Structural and biochemical characterization of the irganomercurial Lyase MerB

Mercury is introduced into the environment from either natural occurrences (volcanoes) or from human activities (combustion of fossil fuels). Mercury exists as elemental mercury (Hg0), ionic mercury (HgII) or organic mercury like methylmercury (MeHg) and these forms are in constant flux with each other as part of the natural biogeochemical cycle. Organomercurial compounds like MeHg are the most toxic form because of their hydrophobicity and their ability to efficiently permeate membranes and bioaccumulate in organisms. High levels of MeHg have been found in fish in many areas around the world, and therefore human consumption of contaminated seafood represents a serious danger for human health. Bacteria isolated from mercury-contaminated environments have evolved a system that allows them to efficiently convert both ionic and organic mercury compounds to the less toxic elemental mercury. The mercury resistance is due to the acquisition of a transferable genetic element known as the mer operon. The mer operon encodes for several proteins including two enzymes, the organomercurial lyase MerB and the mercuric ion reductase MerA. MerB catalyzes the protonolysis of the carbon-mercury bond of organomercurial compounds to produce a reduced-carbon compound and inorganic ionic mercury HgII. MerA catalyzes the reduction of HgII to elemental mercury Hg0, which is volatile and less toxic. Due to their ability to cleave MeHg and reduce the resulting HgII product, MerB and MerA are considered crucial to bioremediation efforts to clean up MeHg from contaminated waterways. A clear understanding of the mechanistic details of how MerB and MerA function together at the atomic level is crucial for appropriate utilization of the mer system in bioremediation efforts. We have been using nuclear magnetic resonance (NMR) spectroscopy and X-ray crystallography to structurally and mechanistically characterize E. coli MerB. Based on previous structural studies of E. coli MerB, three residues (Cys96, Asp99 and Cys159) have been identified as a catalytic triad which is required for carbon-Hg bond cleavage. As a follow up to the earlier studies, my project involves using X-ray crystallography to define the roles of Cys96, Asp99 and Cys159 in substrate binding and cleavage.  Two different approaches were implemented to fulfill this goal. Firstly, MerB mutants were tested to define the role for the catalytic residues. Secondly, MerB inhibitors and other potential non-organomercurial substrates were used to probe MerB active site. The Cys,-Asp-Cys catalytic triad found in E.coli MerB is conserved in all MerB variants except four variants where aspartic acid is replaced by a serine. To understand the role of Asp99, we compared a serine-containing MerB variant (Bacillus megaterium MerB2) and an E. coli MerB mutant (MerB D99S) to wild type E. coli MerB. Interestingly, the purified MerB D99S protein was found to contain a pink color. X-ray crystal structure indicated the presence of a bound metal in the active site of MerB D99S. Analysis by inductively coupled plasma mass spectrometry (ICP-MS) and X-ray fluorescence indicated that MerB D99S binds copper in the active site. Further, electron paramagnetic resonance (EPR) and NMR studies identified the copper as CuII. Addition of organomercurial substrate displaces bound CuII but MerB D99S shows diminished catalytic activity. In contrast, MerB2 did not co-purify with copper although the X-ray structure of MerB2-Hg complex is virtually identical to the structure of the MerB D99S-Hg. This suggests that the aspartic acid residue is crucial for the cleavage of carbon-Hg bonds of organomercurials as well as metal-binding specificity. Furthermore, the binding of copper to the MerB D99S protein suggests a possible evolutionary link between MerB and its structural homolog, the copper-binding protein NosL. In the second approach, we probed the active site of MerB through testing its binding to organotin and organolead compounds. The known MerB inhibitor triethyltin (TET) binds to Asp99 without binding to any of the active site cysteines. A similar binding has been observed with trimethylead (TML). Dimethyltin (DMT) inhibits MerB using an alternative mechanism. It first binds to Asp99 then Cys96, which induces a dramatic change in the active site by disrupting a cation-π interaction between Try95 and Arg155. In contrast, diethyltin (DET) and diethylead (DEL) were found to be substrates for MerB, where both ethyl groups were cleaved and the SnIV and PbIV products bound to the active site in a similar manner to HgII. DMT, DET and DEL show higher binding affinity to MerB than its initial substrate MeHg. These results suggest that organomercurials may not be the only substrates for MerB and Asp99 is the first residue to bind to organometals followed by subsequent binding to Cys96 and Cys159. In addition, these observations suggest that there are other possible applications for employing MerB in bioremediation of organolead and organotin contaminated sites while other organometals may have implications when using MerB in bioremediation systems.  Keyword: Organomercuriallyase, MerB, Organolead. Organotin, Copper binding protein, Carbon metal bond cleavage, Methylmercury, Organomercuriels, Bioremédiation, Nuclear magnetic resonance, X ray crystallography.

Keyphrases: Organomercuriallyase, MerB, Organolead, Organotin, Copper binding protein, Carbon metal bond cleavage, Organomercuriels, Bioremédiation