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Applied and Environmental Microbiology, January 2008, p. 540-542, Vol. 74, No. 2
0099-2240/08/$08.00+0 doi:10.1128/AEM.01750-07
Copyright © 2008, American Society for Microbiology. All Rights Reserved.
Methyl Sulfide Production by a Novel Carbon Monoxide Metabolism in Methanosarcina acetivorans
James J. Moran,1,2*
Christopher H. House,1*
Jennifer M. Vrentas,1 and
Katherine H. Freeman1
Department of Geosciences and The Penn State Astrobiology Research Center, The Pennsylvania State University, University Park, Pennsylvania 16802,1
School of Geography and Earth Sciences, McMaster University, Hamilton, Ontario, Canada L8S 4K12
Received 27 July 2007/
Accepted 7 November 2007

ABSTRACT
We observed dimethyl sulfide and methanthiol production in pure
incubations of the methanogen
Methanosarcina acetivorans when
carbon monoxide (CO) served as the only electron donor. Energy
conservation likely uses sodium ion gradients for ATP synthesis.
This novel metabolism permits utilization of CO by the methanogen,
resulting in quantitative sulfide methylation.

INTRODUCTION
Rother and Metcalf (
18) recently described a CO metabolism for
the methanogen
Methanosarcina acetivorans. Unlike previously
described CO methanogenic pathways (
5,
12,
17), this metabolism
produces acetate, formate, and methane but not hydrogen. We
cultured
M. acetivorans C2A by using CO as a growth substrate
and observed the additional production of both dimethyl sulfide
(DMS) and methanthiol (MeSH). Culturing (33.5°C) occurred
under 300 kPa of CO in medium (150 ml per bottle) similar to
that described by Moran et al. (
16), but with 1 g/liter sodium
bicarbonate and no organic substrate in 600-ml bottles. Standard
bottles for analyte quantification were made in parallel but
lacked the sulfide addition. Cultures were inoculated (2.0 ml)
from a CO-grown preculture. At intervals throughout growth,
1.0-ml liquid samples were collected for sulfide analysis (by
a technique adopted from Hach water quality test kits [Hach
Company, Loveland, CO], which showed no interference with DMS
or MeSH), acetate and formate analysis (by ion chromatography;
Dionex LC30 and AS18 analytical column), and cell counting.
Headspace samples (200 µl) were analyzed for CH
4, DMS,
and MeSH by using gas chromatography (HP 5890 with a GS-Q column
and flame ionization detector), and the analyte was quantified
by comparison to standard bottles to determine the total moles
of analyte in the bottle (combined dissolved and gaseous fractions).
Our results (Fig. 1) show that during growth, microbial DMS and MeSH production effectively scrubbed out free sulfide in the culture medium to less than 4% of the pregrowth values, suggesting sulfide methylation as the pathway for methyl sulfide formation. Enhanced growth (as measured by increased cell densities and methane production) when cultures were exposed to more sulfide suggests energy conservation by sulfide methylation (Fig. 2). Here, we used four sets of triplicate culture bottles containing preinoculation sulfide totaling 0.00, 0.16, 0.31, and 0.63 mmol per bottle.
At standard state, energy yields for MeSH production are consistent
with energy conservation (calculated with data from references
1 and
19):
Free-energy gains by MeSH production are comparable
to those previously estimated (
18) for acetate formation from
CO, –41.2 kJ/mol CO consumed.
CO is a known methanogenesis inhibitor in both M. acetivorans (18) and other methanogen species (5, 17). This inhibition likely targets the methanogenic pathway at methyl coenzyme M reductase (MCR) and would restrict carbon flow through this enzyme, leading to methyl-CoM accumulation, which would eventually stop energy production by sequestering all CoM.
Methyl sulfide formation provides a low-energy method for regenerating CoM without MCR activity. Working with Methanosarcina barkeri, Tallant et al. (22) demonstrated that direct methylation of MeSH to DMS has a modest energy barrier of only 0.35 kJ per reaction. When MCR is inhibited, the transfer protein (480-kDa corrinoid protein) that normally methylates CoM becomes methylated itself by methyl-CoM (4, 21) and elevated MeSH concentrations promote small-scale methylation of MeSH to DMS (15), suggesting reversibility in the first step of methanogenic DMS consumption. Thus, in instances of MCR inhibition by CO, we hypothesize that methyl sulfide formation is essential for regenerating CoM and maintaining an active metabolism for energy production. Furthermore, this occurrence suggests that the methyltransferase protein identified by Cao and Krzycki (4) is metabolically versatile and can be active in both methanogenic and non-methane-producing energy conservation, depending upon environmental conditions.
The mechanism for energy conservation during sulfide methylation is unclear. When generating methane, methanogens rely largely on reduction of a heterodisulfide bond formed by MCR activity for net energy formation (23). The observed methyl sulfide production likely bypasses MCR, suggesting a different pathway for energy conservation. One option is via a sodium gradient (8; J. G. Ferry, personal communication). The Mtr methyltransferase is expressed in M. acetivorans when cultured on CO (14) and is also known to generate a sodium gradient (3) linked to ATP production in another methanogen, Methanococcus voltae (8). The activation of CO2 before reduction, however, consumes some of the sodium gradient produced by Mtr (6), making it unclear how effective ATP synthesis via this route would be during methyl sulfide production by M. acetivorans. Nevertheless, the ability of methanogens to link methyl transfer to a sodium ion gradient may permit energy conservation by sulfide methylation. In contrast, nonenergetic sulfide methylation from methyl transfer is observed in Holophaga foetida (9), a species with no known ability for sodium ion gradient formation.
To the best of our knowledge, the metabolism described here is the first example of both a methanogen producing high concentrations of methyl sulfides and of a CO metabolism resulting in sulfide methylation. M. acetivorans was isolated from marine sediments rich in decaying sea grass and kelp deposits (20). The bladders used to keep kelp upright underwater are filled with up to 12% CO (13), and their decay is a likely CO source. Under realistic marine conditions (500 µM sulfide, 1 µM MeSH, 10 mM dissolved inorganic carbon, pH 8, and 10°C), the free energy of MeSH production remains favorable at low CO concentrations, approaching 10 pM. Potential energy yields at such low CO concentrations suggest that this metabolism could be active in kelp bed sediments. Furthermore, elevated acetate concentrations in organic-rich sediments would thermodynamically disfavor the acetogenic CO metabolism previously reported (18) and therefore confer an energetic advantage toward methyl sulfide formation.
In addition to the potential role of methanogen-mediated CO conversion to methyl sulfides in modern marine environments, this metabolism has implications for sulfur cycling in ancient Earth. Methanogens likely evolved by the late Archean eon or earlier in Earth's history (2, 24) and had a strong influence on global climate regulation (10). The atmosphere at that time may have contained elevated CO concentrations (11), permitting sulfide methylation by the metabolism described herein. The quest for life outside our planet depends on searching for chemical signatures of life (7). If similar, early-evolving organisms are present on other planets, then methyl sulfides provide a valuable target in the search for extraterrestrial microbial life.

