the pH range of 4.0-5.5, pH-related effects were not significant. Meanwhile, at lower pH values the uptake capacity decreased. Time dependency experiments for the metal ions uptake showed that adsorption equilibrium was reached almost 30 min after metal addition. It was found that the q(max) for Pb2+, Cd2+, Cu2+, and Ni2+ ions, were 255, 60, 55, and 26 mg/g respectively (1.23, 0.53, 0.87, and 0.44 mmol/g respectively). The data pertaining to the sorption dependence upon metal ion concentration could be fitted to a Langmiur isotherm model. Based on the results, the anaerobic granules treated with Ca appear to be a promising biosorbent for removal of heavy metals from wastewater due to its optimal uptake of heavy metals, its particulate shape, compact porous structure, excellent settling ability, and its high mechanical strength.     

Zinc(II), cadmium(II) and mercury(II) complexes of the vitamin B1 antagonist oxythiamine

The reaction of oxythiamine chloride hydrochloride (HOxTCl x HCl) with ZnCl2, CdCl2 and HgCl2 in ethanol yielded the complexes [ZnCl3(HOxT)], [CdCl3(HOxT)] and [HgCl3(HOxT)]. In water, the reaction with CdCl2 afforded [CdCl2(OxT)], but reaction with ZnCl2 or HgCl2 yielded unidentified products. The four new complexes were characterized by mass spectrometry and IR spectroscopy in the solid state and by 1H, 13C and 15N nuclear magnetic resonance (NMR) spectroscopy in hexadeuterated dimethylsulfoxide (DMSO-d6), and three were also studied by X-ray diffractometry. In [ZnCl3(HOxT)] and [HgCl3(HOxT)] the oxythiamine ligand is bound to the metal via N(1') and adopts the V conformation exhibited by thiamine in biological contexts. The infrared (IR) spectrum of [CdCl3(HOxT)] suggests a similar coordination mode. In [CdCl2(OxT)] each OxT zwitterion coordinates to one Cd(II) ion via its N(1') atom and to another via its N(3') and O atoms, giving rise to a polymeric chain along the x-axis. The coordination number of the metal is made up to six by Cdc...Cl interactions, two of which link the polymeric chains in pairs. This seems to be the first metal complex containing the oxythiamine ligand as a zwitterion, with the N(3')-H/O(4'alpha)-H group deprotonated. Neither HOxTCl nor its zinc(II) complex showed any significant activity in vitro against HeLa cells.     

Biosorption of cadmium(II), lead (II) and copper(II) with the filamentous fungus Phanerochaete chrysosporium

The biosorption from artificial wastewaters of heavy metals (Cd(II), Pb(II) and Cu(II)) onto the dry fungal biomass of Phanerochaete chryosporium was studied in the concentration range of 5-500 mg l(-1). The maximum absorption of different heavy metal ions on the fungal biomass was obtained at pH 6.0 and the biosorption equilibrium was established after about 6 h. The experimental biosorption data for Cd(II), Pb(II) and Cu(II) ions were in good agreement with those calculated by the Langmuir model.     

Electroanalytical investigation on the interaction between 6-mercaptopurine and zinc(II), lead(II), and cadmium(II) ions in nonaqueous solvents

Different electroanalytical techniques have been employed in the study of the interaction between 6-mercaptopurine and zinc(II), lead(II), and cadmium(II) ions in ethanol, dimethylformamide, and dimethylsulfoxide. The stoichiometry of the formed complexes was determined as well as their instability constants. The kinetic parameters of the electrode processes have been also evaluated.     

