Methylmercury accumulation and fluxes across the intestine of channel catfish,Ictalurus punctatus

The excised intestines of channel catfish, Ictalurus punctatus, were perfused at 20 or 4 degrees C for 1 h 45 min, with methylmercury (CH(3)HgCl) alone, or in the presence of excess L-cysteine (L-Cys), D-cysteine (D-Cys), L-methionine (L-Met); or with ouabain or probenecid to identify the potential CH(3)Hg(II) uptake pathways in fish intestines. A temperature effect was noted, with CH(3)Hg(II) concentrations in tissues perfused at 20 degrees C being higher than at 4 degrees C, substantiating the idea that mechanisms requiring metabolic energy are involved in CH(3)Hg(II) uptake in fish intestines. The results indicate that, when CH(3)Hg(II) is complexed as the CH(3)Hg-L-Cys complex, it is taken up via an L-neutral amino acid carrier and rapidly transported to the serosal side of the intestine. Methylmercury uptake could be inhibited by probenecid and ouabain, although probenecid had less impact on CH(3)Hg(II) uptake than ouabain. Our results for CH(3)Hg(II) uptake in the presence of D-Cys, L-Met in excess of L-Cys, or with a metal mixture further established that CH(3)Hg(II) uptake across fish intestines occurs via a variety of pathways, including an energy-dependent L-neutral amino acid carrier, and that the route and amount of accumulation were a function of CH(3)Hg(II) speciation in the digestive tract of the fish.     

The intestinal parasite Pomphorhynchus laevis (Acanthocephala) interferes with the uptake and accumulation of lead (210Pb) in its fish host chub (Leuciscus cephalus)

Uninfected chub as well as fish experimentally infected with the acanthocephalan parasite Pomphorhynchus laevis were exposed to ²¹⁰Pb²⁺ for up to 38 days and the uptake and distribution of lead within different fish organs and the parasites was determined at various time points. Highest metal concentrations were detected in the acanthocephalans, followed by intestine, bile, liver, gill and muscle of the fish host. Infected chub had significantly lower ²¹⁰Pb levels in the gills on day 17 (P≤0.01), in the bile on day 24 (P≤0.05) and in the gills as well as in the intestine on day 38 compared with uninfected fish. A subsequent polynomial regression revealed that lead levels for the infected fish ranged below the levels determined for uninfected fish during most of the exposure period. This is the first proof that P. laevis reduces lead levels in the bile thereby diminishing or even impeding the hepatic intestinal cycling of lead, which may reduce the amount of metals available for the fish organs. This is especially important for ecotoxicological research. For example, organisms used as accumulation indicators may erroneously indicate low levels of pollution if they are infected with parasites which alter their pollutant uptake mechanisms. Additionally, the results gave further experimental evidence for acanthocephalans as accumulation indicators for metals.     

Effects of cadmium and mercury on Na(+)-K+, ATPase and uptake of 3H-dopamine in rat brain synaptosomes.

Effects in vivo of cadmium (Cd), mercury (Hg) and methylmercury (CH3Hg) on Na(+)-K+ ATPase and uptake of 3H-dopamine (DA) in rat brain synaptosomes were studied. These heavy metals significantly inhibited the Na(+)-K+ ATPase activity in a dose-dependent manner. Similarly, inhibition of DA uptake by synaptosomes was also observed in rats treated with these metals. Intraperitoneal route of metal administration was found to be more effective than per os treatment. Mercuric compounds compared to Cd elicited a higher inhibition of Na(+)-K+ ATPase and DA uptake in rat brain synaptosomes.     

