Permeability of lipid bilayers to methylmercuric chloride: Quantification by fluorescence quenching of a carbazole-labeled phospholipid

We investigated the permeabilities of lipid bilayers to the neurotoxin methylmercuric chloride (MMC). This mercurial is an efficient collisional quencher of the fluorescence of N-alkyl carbazole derivatives. Quenching of the fluorescence of β-(3-(9-carbazole)-propionyl-L--phosphatidylcholine (CPA-PC) in vesicles of dimyristoyl phosphatidylcholine and of dioleoyl phosphatidylcholine reveal rapid diffusion of MMC in the alkyl side chain regions of these bilayers. By a combination of (1) the lipid concentration dependence of the apparent quenching constants, (2) the solubility of MMC in concentrated lipid dispersions and (3) the 270 MHz proton magnetic resonance of methylmercury in the presence of lipid bilayers we conclude that the lipid-water partition coefficient of this mercurial is less than or equal to two. Using the fluorescence quenching and the partitioning data we estimate the diffusion coefficient of MMC in these bilayers to range from 0.13 to 0.31 × 10⁻⁵ cm²/sec, or 20–47% of its diffusion coefficient in ethanol. These data indicate that lipid bilayers do not pose a significant permeability barrier to the diffusional transport of MMC.     

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.     

Human serum albumin-mercurial species interactions

Binding of metal ions to the heteroatomic sites of proteins is undoubtedly fundamental to their observed physiological effects. In this paper, the interactions of inorganic mercury (Hg2+), methylmercury (MeHg+), ethylmercury (EtHg+), and phenylmercury (PhHg+) with human serum albumin (HSA) were studied from the electrophoretic behaviors, stoichiometry, thermodynamics, and kinetics by using a new hybrid technique, capillary electrophoresis on-line coupled with electrothermal atomic absorption spectrometry (CE-ETAAS), together with the consequent structural information from circular dichroism and Raman spectroscopy. The stoichiometry (mercurial species to HSA) for the interactions of Hg2+, MeHg+, EtHg+, and PhHg+ with HSA was found to be 6:1, 4:1, 4:1, and 3:1, respectively. Two types of binding sites in HSA were observed for the binding of mercurial species with the orders of magnitude of binding constants of 10(7) and 10(6) L mol-1, respectively, showing strong affinity of mercurial species for HSA. The interactions of mercurial species with both types of binding sites in HSA are exothermic and thermodynamically favorable and are both enthalpically and entropically driven. The binding of mercurial species to HSA follows the first-order kinetics for mercurial species and zero-order kinetics for HSA with the apparent activation energy of 57-59 kJ mol-1. Among the four mercurial species examined, only Hg2+ induces the secondary structure transition of HSA. Mercury-HSA adducts are formed mainly through metal-sulfur binding with participation of C=O and/or C-N groups of amino acid residues in HSA molecules. The present work represents the most comprehensive study on the interactions between various mercurial species with HSA and provides new evidence for and insights into the interactions of mercurial species with HSA for further understanding of the toxicological effects of mercurial species.     

Does mercury promote lipid peroxidation?

In order to explore the observed association among mercury, atherosclerosis, and coronary heart disease, the effects of mercury, copper, and iron on the peroxidation of low-density lipoprotein (LDL) and on the enzymatic activities of glutathione peroxidase and myeloperoxidase were investigated in vitro. On the basis of our nuclear magnetic resonance (NMR) experiments, we conclude that mercury does not promote the direct nonenzymatic peroxidation of LDL, like copper and iron. In our enzyme measurements, mercury inhibited slightly myeloperoxidase, although not significantly in presence of LDL. Instead, inorganic mercury, but not methylmercury chloride, inhibited glutathione peroxidase effectively and copper event at 10 μmol/L, below physiological concentrations, doubled the inhibition rate. Copper and iron had no direct effect on glutathione peroxidase, but they both seem to activate production of HOCl by myeloperoxidase. We conclude here that, first, mercury and methylmercury do not promote direct lipid peroxidation, but that, second, a simultaneous exposure to high inorganic mercury, copper, and iron and low selenium concentrations can lead to a condition in which mercury promotes lipid peroxidations. This mechanism provides a plausible molecular-level explanation for the observed association between high body mercury content and atherosclerosis.     

