Previous Article
Journal of Bacteriology, June 2002, p. 3146-3149, Vol. 184, No. 11
0021-9193/02/$04.00+0 DOI: 10.1128/JB.184.11.3146-3149.2002
Copyright © 2002, American Society for Microbiology. All Rights Reserved.
Methylation of Inorganic and Organic Selenium by the Bacterial Thiopurine Methyltransferase
Lionel Ranjard,,
Claire Prigent-Combaret, Sylvie Nazaret, and Benoit Cournoyer*
UMR CNRS 5557Ecologie Microbienne (Center for Microbial Ecology), Université Claude BernardLyon I, 69622 Villeurbanne Cedex, France
Received 17 December 2001/
Accepted 6 March 2002

ABSTRACT
Escherichia coli cells expressing the
tpm gene encoding the
bacterial thiopurine methyltransferase (bTPMT) are shown to
methylate selenite and (methyl)selenocysteine into dimethylselenide
(DMSe) and dimethyldiselenide (DMDSe).
E. coli cells expressing
tpm from a gene library cosmid clone (harboring a
Pseudomonas syringae insert of about 20 kb) also methylated selenate into
DMSe and DMDSe. bTPMT is the first methyltransferase shown to
be involved in the methylation of these selenium derivatives.

INTRODUCTION
Selenium is an essential element, but its presence in micromolar
concentrations can lead to death and deformities of wildlife
(
14). It can be found in enzymes under the form of selenocysteine
amino acids or bound in such a way that it can be detached by
denaturing or reducing agents (for a review, see reference
9).
Bacteria have been shown to play a key role in the biological
cycle of selenium by reduction (
19) and volatilization of inorganic
selenium (for a review, see references
4 and
7) in the environment.
A significant contribution to the understanding of the biochemistry
of this cycle was made by studies with
Thauera selenatis. A
dissimilatory selenate reductase enzyme complex was found in
this bacterium and shown to be trimeric and periplasmic and
to reduce selenate to selenite (
18). This selenate reductase
was shown to have a high affinity and turnover rate for selenate,
much higher than the ones of the bacterial periplasmic nitrate
reductases (
17). The
T. selenatis nitrite respiratory system
was shown to reduce selenite to elemental selenium in the presence
of nitrate (
3).
T. selenatis was isolated from sediments of
the San Joaquin Valley, and its selenate-reducing capacity was
recently used for the bioremediation of selenium from agricultural
drainage water (
1). The biochemistry and genetics of the enzymes
involved in selenium methylation remain almost unexplored. Bioremediation
by volatilization of selenium from contaminated sites represents
an interesting alternative to the use of selenate-respiring
bacteria (
10).
Recently, we discovered a methyltransferase that might be involved in the methylation of inorganic selenite (2). This enzyme, named the bacterial thiopurine methyltransferase (bTPMT), was shown to catalyze the S adenosylmethylation of aromatic and heterocyclic sulfhydryl compounds like 6-mercaptopurine. It belongs to a group of methyltransferases whose presence in eukaryotes (human, rat, mouse, etc.) is very well documented (for examples, see references 15 and 20). The human TPMT (hTPMT) is essential for the metabolism of thiopurine drugs (11), which are frequently used in the treatment of human autoimmune diseases and for transplantations (5, 16). The bTPMT, overexpressed in Escherichia coli, conferred resistance to tellurite and the ability to grow at high concentrations of sodium biselenite (2). Here, we present clear evidence that bTPMT is involved in the methylation of inorganic and organic selenium into dimethylselenide (DMSe) and dimethyldiselenide (DMDSe). bTPMT is the first methyltransferase shown to be involved in the bacterial selenium methylation processes.
