The genetics and biochemistry of mercury resistance

Recent advances in exploring the heavy metal(loid) resistant microbiome

Heavy metal(loid)s exert selective pressure on microbial communities and evolution of metal resistance determinants. Despite increasing knowledge concerning the impact of metal pollution on microbial community and ecological function, it is still a challenge to identify a consistent pattern of microbial community composition along gradients of elevated metal(loid)s in natural environments. Further, our current knowledge of the microbial metal resistome at the community level has been lagging behind compared to the state-of-the-art genetic profiling of bacterial metal resistance mechanisms in a pure culture system. This review provides an overview of the core metal resistant microbiome, development of metal resistance strategies, and potential factors driving the diversity and distribution of metal resistance determinants in natural environments. The impacts of biotic factors regulating the bacterial metal resistome are highlighted. We finally discuss the advances in multiple technologies, research challenges, and future directions to better understand the interface of the environmental microbiome with the metal resistome. This review aims to highlight the diversity and wide distribution of heavy metal(loid)s and their corresponding resistance determinants, helping to better understand the resistance strategy at the community level.

Antimicrobial resistance due to the content of potentially toxic metals in soil and fertilizing products

Potentially toxic metals (PTM), along with PTM-resistant bacteria and PTM-resistance genes, may be introduced into soil and water through sewage systems, direct excretion, land application of biosolids (organic matter recycled from sewage, especially for use in agriculture) or animal manures as fertilizers, and irrigation with wastewater or treated effluents. In this review article, we have evaluated whether the content of arsenic (As), cadmium (Cd), chromium (CrIII + CrVI), copper (Cu), lead (Pb), mercury (Hg), nickel (Ni), and zinc (Zn) in soil and fertilizing products play a role in the development, spreading, and persistence of bacterial resistance to these elements, as well as cross- or co-resistance to antimicrobial agents. Several of the articles included in this review reported the development of resistance against PTM in both sewage and manure. Although PTM like As, Hg, Co, Cd, Pb, and Ni may be present in the fertilizing products, the concentration may be low since they occur due to pollution. In contrast, trace metals like Cu and Zn are actively added to animal feed in many countries. In several studies, several different bacterial species were shown to have a reduced susceptibility towards several PTM, simultaneously. However, neither the source of resistant bacteria nor the minimum co-selective concentration (MCC) for resistance induction are known. Co- or cross-resistance against highly important antimicrobials and critically important antimicrobials were identified in some of the bacterial isolates. This suggest that there is a genetic linkage or direct genetic causality between genetic determinants to these widely divergent antimicrobials, and metal resistance. Data regarding the routes and frequencies of transmission of AMR from bacteria of environmental origin to bacteria of animal and human origin were sparse. Due to the lack of such data, it is difficult to estimate the probability of development, transmission, and persistence of PTM resistance. Abbreviations: PTM: potentially toxic metals; AMR: antimicrobial resistance; ARG: antimicrobial resistance gene; MCC: minimum co-selective concentration; MDR: multidrug resistance; ARB: antimicrobial resistant bacteria; HGT: horizontal gene transfer; MIC: minimum inhibitory concentration.

Gene flow, mobile genetic elements and the recruitment of antibiotic resistance genes into Gram-negative pathogens

Antibiotics were one of the great discoveries of the 20th century. However, resistance appeared even in the earliest years of the antibiotic era. Antibiotic resistance continues to become worse, despite the ever-increasing resources devoted to combat the problem. One of the most important factors in the development of resistance to antibiotics is the remarkable ability of bacteria to share genetic resources via Lateral Gene Transfer (LGT). LGT occurs on a global scale, such that in theory, any gene in any organism anywhere in the microbial biosphere might be mobilized and spread. With sufficiently strong selection, any gene may spread to a point where it establishes a global presence. From an antibiotic resistance perspective, this means that a resistance phenotype can appear in a diverse range of infections around the globe nearly simultaneously. We discuss the forces and agents that make this LGT possible and argue that the problem of resistance can ultimately only be managed by understanding the problem from a broad ecological and evolutionary perspective. We also argue that human activities are exacerbating the problem by increasing the tempo of LGT and bacterial evolution for many traits that are important to humans.

Effects of Hg, CH(3)-Hg, and Temperature on the Expression of Mercury Resistance Genes in Environmental Bacteria

Twenty different bacterial isolates obtained from a mercury-contaminated site in Oak Ridge, Tenn., were grown on plate count agar amended with 25 mug of Hg or 3 mug of CH(3)-Hg (R-Hg) per ml. The total cellular RNA was extracted from each isolate by an acid-guanidine-thiocyanate-phenol-chloroform method. The transcripts of merA and merB were detected and quantitated by Northern (RNA) hybridization. A qualitative assay of mercuric reductase was used to confirm the enzyme activity. Low temperature (4 degrees C) with the presence of Hg (25 mug/ml) significantly increased the net merA transcripts of mid-log-phase cells of six environmental isolates. The net merA transcript production by 18 of the isolates increased when they were grown on 50% plate count broth with 15 mug of Hg per ml, but only 8 isolates showed increased production of merB transcripts. The MICs of Hg and R-Hg for 10 methyl mercury-resistant isolates ranged from 45 to 110 mug of Hg and 0.6 to 4.5 mug of R-Hg per ml. R-Hg was able to induce the expression of merB in 70% of methyl mercury-resistant strains.

Dental Amalgam and Antibiotic- and/or Mercury-resistant Bacteria

Mercury emitted from dental amalgam may select for increased numbers of antibiotic- or mercury-resistant commensal bacteria in patients and increase their risk for bacterial diseases that are resistant to common therapies. We hypothesized that the presence of dental amalgams would increase the level of mercury-, tetracycline-, ampicillin-, erythromycin-, or chloramphenicol-resistant oral and urinary bacteria as compared with levels in children receiving composite fillings. Samples were collected at baseline, 3–6 months after the initial dental treatment, and annually for 7 years of follow-up. There were no statistically significant differences between treatment groups in the numbers of bacteria growing on antibiotic- or mercury-supplemented plates. This study provided no evidence that amalgam fillings on posterior teeth influenced the level of antibiotic- or mercury-resistant oral or urinary bacteria as detected by culture.