Effects of Inorganic Mercury and Methylmercury on the Ionic Currents of Cultured Rat Hippocampal Neurons

1. The effects of inorganic Hg²⁺ and methylmercuric chloride on the ionic currents of cultured hippocampal neurons were studied and compared. We examined the effects of acute exposure to the two forms of mercury on the properties of voltage-activated Ca²⁺ and Na⁺ currents and N-methyl-D-aspartate (NMDA)-induced currents.2. High-voltage activated Ca²⁺ currents (L type) were inhibited by both compounds at low micromolar concentrations in an irreversible manner. Mercuric chloride was five times as potent as methylmercury in blocking L-channels.3. Both compounds caused a transient increase in the low-voltage activated (T-type) currents at low concentrations (1 M) but blocked at higher concentrations and with longer periods of time.4. Inorganic mercury blockade was partially use dependent, but that by methylmercury was not. There was no effect of exposure of either form of mercury on the I–V characteristics of Ca²⁺ currents.5. Na⁺- and NMDA-induced currents were essentially unaffected by either mercury compound, showing only a delayed nonspecific effect at a time of overall damage of the membrane.6. We conclude that both mercury compounds show a relatively selective blockade of Ca²⁺ currents, but inorganic mercury is more potent than methylmercury.     

Effects of mercury compounds on the spontaneous and potassium-evoked release of [3H]dopamine from mouse striatal slices

The effects of mercury compounds on the spontaneous and potassium-evoked release of [3H]dopamine from mouse striatal slices have been examined. All mercury compounds examined produced concentration-dependent increases in the spontaneous release of [3H]dopamine, with an order of potency of methylmercury greater than mercuric (Hg2+) mercury greater than p-choloromercuribenzene sulfonic acid. Methylmercury had no effect on the 25 mM potassium evoked release of [3H]dopamine in the presence of 1.3 mM calcium. However, in calcium-free conditions, methylmercury significantly increased the potassium-evoked release of [3H]dopamine. Mercuric mercury significantly reduced the 25 mM potassium evoked release of [3H]dopamine in the presence of 1.3 mM calcium, and this response was not reversible with brief washing of the tissue. In calcium-free conditions, mercuric mercury significantly elevated the evoked release of [3H]dopamine, similar to the result obtained with methylmercury. It is suggested that mercury compounds alter dopaminergic synaptic function, possibly by disrupting calcium homeostasis or calcium-dependent processes, and that methylmercury and mercuric mercury can have differential effects to alter dopaminergic neurotransmission.     