The effect of bTPMT on the production of DMSe and DMDSe was tested in the E. coli cellular environment. Gas chromatography-mass spectrometry (GC-MS) analyses were performed to estimate the production levels of DMSe and DMDSe. These were carried out on a Hewlett-Packard 6890 GC coupled to mass spectrometer model 5973. The chromatography column was a Supelco VOCOL (60 m by 250 µm by 1.5 µm). One milliliter of the headspace gases was injected per analysis. The split ratio was 0.1:1 µl, with a flow rate of 200 µl per min. The gas saver was set at 20 ml per min for 2 min. The carrier gas was helium (obtained from Air Liquide) and was used at a flow rate of 1.7 ml per min in the column and at a flow rate of 4.2 ml per min in the injector. Gas pressure was 180 kPa. The temperature of the injector was 210°C. Elution conditions were 2 min at 30°C and a subsequent temperature ramp of 5°C per min from 30 to 210°C. Retention times of DMSe and DMDSe were estimated by using purchased gases (from Sigma-Aldrich). To demonstrate the role of bTPMT in selenium methylation, GC-MS experiments compared the productions of DMSe and DMDSe by E. coli DH10B strains expressing or not expressing the gene (tpm) encoding the bTPMT and grown with inorganic and organic molecules of selenium [selenite, selenate, (methyl)selenocysteine, and selenomethionine]. E coli cells can naturally transform some of these selenium molecules. For example, E. coli cells growing on selenite accumulate red-orange pigments, known to be elemental selenium and the products of reduction reactions. Our results show that they transform (by an unknown mechanism that is less efficient than the bTPMT-driven one) (methyl)selenocysteine, but not selenomethionine or inorganic selenium, into volatile DMSe and DMDSe (Table 1). The significance of the bTPMT-driven production of DMSe and DMDSe was thus tested by performing Student's t tests with the Staview-SE package.
bTPMT is encoded by the
tpm genetic determinant which was previously
isolated from pAV257, a tellurite-resistant (Tel
r) pLAFR3 library
clone (containing a DNA insert of more than 20 kb) of
Pseudomonas syringae pathovar pisi strain 203 (
2). In this study, the pAV257
tpm gene was inactivated by using a Tn
7-based insertional mutagenesis
approach to further investigate its function. In vitro transposition
was performed with the GPS-M mutagenesis system following the
manufacturer's recommendations (New England Biolabs, Beverly,
Mass.). Using this system, 190 mutagenized pAV257 cosmids subcloned
into
E. coli DH10B (Gibco BRL, Cergy Pontoise, France) were
obtained and were then screened on 4-ppm potassium tellurite
to identify
tpm-inactivated Tel
s cosmid clones. Five Tel
s cosmid
clones were obtained, and the positions of the Tn
7 insertions
were determined, in the first instance, by PCR (following Gibco
BRL's recommendations) using Tn
7L and Tn
7R primers (New England
Biolabs) and the
tpm primer 317 (
2). The positions of four of
five of the insertions of these Tel
s cosmids were determined
by PCR inside the
tpm open reading frame, and one was located
in a region likely to be part of the
tpm promoter region. In
the second instance, the locations of three of these insertions
were determined by DNA sequencing (done by Genome Express S.
A., Grenoble, France) and found to be located 278 bp downstream
of the
tpm start codon of cosmid pD5, 166 bp downstream for
pG10, and 372 bp downstream for pB21. These data suggest that
a single gene,
tpm, on this cosmid conferred Tel
r. pD5 was used
to evaluate the role of
tpm (and the bTPMT) in selenium methylation.
