Mercury's neurotoxicity is characterized by its disruption of selenium biochemistry

Background

Methylmercury (CH₃Hg⁺) toxicity is characterized by challenging conundrums: 1) “selenium (Se)-protective” effects, 2) undefined biochemical mechanism/s of toxicity, 3) brain-specific oxidative damage, 4) fetal vulnerability, and 5) its latency effect. The “protective effects of Se” against CH₃Hg⁺ toxicity were first recognized >50?years ago, but awareness of Se's vital functions in the brain has transformed understanding of CH₃Hg⁺ biochemical mechanisms. Mercury's affinity for Se is ~1 million times greater than its affinity for sulfur, revealing it as the primary target of CH₃Hg⁺ toxicity.

A comparison of the 8-hydroxydeoxyguanosine,chromosome aberrations and micronucleus techniques for the assessment of the genotoxicity of mercury compounds in human blood lymphocytes

We compared the mechanism of action of micronuclei (MN), unstable chromosome aberrations, and 8-hydroxydeoxyguanosine (8-OHdG) levels to evaluate the genotoxicity of methyl mercuric chloride (CH₃HgCl) and mercuric chloride (HgCl₂) in human peripheral lymphocytes. The chromosome aberrations in human peripheral lymphocytes exposed to various concentrations of CH₃HgCl or HgCl₂ increased in a concentration-dependent manner and were significantly higher than the control when the cells were incubated with 1 × 10⁻⁵ M (HgCl₂) or 2 × 10⁻⁶ M (CH₃HgCl). The increase in the incidence of micronucleated lymphocytes was significant among the exposed groups, being 2 × 10⁻⁵ M (HgCl₂) and 5 × 10⁻⁶ M (CH₃HgCl) compared with the control. CH₃HgCl was about 4-fold more potent than HgCl₂. We determined the 8-OHdG levels in human peripheral blood mononuclear cells(PBMC) and found that they were significantly higher in the exposed groups at 1 × 10⁻⁵ M (HgCl₂) and 5 × 10⁻⁶ M (CH₃HgCl) compared with the control. A detectable (p < 0.05) increase in the level of 8-OHdG was induced by CH₃HgCl at a concentration that was about 50% of the amount of HgCl₂ required to produce a similar response. The data confirmed the value of the MN and/or chromosome aberration assays for assessing of HgCl₂- and/or CH₃HgCl-induced genotoxicity, and indicated that they are about the same concentration as the 8-OHdG assay. The presence of genotoxic effects in peripheral blood lymphocytes exposed to the mercuric compounds indicated by the chromosome aberrations and the MN assays could be partly due either to the disturbance of the spindle mechanism, or to the elevated level of 8-OHdG brought by the generation of reactive oxygen species.     

Distribution of mercury, methyl mercury and organic sulphur species in soil, soil solution and stream of a boreal forest catchment

Concentrations of methyl mercury, CH₃Hg (II), total mercury, Hg_tot = CH₃Hg (II) + Hg (II), and organic sulphur species were determined in soils, soil solutions and streams of a small (50 ha) boreal forest catchment in northern Sweden. The CH₃Hg (II)/Hg_tot ratio decreased from 1.2–17.2% in the peaty stream bank soils to 0.4–0.8% in mineral and peat soils 20 m away from the streams, indicating that conditions for net methylation of Hg (II) are most favourable in the riparian zone close to streams. Concentrations of CH₃Hg (II) bound in soil and in soil solution were significantly, positively correlated to the concentration of Hg_tot in soil solution. This, and the fact that the CH₃Hg (II)/Hg_tot ratio was higher in soil solution than in soil may indicate that Hg (II) in soil solution is more available for methylation processes than soil bound Hg (II). Reduced organic S functional groups (Org-S_RED) in soil, soil extract and in samples of organic substances from streams were quantified using S K-edge X-ray absorption near-edge structure (XANES) spectroscopy. Org-S_RED, likely representing RSH, RSSH, RSR and RSSR functionalities, made up 50 to 78% of total S in all samples examined. Inorganic sulphide [e.g. FeS₂ (s)] was only detected in one soil sample out of 10, and in none of the stream samples. Model calculations showed that under oxic conditions nearly 100% of Hg (II) and CH₃Hg (II) were complexed by thiol groups (RSH) in the soil, soil solution and in the stream water. Concentrations of free CH₃Hg⁺ and Hg²⁺ ions in soil solution and stream were on the order of 10^–18 and 10^–32M, respectively, at pH 5. For CH₃Hg (II), inorganic bi-sulphide complexes may contribute to an overall solubility at concentrations of inorganic sulphides higher than 10^–9M, whereas considerably higher concentrations of inorganic sulphides (lower redox-potential) are required to increase the solubility of Hg (II).     