A preparative study of some coronands and their complexation of silver(I), zinc(II), cadmium(II) and lead(II)

A study of the complexation of heavy metal ions by the coronands 3,12,20,29-tetraoxa-35,36-diazapentacyclo[29.3.1.1.^14,18.0^5,10.0^22,27]-hexatriaconta-1(35),5(10),6,8,14,16,18(36),22(27),23,25,31,33-dodecaene (1); 2,3,11,12-bis (4^′-methylbenzo)-1,4,10,13-tetrathia-7,16-dioxacyclo-octadeca-2,11-diene (2); 7,16-diaza-1,4,10,13-tetraoxa-2,3,11,12-dibenzocyclooctadeca-2,11-diene (3); 2-[19-(2-hydroxy-2-phenylethyl)-7,8,9,10, 18,19,20,21-octahydro-6H,17H-dibenzo[b,k][1,4,10,13,7,16]tetraoxadiazacyclooctadecin-8-yl]-1-phenyl-1-ethanol (4); 1,4,10,13-tetraoxa-7,16-diazacyclo-octadecane (5); and 2-[16-(2-hydroxy-2-phenylethyl)-1,4,10,13-tetraoxa-7,16-diazacyclo-octadecanyl]-1-phenyl-1-ethanol (6) is described. Coronands 1 and 3 were prepared by literature methods, improved methods were used to prepare 2, and 4 and 6 were prepared from 3 and 5 (obtained commercially), respectively. Potentiometric studies in N,N-dimethylformamide yielded (logK/dm³ mol⁻¹)=5.50, 6.49, 9.42 and 7.52 for [Ag · 1]⁺, [Ag · 2]⁺, [Ag · 5]⁺ and [Ag · 6]⁺, respectively; <2, <2, 4.30 and <2 for [Zn · 1]²⁺, [Zn · 2]²⁺, [Zn · 5]²⁺ and [Zn · 6]²⁺, respectively, <2, <2, 5.92 and >7.52 for [Cd · 1]²⁺, [Cd · 2]²⁺, [Cd · 5]²⁺, and [Cd · 6]²⁺, respectively, and 2.62, 2.38, 6.71 and >7.52 for [Pb · 1]²⁺, [Pb · 2]²⁺, [Pb · 5]²⁺, and [Pb · 6]²⁺, respectively. ESI-MS studies of the interactions of 1-6 with Ag⁺, Zn²⁺, Cd²⁺ and Pb²⁺ are also reported.     

Silver(I), mercury(II), cadmium(II), and zinc(II) target exposed enzymic iron-sulfur clusters when they toxify Escherichia coli

The toxicity of soft metals is of broad interest to microbiologists, both because such metals influence the community structures in natural environments and because several metals are used as antimicrobial agents. Their potency roughly parallels their thiophilicity, suggesting that their primary biological targets are likely to be enzymes that contain key sulfhydryl moieties. A recent study determined that copper poisons Escherichia coli in part by attacking the exposed [4Fe-4S] clusters of dehydratases. The present investigation sought to test whether other soft metals also target these enzymes. In vitro experiments revealed that low-micromolar concentrations of Ag(I) and Hg(II) directly inactivated purified fumarase A, a member of the dehydratase family. The enzyme was also poisoned by higher levels of Cd(II) and Zn(II), but it was unaffected by even millimolar concentrations of Mn(II), Co(II), Ni(II), and Pb(II). Electron paramagnetic resonance analysis and measurements of released iron confirmed that damage was associated with destruction of the [4Fe-4S] cluster, and indeed, the reconstruction of the cluster fully restored activity. Growth studies were then performed to test whether dehydratase damage might underlie toxicity in vivo. Barely toxic doses of Ag(I), Hg(II), Cd(II), and Zn(II) inactivated all tested members of the [4Fe-4S] dehydratase family. Again, activity was recovered when the clusters were rebuilt. The metals did not diminish the activities of other sampled enzymes, including NADH dehydrogenase I, an iron-sulfur protein whose clusters are shielded by polypeptide. Thus, the data indicate that dehydratases are damaged by the concentrations of metals that initiate bacteriostasis.     

