Previous Article | Next Article 
Applied and Environmental Microbiology, September 2001, p. 4017-4023, Vol. 67, No. 9
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.9.4017-4023.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
Obligate Sulfide-Dependent Degradation of
Methoxylated Aromatic Compounds and Formation of Methanethiol and
Dimethyl Sulfide by a Freshwater Sediment Isolate,
Parasporobacterium paucivorans gen. nov., sp.
nov.
Bart P.
Lomans,
Pieter
Leijdekkers,
Jan-Jaap
Wesselink,
Patrick
Bakkes,
Arjan
Pol,
Chris
van der Drift, and
Huub J. M. Op
den Camp*
Department of Microbiology, Faculty of
Science, University of Nijmegen, NL-6525 ED Nijmegen, The Netherlands
Received 1 February 2001/Accepted 12 June 2001
 |
ABSTRACT |
Methanethiol (MT) and dimethyl sulfide (DMS) have been shown to be
the dominant volatile organic sulfur compounds in freshwater sediments.
Previous research demonstrated that in these habitats MT and DMS are
derived mainly from the methylation of sulfide. In order to identify
the microorganisms that are responsible for this type of MT and DMS
formation, several sulfide-rich freshwater sediments were amended with
two potential methyl group-donating compounds, syringate and
3,4,5-trimethoxybenzoate (0.5 mM). The addition of these methoxylated
aromatic compounds resulted in excess accumulation of MT and DMS in all
sediment slurries even though methanogenic consumption of MT and DMS
occurred. From one of the sediment slurries tested, a novel anaerobic
bacterium was isolated with syringate as the sole carbon source. The
strain, designated Parasporobacterium paucivorans,
produced MT and DMS from the methoxy groups of syringate. The
hydroxylated aromatic residue (gallate) was converted to acetate and
butyrate. Like Sporobacterium olearium, another
methoxylated aromatic compound-degrading bacterium, the isolate is a
member of the XIVa cluster of the low-GC-content
Clostridiales group. However, the new isolate differs from all other known methoxylated aromatic compound-degrading bacteria
because it was able to degrade syringate in significant amounts only in
the presence of sulfide.
 |
INTRODUCTION |
The production of dimethyl sulfide
(DMS) and methanethiol (MT) has been intensively studied because of the
roles that the oxidation products of these compounds (e.g.,
methanesulfonic acid and SO2) play in the
processes of global warming and acid precipitation and in the global
sulfur cycle (15). In marine and estuarine systems, DMS
and MT are derived primarily from the degradation of
dimethylsulfoniopropionate, a widespread osmolyte in marine macroalgae
and phytoplankton (16). In freshwater habitats, formation of MT and DMS originates mainly from the methylation of sulfide (10, 17, 25) and to a lesser extent from the degradation of sulfur-containing amino acids (14). In many
heterotrophic aerobic bacteria the methylation of sulfide is catalyzed
by an S-adenosylmethionine-dependent thiol methyltransferase
(7). Since this pathway is not observed in obligately
anaerobic bacteria (21), it will be of minor importance in
organic-rich freshwater sediments, which generally are oxygen limited
(26, 27). One of the mechanisms for MT and DMS formation
through sulfide methylation is the anaerobic O demethylation of
methoxylated aromatic compounds (3, 10). Bacteria
performing this kind of methylation use sulfide or MT as a methyl group
acceptor instead of CO or CO2, which are used by
several acetogenic bacteria (23, 24). However, in
Holophaga foetida, Sporobacter termitidis
(13), and Sporobacterium olearium
(31), the O demethylation of methoxylated aromatic compounds did not strictly depend on sulfide (or MT) as methyl group
acceptor. O demethylation in strain SA2 appeared to be strictly sulfide
dependent (3), but unfortunately this strain was lost, which made a complete description of the isolate impossible.