Bacterial mercury resistance from atoms to ecosystems

Bacterial resistance to inorganic and organic mercury compounds (HgR) is one of the most widely observed phenotypes in eubacteria. Loci conferring HgR in Gram-positive or Gram-negative bacteria typically have at minimum a mercuric reductase enzyme (MerA) that reduces reactive ionic Hg(II) to volatile, relatively inert, monoatomic Hg(0) vapor and a membrane-bound protein (MerT) for uptake of Hg(II) arranged in an operon under control of MerR, a novel metal-responsive regulator. Many HgR loci encode an additional enzyme, MerB, that degrades organomercurials by protonolysis, and one or more additional proteins apparently involved in transport. Genes conferring HgR occur on chromosomes, plasmids, and transposons and their operon arrangements can be quite diverse, frequently involving duplications of the above noted structural genes, several of which are modular themselves. How this very mobile and plastic suite of proteins protects host cells from this pervasive toxic metal, what roles it has in the biogeochemical cycling of Hg, and how it has been employed in ameliorating environmental contamination are the subjects of this review.

Bioinorganic chemistry in the postgenomic era

Genome sequencing has revolutionized all fields of life sciences. Bioinorganic chemistry is certainly not immune to this influence, which is presenting unprecedented challenges. A new goal for bioinorganic chemistry is the investigation of the linkages between inorganic elements and genomic information. This requires new advancements andor the development of new expertise in fields such as bioinformatics and genetics but also provides a driving force to push forward the exploitation of traditional analytical techniques and spectroscopic tools. The "case study" of metal homeostasis in cells is discussed to provide a flavor of the current evolution of the field.

A new zinc-protein coordination site in intracellular metal trafficking: solution structure of the Apo and Zn(II) forms of ZntA(46-118)

Zinc, a metal ion that functions in a wide variety of catalytic and structural sites in metalloproteins, is shown here to adopt a novel coordination environment in the Escherichia coli transport protein ZntA. The ZntA protein is a P-type ATPase that pumps zinc out of the cytoplasm and into the periplasm. It is physiologically selective for Zn(II) and functions with metalloregulatory proteins in the cell to keep the zinc quota within strict limits. Yet, the N-terminal cytoplasmic domain contains a region that is highly homologous to the yeast Cu(I) metallochaperone Atx1. To investigate how the structure of this region may influence its function, this fragment, containing residues 46-118, has been cloned out of the gene and overexpressed. We report here the solution structure of this fragment as determined by NMR. Both the apo and Zn(II)-ZntA(46-118) structures have been determined. It contains a previously unknown protein coordination site for zinc that includes two cysteine residues, Cys59 and Cys62, and a carboxylate residue, Asp58. The solvent accessibility of this site is also remarkably high, a feature that increasingly appears to be a characteristic of domains of heavy metal ion transport proteins. The participation of Asp58 in this ZntA metal ion binding site may play an important role in modulating the relative affinities and metal exchange rates for Zn(II)/Pb(II)/Cd(II) as compared with other P-type ATPases, which are selective for Cu(I) or Ag(I).

Selectivity in heavy metal- binding to peptides and proteins

The metal-binding affinities and three-dimensional structures of three synthetic 18-residue peptides with sequences derived from that of the highly conserved metal-binding motif MXCXXC found in many heavy metal-binding proteins were determined. A change in register of the cysteines and alanines of the sequence from the periplasmic mercury-binding protein, MerP, i.e., CAAC, CACA, and CCAA, affects the specificity of metal binding, in particular, the peptide with vicinal cysteines binds only mercury. The three-dimensional structures of the mercury-bound forms of the three peptides determined in solution by NMR spectroscopy peptides differ considerably, even though they are all linear bicoordinate complexes. The three-dimensional structure of the peptide with CAAC bound to Cd(II) demonstrates that the metal-binding loop is malleable enough to accommodate modes of coordination other than linear bicoordinate.

Solution structure of the N-terminal domain of a potential copper-translocating P-type ATPase from Bacillus subtilis in the apo and Cu(I) loaded states

A putative partner of the already characterized CopZ from Bacillus subtilis was found, both proteins being encoded by genes located in the same operon. This new protein is highly homologous to eukaryotic and prokaryotic P-type ATPases such as CopA, Ccc2 and Menkes proteins. The N-terminal region of this protein contains two soluble domains constituted by amino acid residues 1 to 72 and 73 to 147, respectively, which were expressed both separately and together. In both cases only the 73-147 domain is folded and is stable both in the copper(I)-free and in the copper(I)-bound forms. The folded and unfolded state is monitored through the chemical shift dispersion of 15N-HSQC spectra. In the absence of any structural characterization of CopA-type proteins, we determined the structure of the 73-147 domain in the 1-151 construct in the apo state through 1H, 15N and 13C NMR spectroscopies. The structure of the Cu(I)-loaded 73-147 domain has been also determined in the construct 73-151. About 1300 meaningful NOEs and 90 dihedral angles were used to obtain structures at high resolution both for the Cu(I)-bound and the Cu(I)-free states (backbone RMSD to the mean 0.35(+/-0.06) A and 0.39(+/-0.07) A, respectively). The structural assessment shows that the structures are accurate. The protein has the typical betaalpha(betabeta)alphabeta folding with a cysteine in the C-terminal part of helix alpha1 and the other cysteine in loop 1. The structures are similar to other proteins involved in copper homeostasis. Particularly, between BsCopA and BsCopZ, only the charges located around loop 1 are reversed for BsCopA and BsCopZ, thus suggesting that the two proteins could interact one with the other. The variability in conformation displayed by the N-terminal cysteine of the CXXC motif in a number of structures of copper transporting proteins suggests that this may be the cysteine which binds first to the copper(I) carried by the partner protein.