ACKNOWLEDGMENTS
We thank B. Thomas for technical assistance and many useful
discussions in preparing this work.
Graduate support for this project was provided by the Penn State Biogeochemical Research Initiative for Education (BRIE) funded by NSF (IGERT) grant DGE-9972759. This work was also funded by the Penn State Astrobiology Research Center (through the National Astrobiology Institute), NOAA-NURP (UAF 05-0132), and the National Science Foundation (MCB-0348492).

FOOTNOTES
* Corresponding author. Mailing address for James J. Moran: School of Geography and Earth Sciences, McMaster University, 1280 Main Street West, Hamilton, Ontario, Canada L8S 4K1. Phone: (905) 525-9140, ext. 20122. Fax: (905) 546-0463. E-mail:
jimjmoran{at}gmail.com. Mailing address for Christopher H. House: Department of Geosciences, The Pennsylvania State University, University Park, PA 16802. Phone: (814) 865-8802. Fax: (814) 863-7823. E-mail:
c.h.house{at}gmail.com 
Published ahead of print on 16 November 2007. 

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Applied and Environmental Microbiology, January 2008, p. 540-542, Vol. 74, No. 2
0099-2240/08/$08.00+0 doi:10.1128/AEM.01750-07
Copyright © 2008, American Society for Microbiology. All Rights Reserved.