DNA conformational changes and cleavage by ruthenium(II) nitrofurylsemicarbazone complexes

Metal complexes that establish interactions with DNA are being studied not only because of their potential use as therapeutic agents but also as tools for biochemistry and molecular biology. Searching for drugs with anti-trypanosome activity, we previously synthesized a series of ruthenium mixed ligand dimethyl sulfoxide complexes of the type [Ru(II)Cl(2)(DMSO)(2)L], where L is 5-nitrofurylsemicarbazone derivatives and DMSO is dimethyl sulfoxide. Though they present the ability to bind DNA, no activity against parasites in cell culture was observed. Considering their potential application as molecular tools we further analyzed the interactions with DNA through an electrophoretic approach. Non covalent withdrawal of superhelicity and a rapid nicking activity upon covalent interaction was observed. Inhibition of both effects was observed in the presence of distamycin suggesting the involvement of the DNA minor groove in the interaction with the nitrofurylsemicarbazone ruthenium complexes. In addition cleavage inhibition by dimethyl sulfoxide suggests an oxidative mechanism of action.     

Iron(III) reduction by D-galacturonic acid. Part II. Influence of uranyl(VI), lead(II), nickel(II), and cadmium(II) complexes formation

As a part of our study on iron reduction-mobilization in biological systems, in particular at root-soil interface, the effect of the addition of different metal ions to the iron(III)-D-galacturonic acid system has been investigated. The ions which are found to form particularly stable complexes with the galacturonate ligand strongly increase the yield of the reduction of iron(III) to iron(II). These findings are in agreement with the capability of some metal ions to form stable complexes through interaction both with the carboxylate group and with the ring oxygen atom of the sugar molecule, inducing opening of the ring and formation of a free aldehydic group. The importance of these processes in availability of iron to plant roots is emphasized.     

Interaction of water-soluble Cu(II), Ni(II), and Co(III) porphyrins with polynucleotides

The interaction of the Cu(II), Ni(II) and Co(III) complexes of the following six water-soluble cationic porphyrins with calf thymus DNA, poly(dG-dC)2 and poly(dA-dT)2 was studied by UV-visible and resonance Raman spectroscopy: tetrakis(2-N-) and (3-N-methylpyridyl) porphyrin (1, 2); monophenyl-tris(4-N-methylpyridyl)porphyrin (4); cis- and trans-diphenyl-bis (4-N-methylpyridyl)porphyrin (5, 6). The binding to nucleic acids was compared with that of tetrakis(4-N-methylpyridyl)porphyrin (3). If the N(+)-CH3 group is moved from the para (3) to the meta position (2), binding of the free porphyrin as well as that of the metal complexes is only gradually modified; thus, the square-planar Cu- and Ni-2 are intercalated at the G-C site whereas Co-2 is groove-bound at A-T. Additionally, Ni-2 is probably also intercalated at the A-T site. When the N(+)-CH3 group is located at ortho position (1), the high rotation barrier of the 2-N-methylpyridyl group prevents intercalation of Cu- and Ni-1, resulting in weak outside binding. At ionic strength mu = 0.2, there is no evidence of significant interaction of Co-1 with any of the polynucleotides. When the charged N-methylpyridyl groups in 3 are subsequently replaced by phenyl groups (4, 5/6), the tendency of the Cu(II) and Ni(II) complexes to bind to the outside of the helix or to intercalate only partially increases at the expense of full intercalation. The coulombic attraction remains strong, no significant differences can be detected between 3, 4, 5, and 6. Ni-4 binds to poly(dA-dT)2 in the same complicated manner as Ni-3. The outside-binding in Co-4, -5 and -6 differs slightly from that in Co-2 and Co-3.     