Metallochaperones and metal-transporting ATPases: a comparative analysis of sequences and structures

A comparative structural genomic analysis of a new class of metal-trafficking proteins can provide insights into the intracellular chemistry of reactive cofactors such as copper and zinc. Starting from the sequences of the metallochaperone Atx1 and from the first soluble domain of the copper-transporting ATPase Ccc2, both from yeast, a search on the available genomes was performed using a homology criterion and a metal-binding motif x'-x"-C-x'''-x''''-C. By limiting ourselves to 20% identity with any of the proteins found, several soluble copper-transport proteins were identified, as well as soluble domains of membrane-bound ATPases. Structural models were calculated using high-resolution solution structures as templates, and the models were validated using statistical and energy criteria. Residue conservation and substitution have been interpreted and discussed in terms of structure-function relationship. The potential energy surfaces have been analyzed in terms of protein-protein interactions. We find that metallochaperones and their physiological partner ATPases from several phylogenetic kingdoms recognize one another, via an interplay of electrostatics, hydrogen bonding, and hydrophobic interactions, in a manner that precisely orients the metal-binding side chains for rapid metal transfer between otherwise tight binding sites. Finally, other putative metal-transport proteins are mentioned that have low homology and/or a different metal-binding consensus motif and that appear to use similar structures for recognition and transfer. This analysis highlights the wealth and the complexity of the field.

Solution structure of the Cu(I) and apo forms of the yeast metallochaperone, Atx1

The (1)H NMR solution structure of the Cu(I)-bound form of Atx1, a 73-amino acid metallochaperone protein from the yeast Saccharomyces cerevisiae, has been determined. Ninety percent of the (1)H and 95% of the (15)N resonances were assigned, and 1184 meaningful NOEs and 42 (3)J(HNH)(alpha) and 60 (1)J(HN) residual dipolar couplings provided a family of structures with rmsd values to the mean structure of 0.37 +/- 0.07 A for the backbone and 0.83 +/- 0.08 A for all heavy atoms. The structure is constituted by four antiparallel beta strands and two alpha helices in a betaalphabetabetaalphabeta fold. Following EXAFS data [Pufahl, R., Singer, C. P., Peariso, K. L., Lin, S.-J., Schmidt, P. J., Fahrni, C. J., Cizewski Culotta, V., Penner-Hahn, J. E., and O'Halloran, T. V. (1997) Science 278, 853-856], a copper ion can be placed between two sulfur atoms of Cys15 and Cys18. The structure of the reduced apo form has also been determined with similar resolution using 1252 meaningful NOEs (rmsd values for the family to the mean structure are 0.67 +/- 0.12 A for the backbone and 1.00 +/- 0.12 A for all heavy atoms). Comparison of the Cu(I) and apo conformations of the protein reveals that the Cu(I) binding cysteines move from a buried site in the bound metal form to a solvent-exposed conformation on the surface of the protein after copper release. Furthermore, copper release leads to a less helical character in the metal binding site. Comparison with the Hg(II)-Atx1 solid-state structure [Rosenzweig, A. C., Huffman, D. L., Hou, M. Y., Wernimont, A. K., Pufahl, R. A., and O'Halloran, T. V. (1999) Structure 7, 605-617] provides insights into the copper transfer mechanism, and a pivotal role for Lys65 in the metal capture and release process is proposed.

The merG gene product is involved in phenylmercury resistance in Pseudomonas strain K-62

The physiological function of a new gene, hereby designated merG, located between merA and merB on the broad-spectrum mer operon of Pseudomonas strain K-62 plasmid pMR26 was investigated. The 654-bp merG gene encodes a protein with a canonical leader sequence at its N terminus. The processing of the signal peptide of this protein was dose-dependently inhibited by sodium azide, a potent inhibitor of protein export. These results suggest that the mature MerG protein (ca. 20 kDa) may be located in the periplasm. Deletion of the merG gene from the broad-spectrum mer operon of pMR26 had no effect on the inorganic mercury resistance phenotype, but rendered the bacterium more sensitive to phenylmercury than its isogenic wild-type strain. Escherichia coli cells bearing pMU29, which carries a deletion of the merG gene, took up significantly more phenylmercury than the bacteria with the intact plasmid pMRA17. When the merG gene in a compatible plasmid was transformed into the E. coli strain carrying pMU29, the high uptake of and high sensitivity to phenylmercury were almost completely restored to their original levels. These results demonstrate that the merG gene is involved in phenylmercury resistance, presumably by reducing in-cell permeability to phenylmercury.

Antibiotic resistance in oral/respiratory bacteria

In the last 20 years, changes in world technology have occurred which have allowed for the rapid transport of people, food, and goods. Unfortunately, antibiotic residues and antibiotic-resistant bacteria have been transported as well. Over the past 20 years, the rise in antibiotic-resistant gene carriage in virtually every species of bacteria, not just oral/respiratory bacteria, has been documented. In this review, the main mechanisms of resistance to the important antibiotics used for treatment of disease caused by oral/respiratory bacteria--including beta-lactams, tetracycline, and metronidazole--are discussed in detail. Mechanisms of resistance for macrolides, lincosamides, streptogramins, trimethoprim, sulfonamides, aminoglycosides, and chloramphenicol are also discussed, along with the possible role that mercury resistance may play in the bacterial ecology.

Repeated fed-batch operations for microbial detoxification of mercury using wild-type and recombinant mercury-resistant bacteria

A wild-type mercury-resistant strain Pseudomonas aeruginosa PU21 (Rip64), and an Escherichia coli PWS1 strain genetically engineered to harbor mercury resistance were examined for their capacity to detoxify soluble mercuric ions with repeated fed-batch operations. The specific mercury detoxification activity for the two strains at different initial mercury concentrations was determined by resting-cell experiments. The fed-batch operations were conducted with different initial culture volumes (Vo), inoculum sizes (Xo), and different mercury feeding rates (FHg) to investigate the effects of those operation parameters on the performance of mercury detoxification. The results showed that the wild-type and the recombinant strains had an optimal specific activity of 5 x 10(-7) and 8 x 10(-8) micrograms cell-1 h-1, respectively. In fed-batch operation for P. aeruginosa PU21, under the conditions of Vo = 400 ml and Xo = 4.5-4.8 x 10(9) cells ml-1 the overall mercury detoxification efficiency (eta) for FHg = 16.9 mg Hg h-1 was 5.26 mg Hg l-1 h-1, nearly 35% higher than that for a lower FHg (11.7 mg Hg h-1). Among the three initial culture volumes examined in this study, the highest eta (5.60 mg Hg l-1 h-1) was obtained when Vo = 1200 ml and FHg = 16.9 mg Hg h-1. It was also found that an inoculum size higher than 4.0 x 10(9) cells ml-1 enabled a stable fed-batch operation, while as the inoculum was reduced to around 1.6 x 10(9) cells ml-1, the mercury feeding caused severe cell death, leading to an unsuccessful fed-batch operation. In the fed-batch operation for E. coli PWS1 strain with Vo = 1200 ml and FHg = 16.9 mg Hg h-1, the mercury detoxification efficiency was 3.07 mg Hg l-1 h-1, only 54% of that for the wild-type P. aeruginosa PU21 strain under the same operating conditions. It was also noticed that the operation with E. coli PWS1 became less efficient at the second fed-batch cycle due to plasmid instability of the recombinant strain.