汞在新建水库食物网中生物累积与风险评价研究进展

汞是唯一参与全球循环的液态重金属。1974年,自美国学者Smith首次报道水库中鱼类总汞含量高于邻近自然湖泊以来,水库中鱼类汞升高的风险成为新建水库环境影响评价中的重要内容之一。汞在水库生态系统生物组分和非生物组分中含量升高的现象先后在世界各国报道,包括加拿大、美国、芬兰、泰国和巴西等。通过对系列的野外研究进行回顾,表明了水库形成后生态系统中汞的甲基化过程发生了变化。水库形成对汞在食物网中的鱼类、底栖生物、浮游生物的累积产生影响。水库中汞的生物累积、迁移转化主要与被淹没土壤和植物腐解过程有着直接或间接的关系。水库形成后,总汞、甲基汞和甲基汞比例在生态系统食物网各组分中的变化并不一致。蓄水后,水体中总汞变化较小,甲基汞和甲基汞比例上升明显;浮游生物尤其是浮游动物中总汞升高,但甲基汞和甲基汞比例升高更为明显;与浮游动物类似,底栖水生昆虫中总汞升高,甲基汞和甲基汞比例升高也更为明显;鱼类作为食物网顶级消费者,甲基汞比例一般在80%以上,在水库形成后鱼类总汞和甲基汞均明显升高,但甲基汞比例变化已经不大。这些变化揭示了水库形成后甲基汞在食物网传递的两个主要可能途径,一是微型生物食物网。通过悬浮颗粒物、浮游植物、浮游动物这一环节,甲基汞和甲基汞比例有明显的增加。第二个途径是底层生物食物网。通过悬浮颗粒物、细菌、碎屑食性底栖水生昆虫、肉食型底栖水生昆虫环节,甲基汞和甲基汞比例明显增加。这两种途径均能导致以水生昆虫、小鱼、甲壳类等为食的肉食性鱼类汞含量增加。水库形成后,生态系统中汞的甲基化发生了明显的"加速"过程。这种"加速"过程最直接的因素是成库后大量土壤淹没使得汞的甲基化平衡被打破。这个过程主要有两方面的影响。一方面是直接影响,被淹没土壤和植被在腐解过程中主动或被动地将甲基汞释放到水库生态系统中;另一方面是间接影响,被淹没土壤和植被的腐解使水库底部形成厌氧环境,有利于无机汞从被淹没土壤和植被中溶出,为甲基化反应提供充裕的、可供甲基化的无机汞,同时腐解产生的大量营养物质为微生物提供丰富食物来源,使硫酸盐还原菌大量繁殖,促进无机汞的甲基化。在我国,有关汞在新建水库食物网中生物累积和风险评价的研究有待进一步加强。     

The thioredoxin system as a target for mercury compounds

BackgroundMercury interaction with selenium in vivo has been recognized for >50 years. Several researchers attempted to use selenium to mitigate the detrimental effects of mercurial compounds but the results were controversial. Selenium pools in living organisms are quite low and the high affinity of mercury to bind selenols pointed out selenoproteins as possible targets of toxicity. Such was the case of the selenoenzyme thioredoxin reductase (TrxR) which is an integrant part of the thioredoxin system. Given the important role of this redox system for cellular functioning and the high affinity of mercury for TrxR's active site, this interaction can be key to understand the mechanism by which Hg causes cell death.Scope of the reviewThis review discusses the current state of knowledge concerning the interaction between mercury compounds and the thioredoxin system, its implications for the development of toxicity and the effects of selenium co-exposure.Major conclusionsThe mechanism of toxicity of mercurials is a complex chain of events starting with inhibition of the selenoenzyme, TrxR. Selenium supplementation protects TrxR from the toxicity of inorganic forms of mercury (i.e., Hg(II)) to a certain extent, but not from methylmercury.When TrxR is inhibited, thioredoxin is reduced by alternative mechanisms involving glutathione and glutaredoxin and only when this pathway is hampered does cell death occur.General significanceUnderstanding the molecular mechanism of mercury toxicity and the mechanisms of enzymatic compensation allows the design of mitigation strategies and, since TxrR and Trx exist in the plasma, puts forward the possibility for future use of changes in activity/expression of these enzymes as biomarkers of mercury toxicity, thus refining the risk assessment process.     

Organomercurial-volatilizing bacteria in the mercury-polluted sediment of Minamata Bay, Japan.

A total of 4,604 bacterial strains isolated from the sediments of Minamata Bay and nearby low-level-mercury stations (control stations) were screened for the ability to volatilize mercury from inorganic and organic mercurial compounds. The strains that volatilize mercury from several kinds of organomercurials were found only in the sediments of Minamata Bay.     

Organomercurial-volatilizing bacteria in the mercury-polluted sediment of Minamata Bay, Japan

A total of 4,604 bacterial strains isolated from the sediments of Minamata Bay and nearby low-level-mercury stations (control stations) were screened for the ability to volatilize mercury from inorganic and organic mercurial compounds. The strains that volatilize mercury from several kinds of organomercurials were found only in the sediments of Minamata Bay.     