Dissolved and suspended mercury. species in the Wabigoon River (Ontario,Canada): seasonal and regional variations

Seasonal and regional variations in the speciation, sediment-water partitioning, and dynamics of mercury (Hg) were studied at selected sites along the Hg-polluted Wabigoon River, and at unpolluted headwater and tributary sites, during April–September, 1979. ‘Dissolved’ and ‘particulate’ forms of Hg in the water were separated by continuous-flow centrifugation in the field. The Hg and other pollutants such as wood chips and salt had been discharged from a chlor-alkali plant and paper mill at Dryden, Ontario. Concentrations and loadings of particulate methyl mercury (CH₃Hg⁺) and total particulate Hg (and loadings of total ‘dissolved’ Hg) were greatest during the spring flood (April-May) owing to accelerated resuspension and transport of sediments. Concentrations of ‘dissolved’ CH₃Hg⁺, however, were highest in the summer (July–September), probably reflecting stimulation of microbial methylating activity by elevated temperatures, together with factors such as reduced levels of metal-scavenging particulates and minimal dilution by runoff. Total dissolved Hg concentrations were relatively high in September at polluted sites only, possibly because of desorption from sediments due to elevated concentrations of Cl⁻ ions. Loadings of dissolved CH₃Hg⁺ tended to be high in the summer but were generally depressed (suggesting sorption by suspended particles) during the major spring-flood episode in May. During July–August dissolved CH₃Hg⁺ was a function of total dissolved Hg, suggesting rapid biomethylation of desorbed inorganic Hg; but in general dissolved and suspended CH₃Hg⁺ levels depended on environmental variables and were unrelated to total Hg concentrations. In the summer only, total dissolved Hg was a function of dissolved Cl⁻. Hg species in particulates were associated with sulfides, hydrated Fe and Mn oxides, organic matter (notably high molecular weight humic and humic-Fe components), and selenium (Se); but CH₃Hg⁺ and total Hg differed in their specific preferences for binding agents, implying that binding sites discriminate between CH₃Hg⁺ and Hg²⁺ ions. CH₃Hg⁺ was associated with sulfide and (in the spring only) with Fe oxides, whereas total Hg was associated with organic matter and Se and with DTPA- and NaOH-extractable Fe in the spring but with Mn oxide and NaOH-extractable organics in the summer. Sulfides were most abundant in May, indicating that they were eroded from bottom sediments, but Fe and Mn oxides were most abundant in the summer, probably owing to activities of filamentous iron bacteria and other micro-organisms. Particulate Hg was 98–100% nonextractable by mild solvents such as Ca acetate, CaCl₂, dilute acetic acid, and (at polluted sites only) DTPA solutions, suggesting that the particulate Hg mobilized in the spring may not be readily available to organisms; association with Se and high molecular weight humic matter also supports this hypothesis. Hg probably becomes more bio-available in the summer, as suggested by the upsurge in dissolved CH₃Hg⁺ and total dissolved Hg levels, and by increases in the solubility of particulate Hg in acetic acid, DTPA, H₂O₂, and NaOH solutions, as well as an increase in the relative importance of lower molecular weight fractions of NaOH-extractable Hg (in September). Regional variations in Hg speciation and partitioning reflected a gradient in sediment composition from wood chips near Dryden to silt-clay mud further downstream. Hg in silt-clay mud relatively far (> 35 km) downstream from the source of pollution or in unpolluted areas appeared to be more readily solubilized by Cl⁻ ions or chelators such as DTPA, more readily methylated (as indicated by downstream increases in dissolved CH₃Hg⁺ levels and CH₃Hg⁺/total Hg ratios), and was to a greater degree organically bound (H₂O₂-extractable), and thus was probably more bio-available, than Hg in wood-chip deposits. Possible explanations include weaker binding of Hg by the mud, the more finely divided state of the mud, and improved microbial growth at lower concentrations of toxic pollutants. Owing to enrichment in sulfides and Fe oxides, resuspended wood-chip sediments were especially efficient scavengers of CH₃Hg⁺. The results indicate that in any pollution abatement plan aimed at lowering the Hg levels in the biota of lakes fed by the Wabigoon River, immobilization, removal, or detoxification of dissolved as well as particulate forms of Hg in the river would probably have to be considered. Possibly, Hg species could be ‘scrubbed’ from the river water by increasing the suspended load and by sedimentation and treatment with Hg-binding agents in special receiving basins.     