Antibiotic resistance mechanisms in bacteria of oral and upper respiratory origin

Over the past 20 years, antibiotic resistance has increased in virtually every species of bacteria examined. In this paper, the main mechanisms of antibiotic resistance currently known for antibiotics used for treatment of disease caused by oral and upper respiratory bacteria will be reviewed, with an emphasis on the most commonly used antibiotics. The possible role that mercury, which is released from silver amalgams, plays in the oral/respiratory bacterial ecology is also discussed, as it relates to possible selection of antibiotic resistant bacteria.

Structures of the reduced and mercury-bound forms of MerP, the periplasmic protein from the bacterial mercury detoxification system

Bacteria carrying plasmids with the mer operon, which encodes the proteins responsible for the bacterial mercury detoxification system, have the ability to transport Hg(II) across the cell membrane into the cytoplasm where it is reduced to Hg(0). This is significant because metallic mercury is relatively nontoxic and volatile and thus can be passively eliminated. The structures of the reduced and mercury-bound forms of merP, the periplasmic protein, which binds Hg(II) and transfers it to the membrane transport protein merT, have been determined in aqueous solution by multidimensional NMR spectroscopy. The 72-residue merP protein has a betaalpha betabeta alphabeta fold with the two alpha helices overlaying a four-strand antiparallel beta sheet. Structural differences between the reduced and mercury-bound forms of merP are localized to the metal binding loop containing the consensus sequence GMTCXXC. The structure of the mercury-bound form of merP shows that Hg(II) is bicoordinate with the Cys side chain ligands, and this is confirmed by the chemical shift frequency of the 199Hg resonance.

Distribution, diversity and evolution of the bacterial mercury resistance (mer) operon

Mercury and its compounds are distributed widely across the earth. Many of the chemical forms of mercury are toxic to all living organisms. However, bacteria have evolved mechanisms of resistance to several of these different chemical forms, and play a major role in the global cycling of mercury in the natural environment. Five mechanisms of resistance to mercury compounds have been identified, of which resistance to inorganic mercury (HgR) is the best understood, both in terms of the mechanisms of resistance to mercury and of resistance to heavy metals in general. Resistance to inorganic mercury is encoded by the genes of the mer operon, and can be located on transposons, plasmids and the bacterial chromosome. Such systems have a worldwide geographical distribution, and furthermore, are found across a wide range of both Gram-negative and Gram-positive bacteria from both natural and clinical environments. The presence of mer genes in bacteria from sediment cores suggest that mer is an ancient system. Analysis of DNA sequences from mer operons and genes has revealed genetic variation both in operon structure and between individual genes from different mer operons, whilst analysis of bacteria which are sensitive to inorganic mercury has identified a number of vestigial non-functional operons. It is hypothesised that mer, due to its ubiquity with respect to geographical location, environment and species range, is an ancient system, and that ancient bacteria carried genes conferring resistance to mercury in response to increased levels of mercury in natural environments, perhaps resulting from volcanic activity. Models for the evolution of both a basic mer operon and for the Tn21-related family of mer operons and transposons are suggested. The study of evolution in bacteria has recently become dominated by the generation of phylogenies based on 16S rRNA genes. However, it is important not to underestimate the roles of horizontal gene transfer and recombinational events in evolution. In this respect mer is a suitable system for evaluating phylogenetic methods which incorporate the effects of horizontal gene transfer. In addition, the mer operon provides a model system in the study of environmental microbiology which is useful both as an example of a genotype which is responsive to environmental pressures and as a generic tool for the development of new methodology for the analysis of bacterial communities in natural environments.

The mercury resistance operon of the IncJ plasmid pMERPH exhibits structural and regulatory divergence from other Gram-negative mer operons

The bacterial mercury resistance determinant carried on the IncJ plasmid pMERPH has been characterized further by DNA sequence analysis. From the sequence of a 4097 bp Bg/II fragment which confers mercury resistance, it is predicted that the determinant consists of the genes merT, merP, merC and merA. The level of DNA sequence similarity between these genes and those of the mer determinant of Tn21 was between 56 center dot 4 and 62 center dot 4%. A neighbour-joining phylogenetic tree of merA gene sequences was constructed which suggested that pMERPH bears the most divergent Gram-negative mer determinant characterized to date. Although the determinant from pMERPH has been shown to be inducible, no regulatory genes have been found within the Bg/II fragment and it is suggested that a regulatory gene may be located elsewhere on the plasmid. The cloned determinant has been shown to express mercury resistance constitutively. Analysis of the pMERPH mer operator/promoter (O/P) region in vivo has shown constitutive expression from the mer PTCPA promoter, which could be partially repressed by the presence of a trans-acting MerR protein from a Tn21-like mer determinant. This incomplete repression of mer PTCPA promoter activity may be due to the presence of an extra base between the -35 and -10 sequences of the promoter and/or to variation in the MerR binding sites in the O/P region. Expression from the partially repressed mer PTCPA promoter could be restored by the addition of inducing levels of Hg2+ ions. Using the polymerase chain reaction with primers designed to amplify regions in the merP and merA genes, 1 center dot 37 kb pMERPH-like sequences have been amplified from the IncJ plasmid R391, the environmental isolate SE2 and from DNA isolated directly from non-cultivated bacteria in River Mersey sediment. This suggests that pMERPH-like sequences, although rare, are nevertheless persistent in natural environments.