The present study reports on the impact of methoxylated aromatic
compounds on the production of volatile organic sulfur compounds (VOSC)
in freshwater sediments. Further, the isolation of an obligately anaerobic bacterium which produces DMS and MT during growth on methoxylated aromatic compounds in sulfide-reduced mineral media is
described. O demethylation of methoxylated aromatic compounds by our
isolate appears to be strictly sulfide dependent.
 |
MATERIALS AND METHODS |
Source of inoculum.
Sediment samples were collected from a
eutrophic freshwater pond (campus of the Dekkerswald Institute,
Nijmegen, The Netherlands). The sediment samples were taken by suction
in anaerobic bottles as described by Lomans et al. (25).
Slurry incubations.
Sediment slurries were prepared and
dispensed in anaerobic bottles as described previously
(25). Additions were made from neutral-pH stock solutions
prepared in distilled water. These additions included
bromoethanesulfonic acid (BES), syringate, and 3,4,5-trimethoxybenzoate
(TMB). The sediment slurries (duplicates or triplicates) were incubated
in the dark without shaking at 30°C. Sterilized sediment slurries
(121°C, 20 min) served as abiotic controls.
Media and culture techniques.
The defined sulfide-reduced
and bicarbonate-buffered medium described before (28) was
supplemented with Na2SO4 to
a final concentration of 28 mM. Instead of sulfide, other
compounds were used as reducing agents: sodium thiosulfate (0.5 mM),
cysteine-HCl (2 mM), sodium dithionite (0.5 mM), and titanium(III)
nitrilotriacetic acid [Ti(III)NTA] (0.1 mM). Additions of carbon
sources (syringate, TMB, gallate, pyrogallol, or pyroglucinol) (final
concentration, 5 mM) were made 1 to 2 h before inoculation from
anaerobic filter-sterilized stock solutions prepared in distilled water
and neutralized with NaOH. Enrichment cultures were done in an
anaerobic chemostat fed with syringate as the sole carbon source,
continuously gassed with an H2S-containing gas
stream (N2-CO2 [80:20,
vol/vol]) (28). The chemostat was inoculated with 10% of
a sediment slurry which had been pulsed with syringate. Batch
cultivation was carried out in either 60-, 120-, or 500-ml serum
bottles filled with 25, 50, or 350 ml of medium, respectively. The
bottles were sealed with black butyl rubber stoppers, gassed with an
O2-free mixture of N2 and
CO2 (80:20, vol/vol), sterilized (121°C, 20 min), and incubated in the dark at 30°C. Purity was tested by growth
experiments in the medium (with or without syringate) supplemented with
yeast extract (0.5%) and Trypticase peptone (0.5%) and was checked by microscopy. Stock cultures were transferred into fresh medium once a
month and stored in glass ampoules under
N2-CO2 (80:20, vol/vol)
after the addition of glycerol (final concentration, 5%) at
80°C.
Determination of optimal growth conditions.
Specific growth
rates were determined by measuring the sum of MT and DMS formed during
growth on syringate, which correlated very well with the increase of
optical density. Effects of various culture conditions (pH,
temperature, and salt concentrations) were tested with preadapted
cultures. Cultures were transferred under these conditions at least two
times sequentially.
Syringate conversion by cell suspension.
Exponential
cultures were centrifuged (30 min, 10,000 × g), and
the pellet was washed in anaerobic medium without syringate and reduced
with Ti(III)NTA (0.05 mM)-sodium dithionite (0.25 mM). Incubations were
carried out under N2-CO2
(80:20, vol/vol) at 35°C. Incubation was started by addition of
syringate or syringate plus sodium sulfide.
Cell extract incubations.