Interactions between selenium and methylmercury in rat brain

The interaction of selenium with methylmercury was investigated in brain of animals labeled with ⁷⁵SeO₃^2? and CH₃²⁰³Hg⁺. Brains were fractionated into subcellular components and the cytosol was further fractionated by chromatography on Sephadex G-150 and G-200. The main result of these studies was evidence suggesting a shift of ⁷⁵Se from the cytosol to the mitochondrial fraction in brain when CH₃Hg⁺ was given. Concurrent equimolar (10 μmoles/kg) selenite injections increased the uptake of Hg but did not alter ²⁰³Hg distribution in brain. Changing the dose of CH₃Hg⁺ from 1 to 38 μmoles/kg had little effect on Hg uptake (% of dose per g). Gel filtrations on Sephadex G-150 and G-200 revealed that ²⁰³Hg in cytosol followed a pattern more closely related to protein (A₂₈₀) than to ⁷⁵Se, although a considerable portion of both isotopes eluted with proteins in the void volume. Assays of whole brain homogenates revealed a slight reduction in glutathione peroxidase activity in CH₃Hg⁺-treated rats which was not seen when equimolar selenite was injected with the CH₃Hg⁺.     

Mercury translocation in and evaporation from soil. II. Evaporation of mercury from podzolized soil profiles treated with HgCl2 and CH3HgCl

Mercury evaporation from soil columns of an iron humus podzol treated with various amounts of HgCl₂ and CH₃HgCl was measured over 3500 h. The effects of rain acidity, rain duration, and rain intensity were investigated. Hg evaporation from CH₃HgCl‐treated soil columns seems to be a biologically determined process. Hg evaporation from HgO₂‐treated soil probably is mainly an abiotic process, following a pseudo first‐order reaction with rapidly decreasing evaporation rate due to a decreasing amount of available Hg. The added Hg compounds were transformed to highly volatile Hg⁰ and/or (CH₃)₂Hg. The Hg evaporation rate decreased with increasing rain acidity, which may cause accumulation of Hg in the soil. No effects of rain duration and rain intensity were found.     

Hg2+-induced leakage of electrolytes and inhibition of NO3 − utilization inNostoc calcicola

Summary The effect of mercury (Hg²⁺) in the absence and presence of methylmercury (CH₃Hg⁺), cadmium (Cd²⁺), copper (Cu²⁺), nickel (Ni²⁺) and calcium (Ca²⁺) on Nostoc calcicola Bréb. has been studied in terms of electrolyte leakage, NO₃ ^– uptake and in vivo nitrate reductase (NR) activity to discover any possible correlation among such parameters under Hg²⁺ stress. Leakage of electrolytes from Hg²⁺-treated cyanobacterial cells was directly proportional to Hg²⁺ concentrations and exposure time. In comparison to NO₃ ^– uptake, an about 60-fold slower rate of NR activity was observed in the untreated cultures, the former being five times more Hg²⁺-sensitive. A non-competitive synergistic interaction of Hg²⁺ with CH₃Hg⁺ or Cd²⁺ and antagonistic with that of Ni²⁺ or Ca²⁺ has been observed for both the processes of NO₃ ^– utilization. The antagonistic interaction of Cu²⁺ with Hg²⁺ in terms of NO₃ ^– uptake and synergistic with respect to NR activity, has been attributed to the dual bonding preference of Cu²⁺ for cellular ligands. These findings suggest that (a) a statistically significant correlation exists among such parameters; (b) Hg²⁺ predominantly attacks the cyanobacterial cell membrane; (c) Hg²⁺ inhibits NO₃ ^– utilization; (d) the presence of other cations increases or decreases the inhibitory actions of Hg²⁺.     