The E. coli DH10B clones harboring pAV257, pD5, and control strains were inoculated into 250-ml flasks sealed with rubber stoppers fastened by aluminum crimps and containing 50 ml of Luria-Bertani medium supplemented with various selenium compounds (Fig. 1; Table 1). A tpm pBluescript subclone, pAV617 (2), strictly harboring tpm was also used in these methylation assays. E. coli DH10B harboring the vector pBluescript SK(-) was included as a negative control in all these experiments. Concentrations of 10 ppm of potassium selenate, potassium selenite, (methyl)selenocysteine, and selenomethionine (Sigma) were added independently to these cultures after growth for 24 h at 37°C. The cultures were then incubated 4 days at 37°C on a rotary shaker (200 rpm). The headspace gases of each flask were then analyzed by GC-MS (as described above). Significant levels (P < 0.05 by comparison with the control and pD5-harboring cells) of DMSe and DMDSe were detected for the tpm-harboring E. coli strains grown with inorganic (selenite and selenate) and organic [(methyl)selenocysteine] selenium (Fig. 1; Table 1). tpm-harboring cells producing DMSe always showed (for a P value of <0.1 and excluding cells grown with potassium selenate) a less important DMDSe production. When selenite was used, DMSe and DMDSe were detected at significant levels (P < 0.05 by comparison with the control and pD5-harboring cells) for both tpm constructs tested, i.e., pAV257 (library clone) and pAV617 (harboring only tpm). When selenate was used, significant DMSe production (P < 0.05 by comparison with the control and pD5-harboring cells) could be detected only for E. coli strains harboring pAV257 (Table 1). Significant peak values (P < 0.05 by comparison with the control and pD5-harboring cells) for DMSe (but not DMDSe) were detected with the pAV257 and pAV617 constructs and (methyl)selenocysteine as a substrate but not selenomethionine. The absence of significant methylation activity observed with pD5 (inactivated tpm) (by comparison with the control cells) showed that tpm encodes the key enzyme involved with the selenate, selenite, and selenocysteine methylation process presented here.
Cournoyer et al. (
2) reported the presence of metallic tellurium
and selenium by
tpm-harboring
E. coli cells growing with tellurite
and selenite. It is thus likely that oxidoreduction steps performed
by
E. coli are essential in this methylation process. However,
the reduction of selenate to selenite did not seem to be performed
by
E. coli because of the lack of significant methylation activity
by the strictly
tpm-harboring pBluescript subclone (pAV617).
Significant DMSe production (
P < 0.05 by comparison with
pAV617-harboring cells) with selenate could be detected only
from pAV257-harboring cells. This suggests a reduction of selenate
into selenite by an enzyme (or complex) encoded by pAV257
tpm-neighboring
genes. A dissimilatory selenate reductase like the one reported
by Schroeder et al. (
18) could be involved in this process and
be encoded by this library clone. Similarly, the production
of DMSe was found significantly (
P < 0.05) more important
for pAV257-harboring cells than for pAV617-harboring cells which
were grown with (methyl)selenocysteine (Table
1). This suggests
that pAV257 genetic determinants other than
tpm are also having
an effect on the TPMT-driven methylation of (methyl)selenocysteine.
Three main observations have thus been made in this work. First, bTPMT can methylate inorganic and organic selenium; second, it can transform these molecules into DMSe and DMDSe; third, other genetic determinants on the bTPMT-encoding cosmid clone (pAV257) are likely to be involved in the methylation process of selenate and selenocysteine. It was previously suggested that the bTPMT was likely to be involved in tellurium and selenium methylation, and a pathway, adapted from the one of Doran (4), presenting a likely methylation process going from selenite to DMSe, had been proposed (2). Here, we provided pieces of evidence that are in line with this pathway but also showed that the processing of other selenium molecules [i.e., selenate and (methyl)selenocysteine] converges toward key intermediates that can be methylated by bTPMT. For selenate, it is more than likely that reduction into selenite is required prior to its volatilization. Regarding (methyl)selenocysteine, methane selenol could be the intermediate shared with the selenite or selenate methylation pathway, although none was detected here (likely because of the chromatography column used). The single cleavage of the covalent bond between the carbon and selenium can easily lead to the release of this product, which could be methylated by bTPMT into DMSe.
From this work, it is now clear that bTPMT can detoxify a broader spectrum of molecules than reported so far. This enzyme could become a key in the remediation of anthropogenically or naturally Se-contaminated sites. DMSe is 500 to 700 times less toxic than inorganic selenium species (6, 8, 12). This process is also likely to be involved in the production of dimethyl selenide in eukaryotes, including humans, because of the widely conserved nature of the methyltransferase involved (2). We are now planning to investigate further the spectrum of molecules that could be methylated by the bTPMT, including other metalloids like arsenic.