A 20-liter fermentor was
inoculated with a pure culture. After depletion of the carbon source,
the culture received another pulse of syringate (5 mM). After growth
for 200 h at 30°C, cells were harvested by continuous
centrifugation (Sharples; 20,000 × g, 17°C) under an
N2 atmosphere. The cell pellet was resuspended in
TES buffer {50 mM
2-[tris(hydroxymethyl)methylamino]-1-ethanesulfonic acid (TES), 5 mM
MgCl2, 1 mM dithiothreitol, pH 7.0}. Cells were broken by passage through a French pressure cell under an
N2 atmosphere at 120 MPa. The crude extract was
centrifuged (40,000 × g, 30 min, 4°C), resulting in
a clear supernatant which was stored under N2-CO2 (80:20, vol/vol) at
80°C. Cell extract incubations were done in 120-ml serum bottles
with 10 to 100 µl of crude cell extract, 50 mM TES buffer, 1 to 2 mM
ATP, 5 mM sodium sulfide, and 0.2 mM syringate adjusted to a total
volume of 1 ml with MilliQ water. The bottles were prepared in an
anaerobic cabinet and sealed with gray butyl rubber stoppers.
Incubations (25°C) were started by addition of syringate, and
demethylation activity was monitored by measuring the formation of MT.
Analytical techniques.
Gas samples were analyzed for
H2S, MT, DMS, and methane as described before
(6, 25). Acetate, butyrate, and methanol were measured as
described by Cazemier et al. (4). Methoxylated and
hydroxylated aromatic compounds were analyzed by isocratic separation
on a high-pressure liquid chromatograph equipped with a Merck
LiChrospher 100 RP-18 column and an HP1040 diode array detector. The
flow rate of the eluent, 40% (vol/vol) methanol in ammonium phosphate
buffer (100 mM, pH 2.6), was 0.5 ml/min. The column temperature was
25°C.
Microscopy and photography.
Transmission and scanning
electron micrographs were made with a transmission electron microscope
(Philips 201) and a Cryo-FEG scanning electron microscope (Jeol JSM
633OF) from cells of a late-exponential-phase culture. Negative
staining was done with uranyl acetate (0.5 to 1%).
Phylogenetic analysis.
DNA from the pure culture was
isolated by harvesting the cells in an Eppendorf centrifuge
(10,000 × g for 5 min at room temperature). The cell
pellet was washed two times in fresh nonreduced medium, suspended in
0.5 ml of lysis buffer (0.1 M sodium EDTA, 0.15 M NaCl, 0.02%
lysozyme), and incubated for 2 h at 37°C. Sodium dodecyl sulfate
(SDS) (1% wt/vol) was added, and incubation was continued for 30 min
at 37°C. Proteinase K (50 µg/ml) was added, and the suspension was
incubated for 30 min at 37°C. The solution was extracted with
phenol-chloroform-isoamyl alcohol (25:24:1). The pellet obtained after
ethanol precipitation of the water phase was dissolved in 10 µl of
sterile distilled water and stored at
20°C. The DNA was used as a
template for PCR amplification of an approximately 1,530-bp segment of
the 16S rRNA gene with 2.5 mM MgCl2, an annealing
temperature of 50°C, and 35 cycles. The PCR amplification primers
used were pA (19EubFOR) (5'-GAGTTTGATCCTGGCTCAG-3') and pH'
(1522REV) (5'-AAGGAGGTGATCCAGCCGCA-3') (8). The
amplification product was ligated in the pCR II vector and transformed
into Escherichia coli cells from the TA cloning kit
(Invitrogen). Plasmid DNA of clones was isolated by using the FlexiPrep
kit (Pharmacia P-L Biochemicals Inc.). The sequence of the cloned PCR
product, which represented the original 16S rRNA sequence, was analyzed on a DNA sequencer (model 373A; Applied Biosystems, Inc., Foster City,
Calif.) using the Taq DyeDeoxy terminator cycle sequencing method (30; Taq DyeDeoxy terminator cycle sequencing kit
user bulletin no. 901497, revision E [Applied Biosystems, Inc.]).