Development of a transgenic tobacco plant for phytoremediation of methylmercury pollution

To develop the potential of plant for phytoremediation of methylmercury pollution, a genetically engineered tobacco plant that coexpresses organomercurial lyase (MerB) with the ppk-specified polyphosphate (polyP) and merT-encoding mercury transporter was constructed by integrating a bacterial merB gene into ppk/merT-transgenic tobacco. A large number of independent transgenic tobaccos was obtained, in some of which the merB gene was stably integrated in the plant genome and substantially translated to the expected MerB enzyme in the transgenic tobacco. The ppk/merT/merB-transgenic tobacco callus showed more resistance to methylmercury (CH₃Hg⁺) and accumulated more mercury from CH₃Hg⁺-containing medium than the ppk/merT-transgenic and wild-type progenitors. These results suggest that the MerB enzyme encoded by merB degraded the incorporated CH₃Hg⁺ to Hg²⁺, which then accumulated as a less toxic Hg-polyP complex in the tobacco cells. Phytoremediation of CH₃Hg⁺ and Hg²⁺ in the environment with this engineered ppk/merT/merB-transgenic plant, which prevents the release mercury vapor (Hg⁰) into the atmosphere in addition to generating potentially recyclable mercury-rich plant residues, is believed to be more acceptable to the public than other competing technologies, including phytovolatilization.     

The chemistry and transport of mercury in a small wetland in the Adirondack region of New York, USA

The biogeochemistry of Hg was evaluated in a small wetland in the Adirondack region of New York. Concentrations of total Hg (Hg_T) in streamwater draining the wetland showed little temporal variation. The annual areal watershed flux of Hg_T (2.2 µg/m²-yr) was considerably smaller than regional inputs of atmospheric deposition of Hg_T, indicating that the terrestrial environment is a net sink for atmospheric deposition of Hg_T. Drainage inputs of Hg_T were conservatively transported through the beaver impoundment. The annual flux of total methyl mercury (CH₃Hg⁺ _T was greater than literature values of atmospheric deposition suggesting that the watershed is a net source of CH₃Hg⁺ _T . Stream concentrations of CH₃Hg⁺ _T increased during low-flow summer conditions in a riparian wetland, and particularly at the outlet of the beaver impoundment. Net production of CH₃Hg⁺ _T occurred in the beaver impoundment (0.45 µg/m²-yr). Rates of net methylation for the beaver impoundment were comparable to values reported in the literature for wetlands.     

Acclimation of aquatic microbial communities to Hg(II) and CH3Hg+ in polluted freshwater ponds

The relationship of mercury resistance to the concentration and chemical speciation of mercurial compounds was evaluated for microbial communities of mercury-polluted and control waters. Methodologies based on the direct viable counting (DVC) method were adapted to enumerate mercury-resistant communities. Elevated tolerance to Hg(II) was observed for the microbial community of one mercury-polluted pond as compared to the community of control waters. These results suggest an in situ acclimation to Hg(II). The results of the methylmercury resistance-DVC assay suggested that minimal acclimation to CH₃Hg⁺ occurred since similar concentrations of CH₃HgCl inhibited growth of 50% of organisms in both the control and polluted communities. Analyses of different mercury species in pond waters suggested that total mercury, but not CH₃Hg⁺ concentrations, approached toxic levels in the polluted ponds. Thus, microbial acclimation was specific to the chemical species of mercury present in the water at concentrations high enough to cause toxic effects to nonacclimated bacterial communities.     