ACKNOWLEDGMENTS
We thank the "Pôle Expertise Eau" and J. Molas of Danone
France for the GC-MS analyses and their helpful expertise on
selenium chemistry.

FOOTNOTES
* Corresponding author. Mailing address: UMR CNRS 5557Ecologie Microbienne, Center for Microbial Ecology, Université Claude BernardLyon I, 43 Bd. 11 Novembre 1918, Bât Gregor Mendel (741), 5th floor, F-69622 Villeurbanne Cedex, France. Phone: 33 (0) 4 72 43 14 95. Fax: 33 (0) 4 72 43 12 23. E-mail:
cournoye{at}biomserv.univ-lyon1.fr.

Present address: Laboratoire de Microbiologie du Sol, INRA/CMSE, 21065 Dijon, France. 

REFERENCES
1
- Cantafio, A. W., K. D. Hagen, G. E. Lewis, T. L. Bledsoe, K. M. Nunan, and J. M. Macy. 1996. Pilot-scale selenium bioremediation of San Joaquin drainage water with Thauera selenatis. Appl. Environ. Microbiol. 62:3298-3303.[Abstract]
2
- Cournoyer, B., S. Watanabe, and A. Vivian. 1998. A tellurite-resistance genetic determinant from phytopathogenic pseudomonads encodes a thiopurine methyltransferase: evidence of a widely-conserved family of methyltransferases. Biochim. Biophys. Acta 1397:161-168.[Medline]
3
- Demoll-Decker, H., and J. M. Macy. 1993. The periplasmic nitrite reductase of Thauera selenatis may catalyse the reduction of selenite to elemental selenium. Arch. Microbiol. 160:241-247.
4
- Doran, J. W. 1982. Microorganisms and the biological cycling of selenium, p. 1-32. In K. C. Marshall (ed.), Advances in microbial ecology. Plenum Press, New York, N.Y.
5
- Elion, G. B. 1989. Nobel lecture. The purine path to chemotherapy. Biosci. Rep. 9:509-529.[CrossRef][Medline]
6
- Franke, K. W., and A. L. Moxon. 1936. A comparison of the minimal fatal doses of selenium, tellurium, arsenic and vanadium. J. Pharmacol. Exp. Ther. 58:454-459.[Abstract/Free Full Text]
7
- Gadd, G. M. 1993. Microbial formation and transformation of organometallic and organometalloid compounds. FEMS Microbiol. Rev. 11:297-316.[CrossRef]
8
- Ganther, H. E., O. A. Levander, and C. A. Saumann. 1966. Dietary control of selenium volatilization in the rat. J. Nutr. 88:55-60.
9
- Heider, J., and A. Böck. 1993. Selenium metabolism in micro-organisms. In A. H. Rose (ed.), Advances in microbial physiology, vol. 35. Academic Press, London, United Kingdom.
10
- Karlson, U., and W. T. Frankenberger. 1990. Volatilization of selenium from agricultural evaporation pond sediments. Sci. Total Environ. 92:41-54.[CrossRef][Medline]
11
- Lennard, L., J. A. Van Loon, J. S. Lilleyman, and R. M. Weinshilboum. 1987. Thiopurine pharmacogenetics in leukemia: correlation of erythrocyte thiopurine methyltransferase activity and 6-thioguanine nucleotide concentrations. Clin. Pharmacol. Ther. 41:18-25.[Medline]
12
- McConnell, K. P., and O. W. Portman. 1952. Toxicity of dimethyl selenide in the rat and mouse. Proc. Soc. Exp. Biol. Med. 79:230-231.
13
- Miller, J. F. 1972. Experiments in molecular genetics, p. 190-201. Cold Spring Harbor Laboratory, Cold Spring Harbor, N.Y.