Metal ion interactions with Limulus polyphemus and Callinectes sapidus hemocyanins: stoichiometry and structural and functional consequences of calcium(II), cadmium(II), zinc(II), and mercury(II) binding

Hemocyanins are oligomeric metalloproteins containing binuclear copper centers that reversibly combine with oxygen molecules. The structural stability and functional properties of these proteins are modified by divalent cations. Equilibrium dialysis was used to study the reversible interaction of Callinectes sapidus and Limulus polyphemus hemocyanins with the divalent cations calcium, cadmium, zinc, copper, and mercury. The number of binding sites and association constants for each cation were obtained from an analysis of the binding data by a nonlinear least-squares minimization procedure. Spectral analysis showed Limulus hemocyanin to possess two mercury-reactive sulfhydryl groups per subunit (Kassoc = 2.02 X 10(45) M-1). Callinectes hemocyanin contains only one such group (Kassoc = 2.29 X 10(34) M-1). Cadmium and zinc are shown to substitute for calcium ions. Oxygen binding studies with Limulus hemocyanin showed that all five divalent metal ions increase its oxygen affinity. Calcium ions increase cooperativity of oxygen binding, while heavy-metal ions have an opposite effect. Binding of two mercuric ions per Limulus hemocyanin subunit irreversibly fixes the 48 subunit aggregate in a high-affinity noncooperative conformational state. These results offer a striking contrast to the functional consequences of heavy-metal ion interactions with Callinectes hemocyanin [Brouwer, M., Bonaventura, C., & Bonaventura, J. (1982) Biochemistry 21, 2529-2538]. The functional alterations associated with metal ion interactions are discussed within the context of an extension of the two-state model for allosteric transitions of Monod et al. [Monod, J., Wyman, J., & Changeux, J.P. (1965) J. Mol. Biol. 12, 88-118]. Incubation of Limulus oxy- or deoxyhemocyanin with mercuric chloride results in the conversion of 60% of the binuclear copper sites to stable half-apo sites. The remaining active sites are stable with respect to mercury-induced copper displacement when oxygen is bridging both coppers. In the absence of oxygen these sites will eventually lose both copper atoms. Under the same conditions 50% of the binuclear copper sites of Callinectes deoxyhemocyanin are converted to half-apo sites. In this case oxygen completely protects against copper displacement [Brouwer, M., Bonaventura, C., & Bonaventura, J. (1982) Biochemistry 21, 2529-2538]. The binuclear copper center of Busycon carica is not affected at all, demonstrating profound differences between the active sites of hemocyanins of a chelicerate arthropod (Limulus), a crustacean arthropod (Callinectes), and a gastropod mollusc (Busycon).     

DNA and nucleotide-induced conformational changes in the Escherichia coli Rep and helicase II (UvrD) proteins

The domain structures of the Escherichia coli Rep and Helicase II proteins and their ligand-dependent conformational changes have been examined by monitoring the sensitivity of these helicases to proteolysis by trypsin and chymotrypsin. Limited treatment of unliganded Rep protein (73 kDa) with trypsin results in cleavage at a single site in its carboxyl-terminal region, producing a 68-kDa polypeptide which is stabilized in the presence of ATP, ADP, or adenosine 5'-O-thiotriphosphate) (ATP gamma S). The purified 68-kDa Rep tryptic polypeptide retains single-stranded (ss) DNA binding, DNA unwinding (helicase), and full ATPase activities. When bound to ssDNA, the Rep protein can be cleaved by trypsin at an additional site in its carboxyl-terminal region, producing a 58-kDa polypeptide that also retains ssDNA binding and ATPase activities. This 58-kDa Rep tryptic polypeptide can also be produced by further tryptic treatment of the 68-kDa Rep tryptic polypeptide when the latter is bound to ssDNA. This 58-kDa polypeptide displays a lower affinity for ssDNA indicating that the 10-kDa carboxyl-terminal peptide facilitates Rep protein binding to ssDNA. The 58-kDa Rep tryptic polypeptide is also stabilized in the presence of nucleotides. Based on these and previous studies that showed that the 68-kDa Rep tryptic polypeptide cannot support DNA replication in a system that is dependent upon the phi X174 cis-A protein (Arai, N. & Kornberg, A. (1981) J. Biol. Chem. 256, 5294-5298), we conclude that the carboxyl-terminal end (approximately 5 kDa) of the Rep protein is not required for its helicase or ATPase activities. However, we suggest that this region of the Rep protein is important for its interactions with the phi X174 cis-A protein. Limited treatment of unliganded Helicase II protein (82 kDa) with chymotrypsin results in cleavage after Tyr254, producing a 29-kDa amino-terminal polypeptide and a 53-kDa carboxyl-terminal polypeptide, which remain associated under nondenaturing conditions. This chymotrypsin cleavage reduces the ssDNA binding activity and eliminates the ssDNA-dependent ATPase and helicase activities of the Helicase II protein. The binding of ATP, ADP, ATP gamma S, and/or DNA to Helicase II protein results in protection of this site (Tyr254) from cleavage by chymotrypsin. Limited treatment of Helicase II protein with trypsin results in cleavage near its carboxyl-terminal end producing two polypeptides with apparent Mr = 72,000, in a manner similar to that observed with the Rep protein; these polypeptides are also stabilized by binding ATP or single-stranded DNA.(ABSTRACT TRUNCATED AT 400 WORDS)     

