Abstract:Bis(cysteineato)mercury(II) hydrochloride hemihydrate, (C3H6O2NS),Hg.HCl.-',H2O, was obtained by reaction of ethanolic solutions of L-cysteine hydrochloride with either HgC1, in 95% EtOH, Hg(OAc), in MeOH, Hg(NO,), in HOAc, or by reaction of L-cysteine (free base) with HgCI,. Reaction of L-cysteine (free base) with Hg(OAc), gave a mercury(I1) cysteineate with composition (C3H6O2NS),Hg,.
Bis(S-methyl-L-cysteineate)mercury (II),(C4H,02NS)2Hg,wasobtained byreactionof S-methyl-L-cysteinewith Hg(OAc),. 'H-and '3C-n… Show more
“…The biological chemistry of mercury is dominated by coordination to cysteine thiolate groups in agreement with the preference of this metal ion for the soft sulfur ligands and a great deal of research has been conducted to understand how the amino acid interacts with metals [11][12][13][14][15]. Several types of cysteine derivatives (e.g., pencillamine and N -actylcysteine) form soluble complexes and have been suggested as possible detoxification agents [16][17][18][19]. Although mercury(II) being a soft Lewis acid forms quit stable complexes with thiol groups [20][21][22][23], many thiolates remain labile and undergo ligand exchange, which is more pronounced in low (two and three)-coordinate compounds [24,25].…”
Abstract. Mercury(II) complexes of thiolates having the general formula [Hg(RS)Cl 2 ]− and [Hg(RS) 2 ] have been prepared and characterized by IR and NMR ( 1 H and 13 C) spectroscopy (RSH = 2-aminoethanethiol hydrochloride (Aet), cysteine (Cys), thiosalicylic acid (Ts) and 2-mercaptonicotinic acid (Mnt)). The spectral data suggests that the coordination of thiolates to mercury(II) occurs through the sulfur as indicated by the absence of S-H vibrations in IR and significant downfield shifts in the C-S resonance in 13 C NMR. However, in Mnt complexes, coordination through both sulfur and nitrogen is indicated. Antimicrobial activities of the complexes were evaluated by minimum inhibitory concentration and the results showed that the complexes exhibited a wide range of activities against gram-negative bacteria (E. coli, P. aeruginosa), while moderate activity was observed against a mold, P. citrinum.
“…The biological chemistry of mercury is dominated by coordination to cysteine thiolate groups in agreement with the preference of this metal ion for the soft sulfur ligands and a great deal of research has been conducted to understand how the amino acid interacts with metals [11][12][13][14][15]. Several types of cysteine derivatives (e.g., pencillamine and N -actylcysteine) form soluble complexes and have been suggested as possible detoxification agents [16][17][18][19]. Although mercury(II) being a soft Lewis acid forms quit stable complexes with thiol groups [20][21][22][23], many thiolates remain labile and undergo ligand exchange, which is more pronounced in low (two and three)-coordinate compounds [24,25].…”
Abstract. Mercury(II) complexes of thiolates having the general formula [Hg(RS)Cl 2 ]− and [Hg(RS) 2 ] have been prepared and characterized by IR and NMR ( 1 H and 13 C) spectroscopy (RSH = 2-aminoethanethiol hydrochloride (Aet), cysteine (Cys), thiosalicylic acid (Ts) and 2-mercaptonicotinic acid (Mnt)). The spectral data suggests that the coordination of thiolates to mercury(II) occurs through the sulfur as indicated by the absence of S-H vibrations in IR and significant downfield shifts in the C-S resonance in 13 C NMR. However, in Mnt complexes, coordination through both sulfur and nitrogen is indicated. Antimicrobial activities of the complexes were evaluated by minimum inhibitory concentration and the results showed that the complexes exhibited a wide range of activities against gram-negative bacteria (E. coli, P. aeruginosa), while moderate activity was observed against a mold, P. citrinum.
“…During leaching, Hg and L-cysteine form a Hg(II) complex (Neville and Drakenberg 1974). In the literature, there is evidence from polarographic measurements for the formation of at least three mercurial complexes with cysteine (R-SH): Hg(RS) 2 , Hg 2 (RS) 2 and Hg 3 (RS) 2 , whereas Hg(RS) 2 is the predominant complex ( Fig.…”
Section: Mobilisation Of Hg Bound To Mineral Surfacesmentioning
confidence: 99%
“…In the literature, there is evidence from polarographic measurements for the formation of at least three mercurial complexes with cysteine (R-SH): Hg(RS) 2 , Hg 2 (RS) 2 and Hg 3 (RS) 2 , whereas Hg(RS) 2 is the predominant complex ( Fig. 2d; Stricks and Kolthoff 1953;Neville and Drakenberg 1974;Bramanti et al 1999). The oxidation process of Hg by cysteine follows the reaction (Kolthoff and Barnum 1940):…”
Section: Mobilisation Of Hg Bound To Mineral Surfacesmentioning
confidence: 99%
“…Despite the high thermodynamic stability of Hg-cysteine complexes (pKs=∼40; Stary and Kratzer 1988), it has been observed that these Hg(II) complexes in biological systems are quite labile (Rabenstein and Isab 1982;Cheesman et al 1988) and can be determined by the addition of SnCl 2 and NaBH 4 (Bramanti et al 1999). Neville and Drakenberg (1974) also assumed complex alteration during their experiments. The Hg(II)-cysteine complex thus seems to be a labile complex which can potentially undergo various species transformations probably related to microbial attack of the cysteine complex.…”
Section: Mobilisation Of Hg Bound To Mineral Surfacesmentioning
A new approach in soil remediation washing techniques is the use of L-cysteine based on the formation of organic complexes. In this study, the applicability of L-cysteine for the mobilisation of different mercury species from contaminated soils was evaluated. Soils were treated with L-cysteine solutions with S-Hg molar ratios of 1, 2, 10, 20, 100 and 200. In 24 h batch experiments, leachates with water could mobilise 1% of Hg. The addition of Lcysteine led to an increase of Hg mobilisation of 42% for soils with inorganically bound Hg. In column experiments, the maximum Hg removal rate was 75%. For soils with organically bound Hg or HgS, only 1-5% of Hg was mobilised. Thus, the extraction of Hg from soils with L-cysteine is highly dependent on the Hg-binding form. Hg speciation analyses of leachates indicate that Hg-L-cysteine complexes are labile complexes which can be easily transformed. Soil samples speciation analysis revealed that reduction to elemental mercury takes place at low S-Hg ratios (1 to 10), assumingly by microbial activity. At higher S-Hg ratios of 10 and 100, precipitation of stable Hg-S complexes could be observed. These species transformation processes are limitations for considering Lcysteine leaching as a remediation strategy.
“…Towards mercuric ion (HgZ+) the binding mode is pH dependent. Although early potentiometric work (1) suggested little or no involvement of thioether coordination to HgZ+ for methionine, ethionine, or S-methylcysteine, it later became apparent from lH (2)(3)(4)(5) and 13C nmr (4)(5)(6) studies of Hg2+/ methionine, ethionine, or S-methyl-L-cysteine solutions that under acidic conditions (pD I 2) HgZ+ was bound exclusively to the thioether sulfur atom.…”
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