1H-NMR study of the removal of methylmercury from intact erythrocytes by sulfhydryl compounds

The effectiveness of penicillamine, N-acetylpenicillamine, meso-2,3-dimercaptosuccinic acid, 2,3-dimercaptopropanesulfonic acid, and dithioerythritol for removing methylmercury (CH3Hg(II) from intact human erythrocytes has been studied by 1H-nuclear magnetic resonance spectroscopy. The removal of CH3Hg(II) was monitored by measuring the chemical shift of the resonance for the proton on the alpha-carbon of the cysteinyl residue of intracellular glutathione in 1H-NMR spectra of intact, CH3Hg(II)-containing erythrocytes in suspensions to which the sulfhydryl ligands were added. Because exchange of intracellular glutathione between its free and CH3Hg(II) complexed forms is fast, the chemical shift of the cysteinyl resonance provides a direct, noninvasive measure of the fraction of intracellular glutathione that is complexed. The sulfhydryl ligands were found to remove CH3Hg(II) from intact erythrocytes in the order 2,3-dimercaptosuccinic acid greater than 2,3-dimercaptopropane sulfonic acid greater than dithioerythritol greater than penicillamine approximately N-acetylpenicillamine, which also is the order of the conditional formation constants of the CH3Hg(II) complexes at pH 7.4. All five ligands removed CH3Hg(II) from intact erythrocytes much more rapidly than can be accounted for by a mechanism in which the ligand crosses the membrane, combines with the CH3Hg(II), and then transports it out of the cell. An alternative mechanism is proposed in which the ligand reacts with CH3Hg(II) which is complexed by sulfhydryl groups of the membrane, which in turn react with the intracellular CH3Hg(II) to bring more CH3Hg(II) into the membrane, where it can react with the added sulfhydryl ligand.     

Accumulation of zinc and cadmium by Cytophaga johnsonae

Passive and active accumulation of zinc and cadmium by a common soil and freshwater bacterium, Cytophaga johnsonae, was studied using a radio-tracer batch distribution technique. The effects of variation of pH (3–10), as well as of ionic strength (0.007 and 0.07 m) on passive accumulation of the metals were examined. For both zinc and cadmium, accumulation was mainly due to passive processes, such as surface adsorption and/or diffusion into the periplasm. However, at low zinc concentrations, accumulation increased when glucose was added, suggesting an active uptake; at higher zinc concentrations such uptake was not detected, probably because it was masked by the stronger sorption properties of the cell wall. Adsorption of the metals was pH dependent: at higher ionic strength, accumulation was enhanced at pH values above 7; at lower ionic strength, adsorption differed and was markedly higher, with increased accumulation between pH 5 and 8.     

Transport of cadmium across the apical membrane of epithelial cell lines

Cadmium (Cd) uptake and secretion across the apical membrane of epithelial cells was studied using LLC-PK1 cells cultured on Petri dishes and permeable membranes, respectively. Cd accumulation in cells from the apical medium was decreased by low temperature and metabolic inhibitors. A saturable tendency was observed between initial Cd accumulation and increased concentrations of Cd in the apical medium at 37 degrees C, but not at 4 degrees C. Co-incubation with ZnCl2 or CuCl2 competitively decreased Cd accumulation at 37 degrees C. A decrease in the pH of the apical medium markedly decreased Cd accumulation. Pretreatment of cells with an inorganic anion-exchange inhibitor significantly decreased Cd uptake at pH 7.4 in the presence of bicarbonate, but only marginally in its absence. A decrease in the pH of the apical medium increased the secretory (basolateral-to-apical) transport of Cd, with a concomitant decrease in the cellular accumulation of Cd. Co-incubation with Cd and tetraethylammonium, a typical substrate of the organic cation transporter, decreased Cd transport, with a concomitant increase in cellular Cd accumulation. The uptake and secretion of Cd across the apical membrane appear to be partly mediated via an inorganic anion exchanger and a H+ antiport of the organic cation transport system, respectively. Therefore, a decrease in pH of the apical medium markedly decreases Cd accumulation, possibly as a result of not only the decrease in Cd uptake via an inorganic anion exchanger, but also the increase in Cd secretion via the Cd2+/H+ antiport. Further evidence of the antiport was obtained from experiments using brush border membrane vesicles isolated from rat kidney and small intestine. In addition, passive diffusion of Cd appears to be decreased by low temperature and a decrease in pH.     