Besides the primers of the TA cloning kit (M13FOR and M13REV) and
primers mentioned in the literature (pA [19FOR], pE' [908REV], and
pH' [1522REV] [8] and 517REV [1]), the
following primers were used for sequencing: 500FOR
(5'-TGTGCCAGCAGCCGCGGTAA-3'), 1050FOR (5'-GTGCATGGCTGTCGTCAGYTC-3'), and 1161REV
(5'-TGACGTCATCCCCACCTT-3'). The primers 500FOR, 1050FOR, and
1162REV were designed on the basis of published eubacterial and
archaeal 16S rRNA sequences. The resulting sequences were assembled to
produce a 1,487-bp DNA sequence. The deduced 16S rRNA sequence of
strain SYR1 was aligned with homologous 16S rRNA sequences of closely
related members of the Eubacteria domain by using the Pileup
method (Dutch CMBI Center Facility, Nijmegen, The Netherlands).
Distance matrix trees were constructed by using the method of Fitch and
Margoliash (12) and the neighbor-joining method of Saitou
and Nei (33) in the FITCH and NEIGHBOR programs of the
PHYLIP (version 3.4) program package (9). Parsimony and
bootstrap parsimony analyses were performed using the DNAPARS and
DNABOOT programs as implemented in the PHYLIP package.
Nucleotide sequence accession numbers.
The deduced
almost-complete primary structure (1,487 bp) of the 16S rRNA gene of
strain SYR1 has been deposited in the EMBL sequence database under
accession number AJ272036.
 |
RESULTS |
Slurry incubations.
Slurries from various origins amended with
either syringate (0.5 mM) or TMB (0.5 mM) all showed transient
accumulation of DMS and traces of MT. After prolonged incubation (>200
h), the accumulated DMS and MT disappeared. In contrast, in nonamended slurries MT and DMS concentrations were below the detection limit (<0.3 µM). Addition of BES to syringate- or TMB-amended slurries resulted in a dramatic increase of the rate of accumulation of MT and
DMS, which reached concentrations of higher than 0.5 and 1.5 mM,
respectively. In BES-syringate- or BES-TMB-amended slurries, DMS and MT
did not disappear even after prolonged incubation. All of the sediments
tested showed similar patterns, although the final concentrations of
the MT and DMS accumulated differed. In all incubations DMS was the
major VOSC produced.
Enrichment and isolation of strain SYR1.
The sediment of a
eutrophic freshwater pond (Dekkerswald) was used to inoculate a
chemostat in order to isolate anaerobic syringate-utilizing and
DMS-producing microorganisms. Syringate was converted to acetate, MT,
and DMS. The use of this chemostat (D = 0.10 h
1) resulted in an MT- and DMS-producing
enrichment consisting of one dominant morphologically distinct
bacterium. Deep-agar tube dilution series on syringate plus sulfide
eventually led to a pure culture of an MT- and DMS-producing anaerobic
bacterium, which was named strain SYR1. Purity was confirmed by
microscopic analysis and absence of growth after addition of yeast
extract (0.5%) and Trypticase peptone (0.5%) to the medium.
Morphology.
Deep-agar colonies of strain SYR1 were white
circular disks and reached a diameter of 1 to 2 mm in 1 week while
growing on syringate plus sulfide. Cells occur as double rods (Fig.
1). The average length and width of
individual cells were 2.0 and 0.4 µm, respectively. Motility and
spore formation were not observed. Cells did not lyse within 15 min
after addition of SDS (0.1 to 1%). The Gram stain reaction was
negative.

View larger version (98K):
[in this window]
[in a new window]
|
FIG. 1.
Scanning electron micrograph of a logarithmic-phase
culture of strain SYR1 grown on syringate (5 mM). The photograph
clearly shows the double-rod morphology of strain SYR1.
|
|
Catabolic substrates.
Growth of strain SYR1 was observed only
on syringate (5 mM), TMB (5 mM), and gallate (5 mM). Growth on
syringate and TMB was accompanied by concomitant formation of MT and
DMS, whereas growth on gallate was not. Degradation of syringate was
characterized by transient accumulation of MT (mostly during the
logarithmic phase), directly followed by accumulation of DMS (Fig.
2). This increase of the MT and DMS
correlated with an increase in optical density and acetate
concentration and a decrease in syringate. Cultures normally had a lag
phase of about 10 to 15 h followed by exponential growth.