Degradation of Methylmercury by Bacteria Isolated from Environmental Samples

A total of 207 bacterial cultures, isolated from environmental samples, was screened for ability to degrade methylmercury. Of these, 30 were found positive for aerobic demethylation. Twenty-two of these were shown to be facultative anaerobes and 21 of these degraded methylmercury anaerobically. All positive species volatilized methylmercury aerobically, and methane was produced as a degradation product. Although methylmercury degradation was complete in most cases, material balances indicated some of the inorganic mercury formed was not volatilized and is presumed bound to the cells. All positive isolates were tolerant to at least 0.5 mug of methylmercury per ml, and the extent of volatilization of mercury increased with concentration to the threshold value. The results indicate that demethylating species are prevalent in the environment and may be important in suppressing the methylmercury content of sediments.     

Dynamic accumulation and redistribution of methylmercury in the lens of developing zebrafish embryos and larvae

Neurotoxic methylmercury compounds are widespread in the environment and human exposure worries many communities worldwide. Despite numerous studies addressing methylmercury toxicity, the detailed mechanisms underlying its transport and accumulation, especially during early developmental stages, remain unclear. Zebrafish larvae are increasingly used as a model system for studies of vertebrate development and toxicology. Previously, we have identified the lens epithelium as the primary site for cellular mercury accumulation in developing zebrafish larvae (Korbas et al. in Proc Natl Acad Sci USA 105:12108–12112, 2008). Here we present a study on the dynamics of methylmercury accumulation and redistribution in the lens following embryonic and larval exposure to methylmercury l-cysteineate using synchrotron X-ray fluorescence imaging. We observed highly specific accumulation of mercury in the lens that continues well after removal of fish from treatment solutions, thus significantly increasing the post-exposure loading of mercury in the lens. The results indicate that mercury is redistributed from the original target tissue to the eye lens, identifying the developing lens as a major sink for methylmercury in early embryonic and larval stages.     

The effects of bromosulphophthalein, indocyanine green and bilirubin on the biliary excretion of methylmercury

The effects of three ligands for ligandin on the biliary excretion of methylmercury were investigated in male rats injected intravenously with 1.0 mg/kg Hg as Me203 HgCl. Bromosulphophthalein and indocyanine green inhibited the biliary excretion of methylmercury, while bilirubin had no such effect. None of the compounds tested which inhibited the biliary excretion of methylmercury decreased bile flow or changed the hepatic concentration of mercury of non-protein thiols. The possibility of the involvement of ligandin in the biliary excretion of methylmercury is discussed.     

锌对染汞孕鼠胚胎毒性的影响及其机理研究

目的:探讨妊娠期补锌对染汞孕鼠胚胎发育毒性的保护作用.方法:建立孕鼠动物模型,应用不同剂量的氯化甲基汞(0.01、0.05、2.00mg/kg·d)及5.00mg/kg·d硫酸锌于妊娠6～9天连续灌胃.蒸馏水灌胃为对照组,观察孕鼠及胚胎的汞毒性及硫酸锌的影响.应用ICP-MS法测定各组胎鼠脑组织汞含量;Western blot法检测各组胎鼠脑bcl-2蛋白表达情况;TUNEL法检测各组胎鼠脑细胞凋亡情况.结果:各组均未发现死胎、吸收胎及畸形胎;0.01、0.05mg/kg·d氯化甲基汞对孕鼠及胎鼠生长发育没有明显的抑制作用;2.00mg/kg·d氯化甲基汞可以明显抑制孕鼠体重增长及胎鼠身长、体重及尾长的增长(P＜0.05),但对孕鼠产仔数、胎窝总重及胎盘总重没有明显的影响,0.05mg/kg·d、2.00mg/kg·d 氯化甲基汞组胎鼠脑组织汞含量较对照组明显升高(P＜0.05),bcl一2蛋白表达明显下降(P＜0.05),脑细胞凋亡较对照组明显升高(P＜0.05);应用硫酸锌预处理后,氯化甲基汞对孕鼠及胚胎的毒性作用明显降低(P＜0.05),胎鼠脑组织汞含量较染汞组明显降低(P＜0.05),bcl-2蛋白表达明显升高(P＜0.05),胎鼠脑细胞凋亡明显降低(P＜0.05).结论:孕期补锌可以降低氯化甲基汞对孕鼠胚胎的毒性作用,其机制与锌通过升高bel-2蛋白的表达而抑制细胞凋亡有关.     