Histological changes in relation to accumulation and elimination of inorganic and methyl mercury in gills of Labeo rohita Hamilton

L. rohita was exposed to identical concentrations of inorganic and methyl mercury (HgCl2 and CH3HgCl) and the gills were studied for mercury bioaccumulation and histological changes. In methyl mercury exposed group the mercury level in the gills continuously increased til the end of the exposure period whereas the level started decreasing from the day 30 onwards in the other group even though the exposure was continued for 60 days. Histological changes were similar in inorganic and methyl mercury treated fish except the higher intensity observed in the latter treatment. Under depuration for 15 days the clearance rate of accumulated mercury and subsequent histological recovery in the gills were less prominent in fish pretreated with methyl mercury.     

Accumulation of pollutants in fish

The amount of radioactivity which derived from 14C-labeled pollutants was determined in liver, kidney, intestine, blood, muscle and gills of carp, exposed for 6, 24 and 72 hr to high external concentrations of urea, methanol, atrazine and PCP. The results allowed one to calculate roughly the uptake rate for these compounds. It was low for urea (0.055 micrograms/g per hr), higher for methanol (0.12) and atrazine (0.16) and highest for PCP (1.5). The bioaccumulation factors (BFs) were determined for the different substances and organs. They correlated with the hydrophilic-lipophilic nature of the chemicals. The more lipophilic the substances the more accumulation occurred in the liver. PCP accumulated the most. BF was 300-400 in most tissues except muscle where it was quite low. The BF was 3-4 for atrazine in liver, kidney and intestine, but just 1 in blood, muscle and gills. There is some evidence that the BF for methanol equals 1 in liver, kidney, gills and intestine. It is less than 1 in blood and muscle. Urea was equally distributed in all organs and in the external medium.     

Multiple effects of mercury on cell volume regulation, plasma membrane permeability, and thiol content in the human intestinal cell line Caco-2

In a previous study, we characterized Cd–Hg interactions for uptake in human intestinal Caco-2 cells. We pursued our investigations on metal uptake from metal mixtures, focusing on the effects of Hg on cellular homeostasis. A 4-fold higher equilibrium accumulation value of 0.3 μmol/L ²⁰³Hg was measured in the presence of 100 μmol/L unlabeled Hg in the serum-free exposure medium without modification in the initial uptake rate. This phenomenon was eliminated at 4^∘C. Mercury induced an increase in tritiated water and [³H]mannitol uptakes for exposure times greater than 20 min. Incubations for 20 min and 30 min with 100 μmol/L Hg and 2 mmol/L N-ethylmaleimide (NEM) resulted in a 34% and 50% reductions in cellular thiol staining, respectively, with additive effects. Lactate dehydrogenase leakage and live/dead assays confirmed the maintenance of cell membrane integrity in Hg- or NEM-treated cells. We conclude that Hg may alter membrane permeability and increase cell volume without any loss in cell viability. This phenomenon is sensitive to temperature and could involve Hg interaction with membrane thiols, possibly related to solute transport. During metal uptake from metal mixtures, Hg may thus promote the uptake of other toxic metals by increasing cell volume and consequently cell capacity. Deceased 25 March 2004     

Effects of dissolved organic carbon and salinity on bioavailability of mercury.

Hypotheses that dissolved organic carbon (DOC) and electrochemical charge affect the rate of methylmercury [CH3Hg(I)] synthesis by modulating the availability of ionic mercury [Hg(II)] to bacteria were tested by using a mer-lux bioindicator (O. Selifonova, R. Burlage, and T. Barkay, Appl. Environ. Microbiol. 59:3083-3090, 1993). A decline in Hg(II)-dependent light production was observed in the presence of increasing concentrations of DOC, and this decline was more pronounced at pH 7 than at pH 5, suggesting that DOC is a factor controlling the bioavailability of Hg(II). A thermodynamic model (MINTEQA2) was used to select assay conditions that clearly distinguished among various Hg(II) species. By using this approach, it was shown that negatively charged forms of mercuric chloride (HgCl3-/HgCl(4)2-) induced less light production than the electrochemically neutral form (HgCl2), and no difference was observed between the two neutral forms, HgCl2 and Hg(OH)2. These results suggest that the negative charge of Hg(II) species reduces their availability to bacteria and may be one reason why accumulation of CH3Hg(I) is more often reported to occur in freshwater than in estuarine and marine biota.     