Characterization and crystal structure of cadmium(II) halide complexes with amino acids and their derivatives: VII. Crystal structures of aquadibromo(3-aminopropanoic acid)cadmium(II), dichloro(4-aminobutanoic acid)cadmium(II), diaquabis(aminohexanoic acid)cadmium(II) tetrachlorocadmium(II), and dibromo(azetidine-3-carboxylic acid)cadmium(II)

Seven cadmium complexes: [CdX2(Hapro)(H2O)n] (X: Cl(1), Br(2)), [CdX2(Hgaba)] (X: Cl(3), Br(4)), [Cd(Hahex)2(H2O)2][CdCl4] (5), and [CdX2(Haze-3)](H2O)n (X: Cl(6), Br(7)) have been prepared and investigated by means of IR and FT Raman spectra. The crystal and molecular structures of 2, 3, 5 and 7 were determined by a single-crystal X-ray diffraction method. In complex 2, the cadmium atom is in a distorted octahedral geometry, ligated by two carboxyl oxygen atoms of Hapro, a water molecule, and three bromine atoms; one is terminal and each of the other two is bridging two cadmium atoms to make a polymer. The structure of 3 consists of one-dimensional polymers bridged by two chlorine atoms and a carboxyl group. The carboxyl oxygen atoms of Hgaba coordinate forkedly to two cadmium atoms. The cadmium atom of [Cd(Hahex)2(H2O)2]2+ in complex 5 is in a distorted octahedral geometry, ligated by four carboxyl oxygen atoms of two molecules of Hahex and by two water molecules. [Cd(Hahex)2(H2O)2]2+ exists between two layers which are formed of infinite [CdCl4]2- chains. The carboxyl oxygen atoms of Hahex coordinate to the same cadmium atom. In complex 7, the cadmium atom is ligated by two carboxyl oxygen atoms and four bridging bromine atoms to make a polymer.     

Complexation of thiomalic acid with mercury (II) and lead (II) under physiological conditions

The complex formation of thiomalic acid (H3L) with Hg(II) and Pb(II) was investigated under physiological conditions of 37 degrees C and 0.15 mol dm-3 NaCl by potentiometric titrations using glass electrodes. From the analysis of the emf data in the two systems by use of computer program MIQUV it was concluded that the species formed in the two systems are [HgH4L2], [HgH3L]-, [HgH2L2]2-, [HgHL2]3-, [HgHL], [HgL]-, [HgL2]4-, [Hg(OH)L]2-, [Hg(OH)L2]5-, [PbH2L2]2-, [PbH2L]+, [PbHL2]3-, [PbHL], [PbL]-, [Pb(OH)L]2-, and [Pb(OH)2L]3-. The hydrolytic reactions of Hg(II), data on which were used in the analysis of the above system, were also studied by separate potentiometric titrations. Measurements of 13C NMR spectra of [HgL2]4- and [PbL]- and [PbHL2]3- in D2O solutions suggested that the ligand coordinates with both the metal ions through the sulfhydryl group and one of the two carboxylate groups in such a way that the five-membered chelate ring is formed within the complexes.     