14
- Ohlendorf, H. M., D. J. Hoffman, M. K. Saiti, and T. W. Aldrich. 1986. Embryonic mortality and abnormalities of aquatic birds: apparent impacts of selenium from irrigation drainwater. Sci. Total Environ. 52:49-63.[CrossRef]
15
- Otterness, D. M., and R. M. Weinshilboum. 1987. Mouse thiopurine methyltransferase pharmacogenetics: monogenic inheritance. J. Pharmacol. Exp. Ther. 240:817-824.[Abstract/Free Full Text]
16
- Paterson, A. R. P., and D. M. Tidd. 1975. 6-Thiopurines, p. 384-403. In A. C. Sartorelli and D. G. Johns (ed.), Antineoplastic and immunosuppressive agents II. Springer Verlag, New York, N.Y.
17
- Sabaty, M., C. Avazeri, D. Pignol, and A. Vermeglio. 2001. Characterization of the reduction of selenate and tellurite by nitrate reductases. Appl. Environ. Microbiol. 67:5122-5126.[Abstract/Free Full Text]
18
- Schroeder, I., S. Rech, T. Frafft, and J. M. Macy. 1997. Purification and characterization of the selenate reductase from Thauera selenatis. J. Biol. Chem. 272:23765-23768.[Abstract/Free Full Text]
19
- Stolz, J. F., and R. S. Oremland. 1999. Bacterial respiration of arsenic and selenium. FEMS Microbiol. Rev. 23:615-627.[CrossRef][Medline]
20
- Szumlanski, C., D. Otterness, C. Her, D. Lee, B. Brandriff, D. Kelsell, N. Spurr, L. Lennard, E. Wieben, and R. M. Weinshilboum. 1996. Thiopurine methyl transferase pharmacogenetics: human gene cloning and characterization of a common polymorphism. DNA Cell Biol. 15:17-30.[Medline]
Journal of Bacteriology, June 2002, p. 3146-3149, Vol. 184, No. 11
0021-9193/02/$04.00+0 DOI: 10.1128/JB.184.11.3146-3149.2002
Copyright © 2002, American Society for Microbiology. All Rights Reserved.
This article has been cited by other articles:
-
Pierru, B., Grosse, S., Pignol, D., Sabaty, M.
(2006). Genetic and Biochemical Evidence for the Involvement of a Molybdenum-Dependent Enzyme in One of the Selenite Reduction Pathways of Rhodobacter sphaeroides f. sp. denitrificans IL106.. Appl. Environ. Microbiol.
72: 3147-3153
[Abstract]
[Full Text]
-
Swearingen, J. W. Jr., Fuentes, D. E., Araya, M. A., Plishker, M. F., Saavedra, C. P., Chasteen, T. G., Vasquez, C. C.
(2006). Expression of the ubiE Gene of Geobacillus stearothermophilus V in Escherichia coli K-12 Mediates the Evolution of Selenium Compounds into the Headspace of Selenite- and Selenate-Amended Cultures. Appl. Environ. Microbiol.
72: 963-967
[Abstract]
[Full Text]
-
LeDuc, D. L., Tarun, A. S., Montes-Bayon, M., Meija, J., Malit, M. F., Wu, C. P., AbdelSamie, M., Chiang, C.-Y., Tagmount, A., deSouza, M., Neuhierl, B., Bock, A., Caruso, J., Terry, N.
(2004). Overexpression of Selenocysteine Methyltransferase in Arabidopsis and Indian Mustard Increases Selenium Tolerance and Accumulation. Plant Physiol.
135: 377-383
[Abstract]
[Full Text]
-
Wackett, L. P., Dodge, A. G., Ellis, L. B. M.
(2004). Microbial Genomics and the Periodic Table. Appl. Environ. Microbiol.
70: 647-655
[Full Text]
-
Ranjard, L., Nazaret, S., Cournoyer, B.
(2003). Freshwater Bacteria Can Methylate Selenium through the Thiopurine Methyltransferase Pathway. Appl. Environ. Microbiol.
69: 3784-3790
[Abstract]
[Full Text]