Transferring SYR1 from syringate to gallate did not result in a
prolonged lag phase. The maximum specific growth rate estimated from MT
and DMS formation as well as from optical density measurements was 0.2 h
1. No growth or MT or DMS formation was
observed on 3,4-dimethoxybenzoate, 3,5-dimethoxybenzoate, vanillate,
pyrogallol, phloroglucinol, benzoate, pyruvate,
H2-CO2, methanol, malate,
fructose, glucose, pectin, or glycine-betaine. Concentrations used were
5 mM, except for methanol (10 mM),
H2-CO2 (80:20, vol/vol),
phloroglucinol (2.5 mM), and pectin (1 g/liter).

View larger version (16K):
[in this window]
[in a new window]
|
FIG. 2.
Time courses of growth of strain SYR1 on syringate and
sulfide. Symbols: , syringate; , MT; , DMS; , acetate; ×,
optical density at 660 nm (OD660).
|
|
Reducing agents.
In cultures of strain SYR1 on syringate, TMB,
or gallate, no growth was observed when sulfide was replaced by
cysteine, thiosulfate, or Ti(III)NTA. Cysteine, thiosulfate, and
Ti(III)NTA were not toxic, since they did not inhibit growth of strain
SYR1 when added to sulfide-reduced cultures. Moreover, if sulfide was
added to cysteine- or Ti(III)NTA-reduced cultures after
prolonged incubation, growth was observed (see also Fig. 3B). The
combined addition of sodium sulfide, cysteine, sodium thiosulfate, and
Ti(III)NTA usually resulted in higher final MT and DMS concentrations
in fully grown cultures. Addition of cysteine also resulted in a slightly higher optical density (at 660 nm) of the final culture (0.184, versus 0.155 on 5 mM syringate). Sulfide toxicity was tested by
growing strain SYR1 at various sulfide concentrations (0.9 to 17 mM).
The growth rate calculated from MT and DMS production was highest (0.18 h
1) in cultures with 2.5 mM sulfide and
decreased dramatically in cultures with higher sulfide concentrations.
Optimal growth conditions.
Strain SYR1 grew optimally between
pH 6.5 and 7.0 and between 34 and 37°C. No growth was observed above
40°C. Strain SYR1 showed optimal growth at NaCl concentrations of 0 to 30 mM (note that the standard medium already contained 28 mM sodium
sulfate). MT and DMS formation occurred up to 135 mM NaCl. The
tolerance of strain SYR1 to high concentrations of syringate and
acetate was tested in order to be able to predict the behavior of
strain SYR1 during cultivation of high quantities of cell biomass. In cultures with higher concentrations of syringate, sodium sulfide was
added in pulses (2.5 mM) to avoid both toxicity and depletion of
sulfide. Strain SYR1 showed optimal growth at syringate concentrations of 2.5 to 7.5 mM. At higher concentrations (tested up to 20 mM), growth
was observed but appeared to be lower and less predictable. Moreover,
in cultures grown with increasing concentrations of syringate, the
concentrations of acetate produced did not increase proportionally to
the amount of syringate added. In addition, increasing amounts of
butyrate were formed (Table 1). Addition of 0.05% (wt/vol) yeast extract stimulated growth but did not appear
to be essential for growth.
Impact of sulfide on syringate degradation.
The sulfide
dependency of the syringate degradation was investigated by cultivation
of strain SYR1 under sulfide-rich and sulfide-free conditions.
(i) Cultivation in an excess of sulfide.
During the
incubation, cultures were pulsewise amended with sodium sulfide to
prevent both sulfide-limited conditions and sulfide toxicity. Under
sulfide-rich conditions, syringate degradation resulted in the
formation of large amounts of MT, DMS, and acetate (Fig.
3A). Formation of MT, DMS, acetate, and
butyrate stopped when syringate was depleted (90 h). The amount of
butyrate was very low compared to amount of acetate produced (Fig. 3B).
After complete degradation of syringate, in the presence of residual sulfide, MT remained in the medium.