Soft-tissue accumulation of lead in the blue tilapia,Oreochromis aureus (steindachner), and the modifying effects of cadmium and mercury

The interaction of mercury and cadmium with lead was investigated by exposingOreochromis aureus to two heavy metals simulataneously. The chronic accumulation prolife of lead was determined by analyzing the liver, brain, gill filaments, intestine, caudal muscle, spleen, trunk kidney, and gonads following exposure to lead alone and in mixtures with mercury and cadmium. Nominal exposure concentrations of lead were 0.05, 0.10, 0.50, and 1.00 mg/L. Mixtures of lead (0.50 or 0.05 mg/L) with cadmium (0.05 mg/L) and lead (0.50 or 0.05 mg/L) with mercury (0.05 mg/L) were also used. Following 140 d of exposure to lead, the highest concentrations of lead consistently accumulated in the trunk kidney. The concentration of lead in the kidney was decreased by coexposure to mercury or cadmium, but increased in the muscle and liver. Under all exposure regimes, the median concentration of lead in the muscle exceeded safety levels recommended for human consumption. In a food fish, such asO. aureus, a knowledge of toxic metal accumulation patterns is of great importance.     

Linear free-energy analysis of mercury(II) and cadmium(II) binding to three-stranded coiled coils

Investigators have studied how proteins enforce nonstandard geometries on metal centers to assess the question of how protein structures can define the coordination geometry and binding affinity of an active-site metal cofactor. We have shown that cysteine-substituted versions of the TRI peptide series [AcG-(LKALEEK)(4)G-NH(2)] bind Hg(II) and Cd(II) in geometries that are different from what is normally found with thiol ligands in aqueous solution. A fundamental question has been whether this structural perturbation is due to protein influence or a change in the metal geometry preference. To address this question, we have completed linear free-energy analyses that correlate the association of three-stranded coiled coils in the absence of a metal with the binding affinity of the peptides to the heavy metals, Hg(II) and Cd(II). In this paper, six new members of this family have been synthesized, replacing core leucine residues with smaller and less hydrophobic residues, consequently leading to varying degrees of self-association affinities. At the same time, studies with some smaller and longer sequenced peptides have also been examined. All of these peptides are seen to sequester Hg(II) and Cd(II) in an uncommon trigonal environment. For both metals, the binding is strong with micromolar dissociation constants. For binding of Hg(II) to the peptides, the dissociation constants range from 2.4 x 10(-)(5) M for Baby L12C to 2.5 x 10(-)(9) M for Grand L9C for binding of the third thiolate to a linear Hg(II)(pep)(2) species. The binding of Hg(II) to the peptide Grand L9C is similar in energetics for metal binding in the metalloregulatory protein, mercury responsive (merR), displaying approximately 50% trigonal Hg(II) formation at nanomolar metal concentrations. Approximately, 11 kcal/mol of the Hg(II)(Grand L9C)(3)(-) stability is due to peptide interactions, whereas only 1-4 kcal/mol stabilization results from Hg(II)(RS)(2) binding the third thiolate ligand. This further validates the hypothesis that the favorable tertiary interactions in protein systems such as merR go a long way in stabilizing nonnatural coordination environments in biological systems. Similarly, for the binding of Cd(II) to the TRI family, the dissociation constants range from 1.3 x 10(-)(6) M for Baby L9C to 8.3 x 10(-)(9) M for TRI L9C, showing a similar nature of stable aggregate formation.