Quantitative aspects of mercurial-agarose gel electrophoresis

Single-stranded nucleic acids are capable of extensive intramolecular base pairing as well as intermolecular aggregation. Consequently, electrophoretic studies of single-stranded nucleic acids are most effective when conducted under denaturing conditions. A number of techniques are available for nucleic acid denaturing gel electrophoresis (1–3). In this paper we describe certain quantitative features of one of these techniques, mercurial-agarose gel electrophoresis (4–7). Specifically, we address the questions of resolution and base composition dependence and we introduce a new mercurial for agarose gel electrophoresis, p-chloromercuriphenyl-sulfonic acid.In a previous publication we demonstrated that methylmercury was an effective denaturant in an agarose gel (4). The mechanism of denaturation is presumably the disruption of hydrogen bonding by the reversible binding of methylmercury to uridine and guanosine imino nitrogens. At saturating mercurial concentrations accurate molecular weights can be determined, free of conformation effects. The presence of methylmercury has no observable effect on the mechanical properties of the gel. Hence the denaturing power of the gel can be readily varied. The strength and rigidity of agarose gels make them considerably easier to handle than acrylamide gels, and the large pore size ensures a system compatible with high molecular weight RNA.     

Accumulation of mercury in estuarine food chains

To understand the accumulation of inorganic mercury and methylmercury at the base of the estuarine food chain, phytoplankton (Thalassiosira weissflogii) uptake and mercury speciation experiments were conducted. Complexation of methylmercury as methylmercury-bisulfide decreased the phytoplankton uptake rate while the uptake rate of the methylmercury-cysteine and -thiourea complexes increased with increasing complexation by these ligands. Furthermore, our results indicated that while different ligands influenced inorganic mercury/methylmercury uptake by phytoplankton cells, the ligand complex had no major influence on either where the mercury was sequestered within the phytoplankton cell nor the assimilation efficiency of the mercury by copepods. The assimilation efficiency of inorganic mercury/methylmercury by copepods and amphipods feeding on algal cells was compared and both organisms assimilated methylmercury much more efficiently; the relative assimilation efficiency of methylmercury to inorganic mercury was 2.0 for copepods and 2.8 for amphipods. The relative assimilation is somewhat concentration dependent as experiments showed that as exposure concentration increased, a greater percentage of methylmercury was found in the cytoplasm of phytoplankton cells, resulting in a higher concentration in the copepods feeding on these cells. Additionally, food quality influenced assimilation by invertebrates. During decay of a T. weissflogii culture, which served as food for the invertebrates, copepods were increasingly less able to assimilate the methylmercury from the food, while even at advanced stages of decay, amphipods were able to assimilate mercury from their food to a high degree. Finally, fish feeding on copepods assimilated methylmercury more efficiently than inorganic mercury owing to the larger fraction of methylmercury found in the soft tissues of the copepods.     