Development of biosensors for the detection of mercury and copper ions

The development of genetically engineered biosensors for copper and mercury ions is described. The biosensors have been constructed by fusing thelux or light emitting genes fromVibrio fischeri with genetic regulating elements that respond to copper ions or mercury ions, derived respectively fromEscherichia coli andSerratia marcescens. The fusions were placed intoE. coli cells which then emitted light in response to copper or mercury ions. Data is presented describing the sensitivity, specificity, and dynamic range of the biosensors to their respective target metal ions. A preliminary description of experiments is provided indicating how these biosensors might be used to investigate the bioavailability of mercury and copper ions in environmental samples.

The sequence of the mer operon of pMER327/419 and transposon ends of pMER327/419, 330 and 05

Three different, independently isolated mercury-resistance-conferring plasmids, pMER327/419, pMER330 and pMER05, from cultures originating from the river Mersey (UK), contain identical regulatory merR genes and transposon ends. The mer determinant from pMER327/419 contains an additional potential ORF (ORF F) located between merP and merA when compared with the archetypal Tn501. Although these plasmids confer narrow-spectrum resistance (resistance to Hg2+, but not organomercurials) their merR genes encode a potential organomercurial-sensing protein. Transposition of the mer of pMER05 into plasmid RP4 was demonstrated and, as with Tn502 and Tn5053, insertion occurred at a specific region. The sequence of pMER05 is identical at the 'left' and 'right' termini and across merR to Tn5053, which was independently isolated from the chromosome of a Xanthomonas sp. bacteria from the Khaidarkan mercury mine in Kirgizia, former Soviet Union [Kholodii et al., J. Mol. Biol. 230 (1993a) 1103-1107]. The transpositional unit of pMER05 is, like that of Tn5053, bounded by DNA homologous to the imperfect 25-bp inverted repeats (IR) of the In2 integron, which brackets antibiotic-resistance cassettes in Tn21 subgroup transposons. At one end of the transposable element, and internal to the In2-like IR, is a 38-bp IR which closely resembles the IR that bounds Tn21.

High levels of multiple metal resistance and its correlation to antibiotic resistance in environmental isolates of Acinetobacter

Forty strains of Acinetobacter were isolated from different environmental sources. All the strains were classified into four genospecies, i.e., A. baumannii (33 isolates), A. calcoaceticus (three isolates), A. junii (three isolates) and A. genospecies3 (one isolate). Susceptibility of these 40 strains to salts of 20 heavy metals and 18 antibiotics was tested by the agar dilution method. All environmental isolates of Acinetobacter were resistant to multiple metal ions (minimum 13 metal ions) while all but one of the strains were resistant to multiple antibiotics (minimum four antibiotics). The maximum number of strains were found to be sensitive to mercury (60% strains) while all strains were resistant to copper, lead, boron and tungsten even at 10 mM concentration. Salts of these four metal ions may be added to the growth medium to facilitate selective isolation of Acinetobacter. Rifampicin and nalidixic acid were the most toxic antibiotics, inhibiting 94.5 and 89.5% of the acinetobacters, respectively. A. genospecies3 was found to be the most resistant species, tolerating high concentrations of all the 20 metal ions and also to a greater number of antibiotics than any other species of Acinetobacter tested. An inhibitory concentration (10 mM) of Ni(2+) and Zn(2+) was observed to inhibit the growth of all of the clinical isolates but allowed the growth of the environmental isolates, facilitating the differentiation between pathogenic and non-pathogenic acinetobacters.

Regulation of the Staphylococcus aureus plasmid pI258 mercury resistance operon

Experiments involving fusion between the Staphylococcus aureus plasmid pI258-encoded mer operon and the reporter gene beta-lactamase, mutational analysis, and trans-complementation studies have shown that the merR gene of pI258, which shows DNA sequence similarity with known merR genes from other bacteria, regulates the expression of the mer operon in vivo. The merR gene product is a trans-acting protein that activates mer operon transcription in the presence of the inducers Hg2+ and Cd2+. A glutathione-S-transferase-MerR fusion protein specifically bound and protected a 27-nucleotide operator sequence from DNase I digestion. This operator sequence is highly homologous with mer operator sequences of other known systems.

Synthesis and degradation of the mRNA of the Tn21 mer operon

The mercury resistance locus encoded by Tn21 on the monocopy IncFII plasmid R100 (merTn21) consists of a metal-responsive activator/repressor, merR, which controls initiation of a polycistronic message that includes genes for the uptake (merTPC) and reduction (merA) of Hg2+ and merD, which may also play a minor regulatory role. Comparison of the relative abundance of the 5' and 3' ends of the merTPCAD transcript revealed a strong transcriptional gradient in the operon, consistent with previous observations of lower relative abundance of the more promoter-distal gene products. In vivo mRNA degradation rates varied only slightly for the different genes: however, the rates of mRNA synthesis varied considerably from the beginning to the end of the operon. Specifically, mRNA corresponding to the promoter-proximal genes, merTPC, achieved a maximum in vivo synthesis rate between 60 and 120 seconds after induction; this rate was maintained for approximately ten minutes. In contrast, the synthesis rates of mRNA corresponding to the promoter-distal genes merA and merD, were initially fivefold lower than the rates of the promoter-proximal genes for the first five minutes after induction, and then rose gradually to approximately 50% of the merTPC synthesis rates. These data suggested that early after induction only 20% of the transcripts initiating at merT proceed beyond merC. At later times after induction approximately 50% of the transcripts proceed beyond merC. Nuclease end mapping did not reveal any discrete termination events in the merPCA region, thus, premature termination may occur at many sites.