Binding of Mercurials to Membrane Suspensions and Undenatured Proteins

Binding capacities of membrane suspensions and dissolved compounds for mercurials were titrated by a new potentiometric method. Critical steps included a silver electrode of new design, the use of L-cysteine as a thiol buffer, a nitrogen atmosphere, and pretreatment of samples with equimolar mercurial and cysteine. Titrations had a sharp endpoint, accurate ±26 nmole methylmercury or ±8 nmole mercuric salt. Measurements of binding capacity of bovine serum albumin averaged 93% of the titer predicted for one SH group per molecule; those of human hemoglobin yielded 86-91% of the titer predicted for two SH groups per molecule. Yields dropped with exposure of protein solutions or membrane suspensions to atmospheric oxygen. Brain microsomes had significantly higher binding capacities (per milligram of protein) than red blood cell ghosts. The ratio of endpoint titers of CH₃ HgCl to HgCl₂ averaged 2:1 in assays of cysteine, proteins, and membranes, showing that the assay was free of denaturation artifacts and protein-protein interference. Solutions of EDTA showed measurable binding of Hg²⁺ but not of CH₃ Hg⁺. Satisfactory titrations were also obtained with N-ethylmaleimide.     

Skeletal muscle glycogen phosphorylase is irreversibly inhibited by mercury: Molecular,cellular and kinetic aspects

Muscle glycogen phosphorylase (GP) plays an important role in muscle functions. Mercury has toxic effects in skeletal muscle leading to muscle weakness or cramps. However, the mechanisms underlying these toxic effects are poorly understood. We report that GP is irreversibly inhibited by inorganic (Hg²⁺) and organic (CH₃Hg⁺) mercury (IC₅₀ = 380 nM and k_inact = 600 M⁻¹ s⁻¹ for Hg²⁺ and IC₅₀ = 43 μM and k_inact = 13 M⁻¹ s⁻¹ for CH₃Hg⁺) through reaction of these compounds with cysteine residues of the enzyme. Our data suggest that the irreversible inhibition of GP could represent one of the mechanisms that contribute to mercury-dependent muscle toxicity.     

The human xenobiotic-metabolizing enzyme arylamine N-acetyltransferase 1 (NAT1) is irreversibly inhibited by inorganic (Hg) and organic mercury (CH3Hg): Mechanism and kinetics

Human arylamine N-acetyltransferase 1 (NAT1) is a xenobiotic-metabolizing enzyme that biotransforms aromatic amine chemicals. We show here that biologically-relevant concentrations of inorganic (Hg²⁺) and organic (CH₃Hg⁺) mercury inhibit the biotransformation functions of NAT1. Both compounds react irreversibly with the active-site cysteine of NAT1 (half-maximal inhibitory concentration (IC₅₀) = 250 nM and k_inact = 1.4 × 10⁴ M⁻¹ s⁻¹ for Hg²⁺ and IC₅₀ = 1.4 μM and k_inact = 2 × 10² M⁻¹ s⁻¹ for CH₃Hg⁺). Exposure of lung epithelial cells led to the inhibition of cellular NAT1 (IC₅₀ = 3 and 20 μM for Hg²⁺ and CH₃Hg⁺, respectively). Our data suggest that exposure to mercury may affect the biotransformation of aromatic amines by NAT1.     

Studies of silyl and germyl group VI species. Part VIII. Synthesis and characterization of trimethyl-, silyl-, germyl- and stannyl-methyl derivatives of methane- and benzene-selenols

Asymmetrically substituted selenides of the type (CH₃)₃MCH₂SeR, where M = Si, Ge, Sn and R = CH₃ and C₆H₅, have been prepared by the reaction of Group IV halides with lithium organoselenolates and characterized by their infra-red, Raman, ¹H, ¹³C and ⁷⁷Se (M = Si, Ge) NMR spectra.     

Inorganic mercury (Hg2+) transport through lipid bilayer membranes

Summary Diffusion of inorganic mercury (Hg²⁺) through planar lipid bilayer membranes was studied as a function of chloride concentration and pH. Membranes were made from egg lecithin plus cholesterol in tetradecane. Tracer (²⁰³Hg) flux and conductance measurements were used to estimate the permeabilities to ionic and nonionic forms of Hg. At pH 7.0 and [Cl^–] ranging from 10–1000mm, only the dichloride complex of mercury (HgCl₂) crosses the membrane at a significant rate. However, several other Hg complexes (HgOHCl, HgCl ₃ ^– and HgCl ₄ ^2– ) contribute to diffusion through the aqueous unstirred layer adjacent to the membrane. The relation between the total mercury flux (J _Hg), Hg concentrations, and permeabilities is: 1/J _Hg=1/P ^ul[Hg ^t ]+1/P ^m [HgCl₂], where [Hg ^t ] is the total concentration of all forms of Hg,P ^ul is the unstirred layer permeability, andP ^m is the membrane permeability to HgCl₂. By fitting this equation to the data we find thatP ^m =1.3×10^–2 cm sec^–1. At Cl^– concentrations ranging from 1–100mm, diffusion of Hg ^t through the unstirred layer is rate limiting. At Cl^– concentrations ranging from 500–1000mm, the membrane permeability to HgCl₂ becomes rate limiting because HgCl₂ comprises only about 1% of the total Hg. Under all conditions, chemical reactions among Hg²⁺, Cl^– and/or OH^– near the membrane surface play an important role in the transport process. Other important metals, e.g., Zn²⁺, Cd²⁺, Ag⁺ and CH₃Hg⁺, form neutral chloride complexes under physiological conditions. Thus, it is likely that chloride can facilitate the diffusion of a variety of metals through lipid bilayer and biological membranes.     