The effect of aqueous speciation and cellular ligand binding on the biotransformation and bioavailability of methylmercury in mercury-resistant bacteria

Mercury resistant bacteria play a critical role in mercury biogeochemical cycling in that they convert methylmercury (MeHg) and inorganic mercury to elemental mercury, Hg(0). To date there are very few studies on the effects of speciation and bioavailability of MeHg in these organisms, and even fewer studies on the role that binding to cellular ligands plays on MeHg uptake. The objective of this study was to investigate the effects of thiol complexation on the uptake of MeHg by measuring the intracellular demethylation-reduction (transformation) of MeHg to Hg(0) in Hg-resistant bacteria. Short-term intracellular transformation of MeHg was quantified by monitoring the loss of volatile Hg(0) generated during incubations of bacteria containing the complete mer operon (including genes from putative mercury transporters) exposed to MeHg in minimal media compared to negative controls with non-mer or heat-killed cells. The results indicate that the complexes MeHgOH, MeHg-cysteine, and MeHg-glutathione are all bioavailable in these bacteria, and without the mer operon there is very little biological degradation of MeHg. In both Pseudomonas stutzeri and Escherichia coli, there was a pool of MeHg that was not transformed to elemental Hg(0), which was likely rendered unavailable to Mer enzymes by non-specific binding to cellular ligands. Since the rates of MeHg accumulation and transformation varied more between the two species of bacteria examined than among MeHg complexes, microbial bioavailability, and therefore microbial demethylation, of MeHg in aquatic systems likely depends more on the species of microorganism than on the types and relative concentrations of thiols or other MeHg ligands present.     

Biomonitoring Atmospheric Heavy Metals with Lichens: Theory and Application

Recent records of environmental contamination noted a moderate decrease of SO2 pollution, whereas the burden of atmospheric heavy metals is still considerable. The present review refers to the entrapment, uptake, and accumulation of heavy metals by lichen thalli, made apparent by parameters of lichen vitality and stress. The particulate nature of airborne heavy metals is made evident by parameters referring to the entrapment of heavy-metal containing particles by lichen thalli. The mechanism of uptake of heavy metals, investigated by means of controlled experiments, refers to extracellular and intracellular uptake. The rate of absorption and the accumulation of heavy metals is dependent on morphological features of lichen thalli in addition to kind and intensity of emission sources and to nonanthropogenic factors such as climate and topography. The role of lichens as biomonitors is demonstrated by the case of lead. In contrast to data obtained by retrospective studies, using lichens as biomonitors of heavy metal pollution, performed in the 1970s, which indicated an increase of Pb as a result of the massive use of leaded gasoline, the subsequent disuse of this additive led to a decrease detected in later studies. The disparity of emission sources is illustrated by the case of Hg. Mercury is a product of anthropogenic activity in addition to its natural derivation. The dominance of the anthropogenic factors is made obvious by high levels of Hg recorded near chlor alkali plants and other industrial sites. The role of the substrate in the uptake and accumulation of heavy metals was investigated to detect its relative share. Airborne metals were, however, determinant factors in the metal content of lichen thalli. The interaction of contaminants and biomonitors has a definite physiological impact on the vitality of the biomonitors. Physiological processes of disintegration investigated in this context are degradation of cell membranes and chlorophyll, decrease of the quantum yield of photosynthesis, decrease of the photosynthetic rate, increase of stress-ethylene production, and severe ultrastructural change. Lichens exposed to heavy metal pollution exhibit changes of the spectral reflectance response, an increase of malondialdehyde (MDA), a decrease of ATP, and injury to enzymatic activities. A comparative analysis of data referring to the accumulation of airborne elements in lichens and of data referring to alterations in physiological parameters of lichen viability substantiates the validity of assessments of environmental quality.     