Gene regulation of plasmid- and chromosome-determined inorganic ion transport in bacteria

Regulation of chromosomally determined nutrient cation and anion uptake systems shows important similarities to regulation of plasmid-determined toxic ion resistance systems that mediate the outward transport of deleterious ions. Chromosomally determined transport systems result in accumulation of K+, Mg2+, Fe3+, Mn2+, PO4(3-), SO4(2-), and additional trace nutrients, while bacterial plasmids harbor highly specific resistance systems for AsO2-, AsO4(3-), CrO4(2-), Cd2+, Co2+, Cu2+, Hg2+, Ni2+, SbO2-, TeO3(2-), Zn2+, and other toxic ions. To study the regulation of these systems, we need to define both the trans-acting regulatory proteins and the cis-acting target operator DNA regions for the proteins. The regulation of gene expression for K+ and PO4(3-) transport systems involves two-component sensor-effector pairs of proteins. The first protein responds to an extracellular ionic (or related) signal and then transmits the signal to an intracellular DNA-binding protein. Regulation of Fe3+ transport utilizes the single iron-binding and DNA-binding protein Fur. The MerR regulatory protein for mercury resistance both represses and activates transcription. The ArsR regulatory protein functions as a repressor for the arsenic and antimony(III) efflux system. Although the predicted cadR regulatory gene has not been identified, cadmium, lead, bismuth, zinc, and cobalt induce this system in a carefully regulated manner from a single mRNA start site. The cadA Cd2+ resistance determinant encodes an E1(1)-1E2-class efflux ATPase (consisting of two polypeptides, rather than the one earlier identified). Cadmium resistance is also conferred by the czc system (which confers resistances to zinc and cobalt in Alcaligenes species) via a complex efflux pump consisting of four polypeptides. These two cadmium efflux systems are not otherwise related. For chromate resistance, reduced cellular accumulation is again the resistance mechanism, but the regulatory components are not identified. For other toxic heavy metals (with few exceptions), there exist specific plasmid resistances that remain relatively terra incognita for future exploration of bioinorganic molecular genetics and gene regulation.

C-terminal cysteines of Tn501 mercuric ion reductase

Mercuric ion reductase (MerA) catalyzes the reduction of Hg(II) to Hg(0) as the last step in the bacterial mercury detoxification pathway. A member of the flavin disulfide oxidoreductase family, MerA contains an FAD prosthetic group and redox-active disulfide in its active site. However, the presence of these two moieties is not sufficient for catalytic Hg(II) reduction, as other enzyme family members are potently inhibited by mercurials. We have previously identified a second pair of active site cysteines (Cys558 Cys559 in the Tn501 enzyme) unique to MerA, that are essential for high levels of mercuric ion reductase activity [Moore, M. J., & Walsh, C. T. (1989) Biochemistry 28, 1183; Miller, S. M., et al. (1989) Biochemistry 28, 1194]. In this paper, we have examined the individual roles of Cys558 and Cys559 by site-directed mutagenesis of each to alanine. Phenotypic analysis indicates that both merA mutations result in a total disruption of the Hg(II) detoxification pathway in vivo, while characterization of the purified mutant enzymes in vitro shows each to have differential effects on catalytic function. Compared to wild-type enzyme, the C558A mutant shows a 20-fold reduction in kcat and a 10-fold increase in Km, for an overall decrease in catalytic efficiency of 200-fold in kcat/Km. In contrast, mutation of Cys559 to alanine results in less than a 2-fold reduction in kcat and an increase in Km of only 4-5 fold for an overall decrease in catalytic efficiency of only ca. 10-fold in vitro. From these results, it appears that Cys558 plays a more important role in forming the reducible complex with Hg(II), while both Cys558 and Cys559 seem to be involved in efficient scavenging (i.e., tight binding) of Hg(II).

Bacterial resistances to inorganic mercury salts and organomercurials

Environmental and clinical isolates of mercury-resistant (resistant to inorganic mercury salts and organomercurials) bacteria have genes for the enzymes mercuric ion reductase and organomercurial lyase. These genes are often plasmid-encoded, although chromosomally encoded resistance determinants have been occasionally identified. Organomercurial lyase cleaves the C-Hg bond and releases Hg(II) in addition to the appropriate organic compound. Mercuric reductase reduces Hg(II) to Hg(O), which is nontoxic and volatilizes from the medium. Mercuric reductase is a FAD-containing oxidoreductase and requires NAD(P)H and thiol for in vitro activity. The crystal structure of mercuric ion reductase has been partially solved. The primary sequence and the three-dimensional structure of the mercuric reductase are significantly homologous to those of other flavin-containing oxidoreductases, e.g., glutathione reductase and lipoamide dehydrogenase. The active site sequences are the most conserved region among these flavin-containing enzymes. Genes encoding other functions have been identified on all mercury ion resistance determinants studied thus far. All mercury resistance genes are clustered into an operon. Hg(II) is transported into the cell by the products of one to three genes encoded on the resistance determinants. The expression of the operon is regulated and is inducible by Hg(II). In some systems, the operon is inducible by both Hg(II) and some organomercurials. In gram-negative bacteria, two regulatory genes (merR and merD) were identified. The (merR) regulatory gene is transcribed divergently from the other genes in gram-negative bacteria. The product of merR represses operon expression in the absence of the inducers and activates transcription in the presence of the inducers. The product of merD coregulates (modulates) the expression of the operon. Both merR and merD gene products bind to the same operator DNA. The primary sequence of the promoter for the polycistronic mer operon is not ideal for efficient transcription by the RNA polymerase. The -10 and -35 sequences are separated by 19 (gram-negative systems) or 20 (gram-positive systems) nucleotides, 2 or 3 nucleotides longer than the 17-nucleotide optimum distance for binding and efficient transcription by the Escherichia coli sigma 70-containing RNA polymerase. The binding site of MerR is not altered by the presence of Hg(II) (inducer). Experimental data suggest that the MerR-Hg(II) complex alters the local structure of the promoter region, facilitating initiation of transcription of the mer operon by the RNA polymerase. In gram-positive bacteria MerR also positively regulates expression of the mer operon in the presence of Hg(II).