Biosorption of inorganic and methyl mercury by a biosorbent from Aspergillus niger

A biosorbent prepared by alkaline extraction of Aspergillus niger biomass was evaluated for its potential to remove mercury species – inorganic (Hg²⁺) and methyl mercury (CH₃Hg⁺) – from aqueous solutions. Batch experiments were carried out to determine the pH and time profile of sorption for both species in the pH range 2–7. The Hg²⁺ exhibited more rapid sorption and higher capacity than the CH₃Hg⁺. Further, removal of both mercury species from spiked ground water samples was efficient and not influenced by other ions. Sorption studies with esterified biosorbent indicated loss of binding of both mercury species (>80%), which was regained when the ester groups were removed by alkaline hydrolysis, suggesting the involvement of carboxyl groups in binding. Further, no interconversion of sorbed species occurred on the biomass. The biosorbent was reusable up to six cycles without serious loss of binding capacity. Our results suggest that the biosorbent from Aspergillus niger can be used for removal of mercury and methyl mercury ions from polluted aqueous effluents.     

An assessment of thermodynamic reaction constants for simulating aqueous environmental monomethylmercury speciation

ABSTRACT

Monomethylmercury (CH₃Hg ⁺) is both the most ecologically significant and the least well characterized species of mercury in environmental settings. Our understanding of the environmental speciation behavior of this compound is limited both as the result of lesser available laboratory data (when compared to inorganic mercury) as well as the uncertainties associated with our understanding of the properties of environmental ligands. A careful examination and synthesis of data reported in the technical literature led to the following findings: (1) a 25°C, zero ionic strength bicarbonate ion complexation constant estimate is remarkably close to an earlier reported value at 0.4 M: CH₃Hg⁺ + HCo₃^-?CH₃HgHCO₃,log₁₀K = 2.6 (±0.22, 1 SD), (2) three 25°C zero ionic strength reaction constants reported by DeRobertis et al.(1998) were confirmed to within ~±0.1 log₁₀K units: CH₃Hg ⁺+ OH^-?CH₃HgOH, log₁₀K = 9.47; 2CH₃Hg ⁺ + H₂O?(CH₃Hg)₂OH ⁺ + H⁺, log₁₀K =?2.15; CH₃Hg ⁺+ Cl^-?CH₃HgCl, log₁₀K = 5.45, (3) “best estimate” literature complexation constants corrected to zero ionic strength include: CH₃Hg ⁺ + F^-?CH₃HgF, log₁₀K = 1.75 (20°C corr. Schwart-zenbach and Schellenberg, 1965); CH₃Hg ⁺ + Br^-?CH₃HgBr, log₁₀K = 6.87 (20°C corr. Schwartzenbach and Schellenberg, 1965); CH₃Hg ⁺ +1^-?CH₃HgI, log₁₀K = 8.85 (20°C corr. Schwartzenbach and Schellenberg, 1965); and CH₃Hg ⁺+ SO₄^2-?CH₃HgSO₄^-,log₁₀K = 2.64 (25°C, DeRobertis et al., 1998), (4) literature reported values for simulating monomethylmercury complexation with the carbonate ion may be too low: CH₃Hg ⁺+ CO₃^2-?CH₃HgCO₃^-, log₁₀K = 6.1 (Rabenstein et al., 1976; Erni, 1981), and (5) ‘‘best estimate’’ constants for simulating methyl mercury complexation with reduced environmental sulfur species include: CH₃Hg ⁺ + S^2-?CH₃HgS ^-, log₁₀K = 21.1; CH³Hg ⁺+ SH ^-? CH3HgSH, log₁₀K = 14.5 (H ⁺ + SH^-?CH₂S, log₁₀K = 6.88; Dyrssen and Wedborg, 1991); CH₃Hg ⁺ + RS^-?CH₃HgSR, log₁₀K = 16.5 (H + + RS^-?RSH, log₁₀K = 9.96; Qian et al., 2002); and CH₃Hg ⁺+ CH₃HgS^{1 -}?(CH₃Hg)₂S, log₁₀K = 16.32 (Schwartzenbach and Schellenberg, 1965; Rabenstein et al., 1978; and Erni, 1981).     