Cadmium accumulation by a Citrobacter sp. immobilized on gel and solid supports: Applicability to the treatment of liquid wastes containing heavy metal cations

Polyacrylamide gel-immobilized cells of a Citrobacter sp. removed cadmium from flows supplemented with glycerol 2-phosphate, the metal uptake mechanism being mediated by the activity of a cell-bound phosphatase that precipitates liberated inorganic phosphate with heavy metals at the cell surface. The constraints of elevated flow rate and temperature were investigated and the results discussed in terms of the kinetics of immobilized enzymes. Loss in activity with respect to cadmium accumulation but not inorganic phosphate liberation was observed at acid pH and was attributed to the pH-dependent solubility of cadmium photsphate. Similarly high concentrations of chloride ions, and traces of cyanide inhibited cadmium uptake and this was attributed to the ability of these anions to complex heavy metals, especially the ability of CN(-) to form complex anions with Cd(2+). The data are discussed in terms of the known chemistry of chloride and cyanide-cadmium complexes and the relevance of these factors in the treatment of metal-containing liquid wastes is discussed. The cells immobilized in polyacrylamide provided a convenient small-scale laboratory model system. It was found that the Citrobacter sp. could be immobilized on glass supports with no chemical treatment or modification necessary. Such cells were also effective in metal accumulation and a prototype system more applicable to the treatment of metal-containing streams on a larger scale is described.     

The role of aryl hydrocarbon receptor and the reactive oxygen species in the modulation of glutathione transferase by heavy metals in murine hepatoma cell lines

Glutathione transferase (GST) is a phase II detoxifying enzyme that plays a protective mechanism against oxidizing substances and toxic contaminants. Among these contaminants, heavy metals and polycyclic and halogenated aromatic hydrocarbons (PHAHs) have been shown to exert their toxic effects through the modulation of detoxifying enzymes, including the GSTs. Recently, we showed that heavy metals particularly Hg2+, Pb2+, and Cu2+ modulate the expression of phase II detoxifying enzymes such as NAD(P)H:quinone oxidoreductase 1 and Gsta1 in a concentration- and time-dependent manner. However, the effect of heavy metals and their potential interactions with aryl hydrocarbon receptor (AhR) ligands, PHAHs, on total Gst activity is still unknown. In the current study, we have investigated the effects of Hg2+, Pb2+, and Cu2+ in the absence and presence of four AhR ligands on the total Gst activity and reactive oxygen species (ROS) production in wild-type and AhR-deficient Hepa 1c1c7 cells. Our results showed that Hg2+ and Cu2+, but not Pb2+, significantly induced Gst activity in wild-type cells, whereas all metals induced the Gst activity in AhR-deficient cells. The induction of Gst activity by heavy metals was strongly correlated with an increase in the ROS production in wild-type, but not in AhR-deficient cells. Co-administration of heavy metals with AhR ligands differentially modulated Gst activity, in that co-exposure to Hg2+ plus AhR ligands could be beneficial in protecting against cytotoxicity as demonstrated by the increase in Gst activity with a proportional decrease in ROS production. Whereas co-exposure to Cu2+ plus AhR ligands was more toxic in that a decrease in Gst activity and an increase in oxidative stress of the cell were observed. We concluded that heavy metals differentially modulate the Gst activity through oxidative stress- and AhR-mediated mechanisms.     

Sodium-dependent copper uptake across epithelia: a review of rationale with experimental evidence from gill and intestine