The merR regulatory gene in Thiobacillus ferrooxidans is spaced apart from the mer structural genes

Two distinct merR genes, which regulate expression of the mercuric ion resistance gene (mer), of Thiobacillus ferrooxidans strain E-15 have been cloned, sequenced and termed merR1 and merR2. As a result of gene walking around two merR genes, it was found that these two genes were quite close in distance. The nucleotide sequence of the region (5,001 base pairs; PstI-EcoRI fragment) containing the merR genes was determined. Between the two merR genes, there were five potential open reading frames (ORFs). Two of these were identified as merC genes, and the other three as ORFs 1 to 3. ORFs 1 to 3 show significant homology to merA, tnsA from transposon Tn7, and merA, respectively. Both merR genes consist of a 408 bp ORF coding for 135 amino acids. Their gene products, MerR1 and MerR2, differed at three amino acid positions, and shared 56-57% and 32-38% identity with the MerRs from other Gram-negative and Gram-positive bacteria, respectively. Competitive primer extension analysis revealed that both regulatory genes were expressed in the host cells. These merR genes were located more than 6 kb from either end of the mer structural genes (merC-merA). This is the first example of merR being separated from the mer structural genes. The two merC genes, each of which coded for a 140-amino-acid protein, appeared to be functionally active because Escherichia coli cells carrying these merC genes on plasmid vectors showed hypersensitivity to HgCl2. However, ORFs 1 and 3, which were homologous to merA, seemed to be inactive both structurally and enzymatically. The gene arrangement in this region took on a mirror image, with the truncated tnsA as the symmetrical centre. It is suggested that the Tn7-like factor may have participated in gene duplication events of the mer region, and in its chromosomal integration.

Novel mercury resistance determinants carried by IncJ plasmids pMERPH and R391

HgCl2 resistance (Hgr) in a strain of Pseudomonas putrefaciens isolated from the River Mersey was identified as plasmid-borne by its transfer to Escherichia coli in conjugative matings. This plasmid, pMERPH, could not be isolated and was incompatible with the chromosomally integrated IncJ Hgr plasmid R391. pMERPH and R391 both express inducible, narrow-spectrum mercury resistance and detoxify HgCl2 by volatilization. The cloned mer determinants from pMERPH (pSP100) and R391 (pSP200) have very similar restriction maps and express identical polypeptide products. However, these features show distinct differences from those of the Tn501 family of mer determinants. pSP100 and pSP200 failed to hybridize at moderate stringency to merRTPA and merC probes from Tn501 and Tn21, respectively. We conclude that the IncJ mer determinants are only distantly related to that from Tn501 and its closely homologous relatives and that it identifies a novel sequence which is relatively rare in bacteria isolated from natural environments.

Distribution of DNA Sequences Encoding Narrow- and Broad-Spectrum Mercury Resistance

The distribution of DNA sequences homologous with three mer genes was determined in unselected and mercury-resistant water and sediment isolates. The maximum proportions of unselected bacterial isolates containing DNA hybridizing with the 358merA, 358merB, and 501merR probes, derived from gram-negative organisms, were 93.8, 21, and 100%, respectively. Up to 53.3% of mercury chloride-resistant isolates and 54% of methylmercury hydroxide-resistant isolates did not contain DNA homologous with 358merA or 358merB, respectively. Hybridizations performed at high and low stringencies demonstrated that divergence of the merA gene accounted for many of the mercury-resistant but probe-negative isolates. Sixteen mercury-resistant Bacillus spp. isolated from the least contaminated site all contained DNA homologous with 258merA, originally from a gram-positive organism, but only four hybridized weakly with 358merA. The results demonstrate the wide distribution of mercury resistance genes but, because of the diversity of genetic determinants, highlight the importance of using multiple detection techniques and gene probes derived from a variety of origins for such studies.

Mercury resistance determined by a self-transmissible plasmid in Bacillus cereus 5

Inducible mercuric reductase activity in Bacillus cereus 5 was plasmid-encoded. Plasmid analysis revealed three plasmids with molecular masses of 2.6, 5.2 and 130 MDa. A mating system permitted transfer of the resistance determinant among strains of B. cereus and B. thuringiensis. Transfer of mercury resistance from B. cereus 5 to B. cereus 569 and B. thuringiensis occurred during mixed culture incubation on agar surfaces. The 130-MDa plasmid (pGB130) was responsible for transfer; frequencies ranged from 10(-5) to 10(-4). B. cereus 569 transconjugants inheriting pGB130 were also effective donors. High transfer frequencies and the finding that cell-free filtrates of donor cultures were ineffective in mediating transfer suggested mercury-resistance transfer was not phage-mediated. Transfer was also insensitive to DNase activity. Further evidence that pGB130 DNA carried the mercury-resistance determinant was transformation of B. cereus 569 by electroporation with pGB130 DNA isolated from B. cereus 5 and a mercury-resistant B. cereus 569 transconjugant. Mercury-resistant transconjugants and transformants exhibited mercuric reductase activity. Plasmid pGB130 also conferred resistance to phenylmercuric acetate.

Mercury operon regulation by the merR gene of the organomercurial resistance system of plasmid pDU1358

The structural basis for induction of the mercury resistance operon with inorganic mercury and with the organomercurial compound phenylmercuric acetate was addressed by DNA sequencing analysis and by lac fusion transcription experiments regulated by merR in trans from broad-spectrum-resistance plasmid pDU1358 (Hg2+ and phenylmercury responding). The lac fusion results were compared with those from a narrow-spectrum-resistance (Hg2+ responding but not phenylmercuric responding) operon and the pDU1358 merR deleted at the 3' end. The nucleotide sequence of the beginning region of the broad-spectrum mer operon of plasmid pDU1358 was determined, including that of the merR gene, the operator-promoter region, the merT and merP genes, and the first 60% of the merA gene. Comparison of this sequence with DNA sequences of narrow-spectrum mer operons from transposon Tn501 and plasmid R100 showed that a major difference occurred in the 3' 29 base pairs of the merR gene, resulting in unrelated C-terminal 10 amino acids. A hybrid mer operon consisting of the merR gene from pDU1358, a hybrid merA gene (determining mercuric reductase enzyme), and lacking the merB gene (determining phenylmercury lyase activity) was inducible by both phenylmercury and inorganic Hg2+. This shows that organomercurial lyase is not needed for induction by organomercurial compounds. A mutant form of pDU1358 merR missing the C-terminal 17 amino acids responded to inorganic Hg2+ but not to phenylmercury. Thus, the C-terminal region of the MerR protein of the pDU1358 mer operon is involved in the recognition of phenylmercury.