A selective phosphorescent chemodosimeter for mercury ion

The synthesis and crystal structure of an anionic phosphorescent iridium complex TBA[Ir(dfppy)₂(NCS)₂] (1) were reported. 1 can selectively detect Hg²⁺ with the help of UV-Vis absorption and emission spectra titration. In the presence of Hg²⁺, the obvious decrease of the luminescence intensity at 475 nm was investigated, which could be observed by the naked eyes. The phosphorescence quantum efficiency in CH₃CN solution changed from 0.07 to 0.00085. No obvious spectra changes were observed upon addition of a large excess of other transition metals. Due to its strong thiophilic affinity, the special chemical reaction induced by Hg²⁺ is responsible for the significant change of absorption and luminescence spectra, which is confirmed by ESI-MS.     

Discriminative detection of mercury (II) and hydrazine using a dual‐function fluorescent probe

A dual‐function fluorescent probe (Probe 1 ) was developed for discriminative detection of Hg²⁺ and N₂H₄. Probe 1 could discriminatively detect Hg²⁺ and N₂H₄ through two different reaction sites, with the mechanism for Probe 1 for Hg²⁺ depending on a desulfurization reaction and for N₂H₄ depending on the Schiff‐base reaction. N₂H₄ had minimal effect on Hg²⁺ detection in dimethyl sulfoxide (DMSO)/H₂O solution, but Hg²⁺ could interfere with N₂H₄ detection in DMSO/buffer solution. Different concentrations of Hg²⁺ and N₂H₄ resulted in different blue shades of Probe 1 test strips, and the shade of blue was different with the same concentration of Hg²⁺ or N₂H₄, as observed under ultraviolet light at 365 nm wavelength.     

Prevention by Ce3+ of DNA destruction caused by Hg2+ in fish intestine

The interactions between Hg²⁺, Ce³⁺, and the mixuure of Ce³⁺ and Hg²⁺, and DNA from fish intestine in vitro were investigated by using absorption spectrum and fluorescence emission spectrum. The ultraviolet absorption spectra indicated that the addition of Hg²⁺, Ce³⁺, and the mixture of Ce³⁺ and Hg²⁺ to DNA generated an obviously hypochromic effect. Meanwhile, the peak of DNA at 205.2 nm blue-shifted and at 258.2 nm red-shifted. The size of the hypochromic effect and the peak shift of DNA by metal ion treatments was Hg²⁺>Hg²⁺+Ce³⁺>Ce³⁺. The fluorescence emission spectra showed that with the addition of Hg²⁺, Ce³⁺, and the mixture of Ce³⁺ and Hg²⁺ the emission peak at about 416.2 nm of DNA did not obviously change, but the intensity reduced gradually and the sequence was Hg²⁺>Hg²⁺+Ce²⁺>Ce³⁺. Hg²⁺, Ce³⁺, and the mixture of Ce³⁺ and Hg²⁺ had 1.12, 0.19, and 0.41 binding sites to DNA, respectively; the fluorescence quenching of DNA caused by the metal ions all attributed to static quenching. The binding constants (K _A ) of binding siees were 8.98×10⁴ L/mol and 1.02×10⁴ L/mol, 5.12×10⁴ L/mol and 1.10×10³ L/mol, 6.66×10⁴ L/mol and 2.36×10³ L/mol, respectively. The results showed that Ce³⁺ could relieve the destruction of Hg²⁺ on the DNA structure.