The paper reviews the evidence for apparent sodium-dependent copper (Cu) uptake across epithelia such as frog skin, fish gills and vertebrate intestine. Potential interactions between Na(+) and Cu during transfer through epithelial cells is rationalized into the major steps of solute transfer: (i) adsorption on to the apical/mucosal membrane, (ii) import in to the cell (iii) intracellular trafficking, and (iv) export from the cell to the blood. Interactions between Na(+) and Cu transport are most likely during steps (i) and (ii). These ions have similar mobilities (lambda) in solution (lambda, Na(+), 50.1; Cu(2+), 53.6 cm(2) Int. ohms(-1) equiv(-1)); consequently, Cu(2+) may compete equally with Na(+) for diffusion to membrane surfaces. We present new data on the Na(+) binding characteristics of the gill surface (gill microenvironment) of rainbow trout. The binding characteristics of Na(+) and Cu(2+) to the external surface of trout gills are similar with saturation of ligands at nanomolar concentrations of solutes. At the mucosal/apical membrane of several epithelia (fish gills, frog skin, vertebrate intestine), there is evidence for both a Cu-specific channel (CTR1 homologues) and Cu leak through epithelial Na(+) channels (ENaC). Cu(2+) slows the amiloride-sensitive short circuit current (I(sc)) in frog skin, suggesting Cu(2+) binding to the amiloride-binding site of ENaC. We present examples of data from the isolated perfused catfish intestine showing that Cu uptake across the whole intestine was reduced by 50% in the presence of 2 mM luminal amiloride, with 75% of the overall inhibition attributed to an amiloride-sensitive region in the middle intestine. Removal of luminal Na(+) produced more variable results, but also reduced Cu uptake in catfish intestine. These data together support Cu(2+) modulation of ENaC, but not competitive entry of Cu(2+) through ENaC. However, in situations where external Na(+) is only a few millimoles (fish gills, frogs in freshwater), Cu(2+) leak through ENaC is possible. CTR1 is a likely route of Cu(2+) entry when external Na(+) is higher (e.g. intestinal epithelia). Interactions between Na(+) and Cu ions during intracellular trafficking or export from the cell are unlikely. However, effects of intracellular chloride on the Cu-ATPase or ENaC indicate that Na(+) might indirectly alter Cu flux. Conversely, Cu ions inhibit basolateral Na(+)K(+)-ATPase and may increase [Na(+)](i).     

In Appreciation

Marine animals can induce metallothioneins (MTs) in their responses to exposure to certain trace metals in the environment. MTs generally function as metal storage/detoxification or homeostatic regulation of both essential and non-essential metals. This review discusses the important roles of MTs in metal biokinetics other than metal detoxification and homeostasis in marine animals. Recent studies have revealed the complicated cellular and biochemical processes involving intracellular ligands (cytosolic proteins and insoluble deposits) during metal uptake and elimination. The responses of metal biokinetics to MT induction are metal- and organism-specific. Depending on the different marine animals and metals, all biokinetic parameters such as dissolved metal uptake rate, dietary assimilation efficiency and elimination (efflux) rate can be significantly impacted by MT induction. Among the different metal biokinetic parameters, dietary assimilation efficiency and elimination rate appear to be most impacted by MT induction. MT turnover kinetics can also significantly affect metal uptake kinetics, but again, such influence is also dependent on the organism, particularly its predominant pathway of metal detoxification. Even though the total MT pool in aquatic animals may remain constant, the turnover of MTs, involving MT synthesis and breakdown, can potentially lead to a major change of metal accumulation biokinetics. We propose several issues that need to be further addressed in studying the interaction between MT induction and metal accumulation biokinetics.     

Induced plant uptake and transport of mercury in the presence of sulphur-containing ligands and humic acid

The induced accumulation of mercury (Hg) by plants was investigated for the species Phaseolus vulgaris (Bush bean), Brassica juncea (Indian mustard), and Vicia villosa (Hairy vetch). All plants were grown in modified Hg-contaminated mine tailings and were treated with sulphur-containing ligands to induce Hg accumulation. The effects of varied substrate Hg concentration and humic acid (HA) level on the induced plant-Hg accumulation for B. juncea were examined. Thiosulphate salts (ammonium and sodium) mobilised Hg in the substrates and caused an increase in the Hg concentration of roots and shoots of all tested plant species. Root Hg accumulation was positively correlated to extractable Hg for (NH4)2S2O3-treated B. juncea plants grown in HA-amended substrates. However, shoot Hg translocation for this species was inhibited at 1.25 g HA kg(-1) of substrate. Mercury-thiosulphate complexes could be translocated and accumulated in the upper parts of the plants up to 25 times the Hg concentration in the substrate. We conclude that shoot Hg accumulation in the presence of thiosulphate salts is dependent upon plant species characteristics (e.g. root surface area) and humic acid content.     