Genetic analysis of transcriptional activation and repression in the Tn21 mer operon

Transcription of the Tn21 mercury resistance operon (mer) is controlled by the toxic metal cation Hg(II). This control is mediated by the product of the merR gene, a 144-amino-acid protein which represses transcription of the structural genes (merTPCAD) in the absence of Hg(II) and activates transcription in the presence of Hg(II). We have used a mer-lac transcriptional fusion to obtain regulatory mutants in this metal-responsive system. Some mutants were defective in Hg(II)-induced activation while retaining repression function (a- r+), others were defective in repression but not activation (a+ r-), and some had lost both functions (a- r-). Mutations in three of the four cysteine residues of merR resulted in complete loss of Hg(II)-inducible activation but retention of the repressor function, suggesting that these residues serve as ligands for Hg(II) in the activation process. Other lesions adjacent to or very near these cysteines exhibited severely reduced activation and also retained repressor function. There were two putative helix-turn-helix (HTH) domains in merR, and mutants in each had very different phenotypes. A partially dominant mutation in the more amino-terminal region of the two putative HTH regions resulted in loss of both activation and repression (a- r-), consistent with a role for this region in DNA binding. Mutations in the more centrally located HTH region resulted only in loss of Hg(II)-induced activation (a- r+). Lesions in the central and in the carboxy-terminal regions of merR exhibited both Hg(II)-independent and Hg(II)-dependent transcriptional activation, suggesting that elements important in the activation mechanism may be widely distributed in this relatively small protein. The sole cis-acting mutant obtained with this operon fusion strategy, a down-promoter mutation, lies in a highly conserved base in the -35 region of the merTPCAD promoter.

DNA sequence analysis of bacterial toxic heavy metal resistances

Bacterial plasmids have genes that confer highly specific resistances to As, Bi, Cd, Cu, Cr, Hg, Pb, Te, Zn, and other toxic heavy metals. For each toxic cation or anion, generally a different resistance system exists, and these systems may be "linked" together on multiple resistance plasmids. For Cd2+, AsO2-, AsO4(3)-, Hg2+, and organomercurials, DNA sequence analysis has supplemented direct physiological and biochemical experiments to produce sophisticated understanding. The cadA ATPase of S. aureus plasmids is a 727 amino acid membrane ATPase that pumps Cd2+ from the cells as rapidly as it is accumulated. This polypeptide is related by sequence to other cation translocating ATPases, including the membrane K+ ATPases of Escherichia coli and Streptococcus faecalis, the H+ ATPases of yeast and Neurospora, the Na+/K+ ATPases of vertebrate animals, and the Ca2+ ATPases of rabbit muscle. The conserved residues include the aspartyl residue that is phosphorylated, the lysine involved in ATP binding, and the proline within a membrane translocating region. The arsenate and arsenite translocating ATPase consists of 3 polypeptides (from DNA sequence analysis), including a recognizable ATP binding protein (arsA), an integral membrane protein (arsB gene), and a substrate specificity subunit (arsC gene). Inorganic mercury and organomercurial degradation is carried out by a series of about 6 polypeptides, including 2 soluble intracellular enzymes (organomercurial lyase and mercuric reductase). The latter is related by sequence and function to glutathione reductase and lipoamide dehydrogenase of prokaryotes and eukaryotes. These enzymes are dimeric, FAD-containing, NAD(P)H-dependent oxidoreductases. Other recognizable polypeptides in the mer system include a DNA-binding regulatory protein from the merR gene and a Hg2+ transport system consisting of a periplasmic Hg2(+)-binding protein (merP gene) and a membrane protein (merT gene) in gram negative systems.

Translation of merD in Tn21

All four sequenced examples of the mercury resistance (mer) operon of gram-negative bacteria have a promoter-distal reading frame, merD, whose removal has little effect on the resistance phenotype and whose translation has not previously been observed. Using merD-lacZ protein fusions, we show that merD is translated. However, Hg(II)-induced merD expression, as measured by beta-galactosidase activity and immunoblotting, is 10- to 15-fold lower than that of fusions to the gene immediately preceding it, merA.

Cell-free mercury volatilization activity from three marine caulobacter strains

Three mercury-resistant marine Caulobacter strains showed an inducible mercury volatilization activity. Cell-free mercury volatilization (mercuric reductase) from these three marine Caulobacter strains was characterized and compared with enzyme activities determined by plasmids of Escherichia coli and Staphylococcus aureus. The temperature sensitivity of the Caulobacter mercuric reductase was greater than that of mercuric reductase from other gram-negative sources. Cell-free enzyme activity required NADH or NADPH, with NADPH functioning much better at lower concentrations than NADH. The Km for the Caulobacter enzyme was 4 microM Hg2+. Ag+ was a competitive inhibitor of Caulobacter mercuric reductase (Ki = 0.2 microM Ag+), as with previously studied enzymes. Arsenite was a noncompetitive inhibitor of the Caulobacter enzyme with a Ki of 75 microM AsO2-.

Nucleotide sequence of a chromosomal mercury resistance determinant from a Bacillus sp. with broad-spectrum mercury resistance

A 13.5-kilobase HindIII fragment, bearing an intact mercury resistance (mer) operon, was isolated from chromosomal DNA of broad-spectrum mercury-resistant Bacillus sp. strain RC607 by using as a probe a clone containing the mercury reductase (merA) gene. The new clone, pYW33, expressed broad-spectrum mercury resistance both in Escherichia coli and in Bacillus subtilis, but only in B. subtilis was the mercuric reductase activity inducible. Sequencing of a 1.8-kilobase mercury hypersensitivity-producing fragment revealed four open reading frames (ORFs). ORF1 may code for a regulatory protein (MerR). ORF2 and ORF4 were associated with cellular transport function and the hypersensitivity phenotype. DNA fragments encompassing the merA and the merB genes were sequenced. The predicted Bacillus sp. strain RC607 MerA (mercuric reductase) and MerB (organomercurial lyase) were similar to those predicted from Staphylococcus aureus plasmid pI258 (67 and 73% amino acid identities, respectively); however, only 40% of the amino acid residues of RC607 MerA were identical to those of the mercuric reductase from gram-negative bacteria. A 69-kilodalton polypeptide was isolated and identified as the merA gene product by examination of its amino-terminal sequence.