Inhibition of the human thioredoxin system. A molecular mechanism of mercury toxicity

Mercury toxicity mediated by different forms of mercury is a major health problem; however, the molecular mechanisms underlying toxicity remain elusive. We analyzed the effects of mercuric chloride (HgCl(2)) and monomethylmercury (MeHg) on the proteins of the mammalian thioredoxin system, thioredoxin reductase (TrxR) and thioredoxin (Trx), and of the glutaredoxin system, glutathione reductase (GR) and glutaredoxin (Grx). HgCl(2) and MeHg inhibited recombinant rat TrxR with IC(50) values of 7.2 and 19.7 nm, respectively. Fully reduced human Trx1 bound mercury and lost all five free thiols and activity after incubation with HgCl(2) or MeHg, but only HgCl(2) generated dimers. Mass spectra analysis demonstrated binding of 2.5 mol of Hg(2+) and 5 mol of MeHg(+)/mol of Trx1 with the very strong Hg(2+) complexes involving active site and structural disulfides. Inhibition of both TrxR and Trx activity was observed in HeLa and HEK 293 cells treated with HgCl(2) or MeHg. GR was inhibited by HgCl(2) and MeHg in vitro, but no decrease in GR activity was detected in cell extracts treated with mercurials. Human Grx1 showed similar reactivity as Trx1 with both mercurial compounds, with the loss of all free thiols and Grx dimerization in the presence of HgCl(2), but no inhibition of Grx activity was observed in lysates of HeLa cells exposed to mercury. Overall, mercury inhibition was selective toward the thioredoxin system. In particular, the remarkable potency of the mercury compounds to bind to the selenol-thiol in the active site of TrxR should be a major molecular mechanism of mercury toxicity.     

A methylene blue-mediated enzyme electrode for the determination of trace mercury(II), mercury(I), methylmercury, and mercury-glutathione complex

A methylene blue-mediated enzyme biosensor has been developed for the detection of inhibitors including mercury(II), mercury(I), methylmercury, and mercury-glutathione complex. The inhibition to horseradish peroxidase was apparently reversible and noncompetitive in the presence of HgCl2 in less than 8 s and irreversibly inactivated when incubated with different concentrations of HgCl2 for 1-8 min. The binding site of horseradish peroxidase with HgCl2 probably was a cysteine residue SH. Mercury compounds can be assayed amperometrically with the detection limits 0.1 ng ml(-1) Hg for HgCl2 and methylmercury, 0.2 ng ml(-1) Hg for Hg2(NO3)2 and 1.7 ng ml(-1) Hg for mercury glutathione complex. Inactivation of the immobilized horseradish peroxidase was displayed in the AFM images of the enzyme membranes.     

Methylation of mercury compounds in soil,sediment and sewage-sludge samples

Summary Sediments of the rivers Rhine and Yssel and sewage sludge samples showed high mercury contents (5–30 ppm). Usually less than 1% — in one sludge sample 5% — of the mercury was in the form of methylmercury. Incubation of these samples, under varied aerobic and anaerobic conditions, with or without HgCl₂ or phenylmercuryacetate added, gave no or only very slight formation of methylmercury.Most agricultural soils have a mercury content below 0.1 ppm and methylation will be no problem.     

Accumulation of methylmercury and inorganic mercury in the brain

Differences in metabolism between different mercury species are well recognized. Conclusions that only a minor demethylation of methylmercury takes place in the brain are based primarily on results from short term studies. Results from a number of studies on humans exposed for many years to methylmercury have shown high concentrations of inorganic mercury in the brain in relation to total mercury. Similar evidence is available from studies on monkeys exposed for several years to methylmercury. The results indicate that a significant accumulation of inorganic mercury takes place with time despite the fact that the demethylation rate is slow. Differences in biological halftimes between different mercury species will explain the results. Some data do still need confirmation using different analytical methods. There is reason to believe that the one-compartment model for methyl mercury cannot be used without reservations. Inorganic mercury has a complicated metabolism. After exposure to metallic mercury vapor, inorganic mercury, probably bound to selenium, accumulates in the brain. A fraction of the mercury is excreted, with a long biological halftime. Studies on rats and monkeys indicate that inorganic mercury penetrates the blood-brain barrier only to a very limited-extent.