Sulfate-reducing bacteria methylate mercury at variable rates in pure culture and in marine sediments

Differences in methylmercury (CH(3)Hg) production normalized to the sulfate reduction rate (SRR) in various species of sulfate-reducing bacteria (SRB) were quantified in pure cultures and in marine sediment slurries in order to determine if SRB strains which differ phylogenetically methylate mercury (Hg) at similar rates. Cultures representing five genera of the SRB (Desulfovibrio desulfuricans, Desulfobulbus propionicus, Desulfococcus multivorans, Desulfobacter sp. strain BG-8, and Desulfobacterium sp. strain BG-33) were grown in a strictly anoxic, minimal medium that received a dose of inorganic Hg 120 h after inoculation. The mercury methylation rates (MMR) normalized per cell were up to 3 orders of magnitude higher in pure cultures of members of SRB groups capable of acetate utilization (e.g., the family Desulfobacteriaceae) than in pure cultures of members of groups that are not able to use acetate (e.g., the family Desulfovibrionaceae). Little or no Hg methylation was observed in cultures of Desulfobacterium or Desulfovibrio strains in the absence of sulfate, indicating that Hg methylation was coupled to respiration in these strains. Mercury methylation, sulfate reduction, and the identities of sulfate-reducing bacteria in marine sediment slurries were also studied. Sulfate-reducing consortia were identified by using group-specific oligonucleotide probes that targeted the 16S rRNA molecule. Acetate-amended slurries, which were dominated by members of the Desulfobacterium and Desulfobacter groups, exhibited a pronounced ability to methylate Hg when the MMR were normalized to the SRR, while lactate-amended and control slurries had normalized MMR that were not statistically different. Collectively, the results of pure-culture and amended-sediment experiments suggest that members of the family Desulfobacteriaceae have a greater potential to methylate Hg than members of the family Desulfovibrionaceae have when the MMR are normalized to the SRR. Hg methylation potential may be related to genetic composition and/or carbon metabolism in the SRB. Furthermore, we found that in marine sediments that are rich in organic matter and dissolved sulfide rapid CH(3)Hg accumulation is coupled to rapid sulfate reduction. The observations described above have broad implications for understanding the control of CH(3)Hg formation and for developing remediation strategies for Hg-contaminated sediments.     

The transfer of cadmium, mercury, methylmercury, and zinc in an intertidal rocky shore food chain

We examined the transfer of cadmium (Cd), inorganic mercury [Hg(II)], methylmercury (MeHg), and zinc (Zn) in an intertidal rocky shore food chain, namely from marine phytoplankton to suspension-feeding rock oysters (Saccostrea cucullata) and finally to predatory whelks Thais clavigera. The uptake of metals from the dissolved phase was also concurrently quantified in the oysters and the whelks. Metal uptake by the oysters was not directly proportional, whereas metal uptake by the whelks was directly proportional to metal concentration in the water. The order of uptake was MeHg>Hg(II)>Zn>Cd, and was much higher in the oysters than in the whelks. The relative uptake of Zn and Cd was comparable between oysters and whelks, whereas MeHg and Hg(II) showed disproportionally higher uptake in oysters than in whelks as compared to Zn and Cd. The assimilation efficiencies (AEs) were in the order of MeHg>Zn>Cd=Hg(II) in oysters, whereas the AEs were highest for MeHg and comparable for Zn, Cd, and Hg(II) in the whelks. Pre-exposure of the oysters to different dissolved concentrations of Cd significantly elevated the AEs of Cd and Hg(II) but not of Zn, in association with the induction of metallothioneins in the oysters. The whelks significantly assimilated Cd and Zn from various prey (barnacles, oysters, mussels, and snails) with contrasting strageties of metal sequestration and storage. There was no significant relationship between the metal AE and the metal partitioning in the soluble fraction (including metallothionein-like proteins, heat stable protein, and organelles). The insoluble fraction of metals was also available for metal assimilation. Our calculations show that the dietary uptake of metals can be dominant in the overall bioaccumulation in the oysters and whelks, and the trophic transfer factor was >1 for all metals. Thus, the four metals have a high potential of being biomagnified in the intertidal rocky shore food chain. MeHg possessed the highest and Hg(II) and Cd the lowest potential of trophic transfer among the four metals considered.