View larger version (17K):
[in this window]
[in a new window]
|
FIG. 3.
Time courses of volatile sulfur compounds (VSC) (A) and
syringate and volatile fatty acids (VFA) (B) of a sulfide-rich culture
of strain SYR1 and time courses of syringate and VOSC of a sulfide-free
culture of strain SYR1 (C). Arrows indicate pulsewise additions of
sodium sulfide. Symbols: , sulfide; , MT; , DMS; ,
syringate; , acetate; , butyrate.
|
|
(ii) Cultivation in sulfide-free media.
Cultures without
sodium sulfide and with Ti(III)NTA (0.6 mM) or cysteine (3.4 mM) as a
reducing agent did not show any DMS formation and showed only very
limited syringate degradation (Fig. 3C). Furthermore, no increase in
optical density was observed. Cultures amended with Ti(III)NTA turned
yellowish. When after an incubation of more than 40 days sulfide was
added to the Ti(III)NTA-reduced cultures, syringate was degraded with
concomitant formation of DMS (Fig. 3C) and the yellow color
disappeared. The cells in this culture apparently were still viable.
(iii) Cell suspension experiments.
The growth experiments with
sulfide limitation mentioned above are likely to be affected by sulfur
source limitation, since strain SYR1 is strictly dependent on sulfide
as a sulfur source. Therefore, cell suspension experiments were
performed under sulfide-rich and sulfide-free [Ti(III)NTA-reduced]
conditions in which no growth and thus no sulfur source is needed.
Indeed, syringate degradation was limited by the absence of sulfide. In
cell suspensions with sulfide, syringate was demethylated very rapidly
within 60 min with concomitant production of MT and DMS (Fig.
4). Although no sulfide was added (or
detected) in the sulfide-free washed-cell suspensions, a limited
degradation of syringate with concomitant MT and DMS formation was
observed (Fig. 4). The potential for demethylation of the cell
suspensions without sulfide was not irreversibly affected, since
addition of sulfide after prolonged incubation of these cell
suspensions resulted in an immediate production of MT, DMS, and
demethylated aromatic residues (data not shown). These aromatic
residues disappeared after prolonged incubation. The
Ks for sulfide of strain SYR1 was
determined by measuring the initial MT formation rate of cell
suspensions incubated with various concentrations of sulfide (added as
sodium sulfide). The Ks of strain SYR1 for
sulfide was on the order of 200 to 400 µM.

View larger version (16K):
[in this window]
[in a new window]
|
FIG. 4.
Time courses of cell suspensions incubated under
sulfide-rich (closed symbols) and sulfide-free (open symbols)
conditions. Triangles, syringate; diamonds, methyl groups (MT plus
DMS).
|
|
Demethylation of methoxylated aromatic compounds by strain
SYR1.
The influence of temperature on the demethylation activity
was tested by incubation of cell extracts at various temperatures (20 to 40°C). Maximum demethylation activity, measured as the MT formed,
was found at 25°C. The oxygen sensitivity of demethylation was tested
by preincubating the cell extract under an air atmosphere in the
absence and presence of ATP. Subsequently, MT formation capacity was
measured under an anaerobic atmosphere. The MT formation capacity of
the cell extracts preincubated under air appeared to be dramatically
lower (38 pmol · min
1 · µl of
cell extract
1) than that of the control (258 pmol · min
1 · µl of cell
extract
1) and was not restored by the addition
of ATP either before of after the exposure to oxygen (15 pmol · min
1 · µl of cell
extract
1). The enzymatic formation of MT was
strictly ATP dependent (optimum at an ATP concentration of 2 mM).
Addition of both glucose and hexokinase during the incubation
significantly inhibited the MT formation. Addition of propyliodide, a
known inhibitor of corronoid-dependent methyltransferases, did not
affect the MT formation by the cell extract. Doubling the amount of
cell extract in the assay mixture resulted in proportionally increased
MT formation rates. Activity screening of fractions obtained by fast
performance liquid chromatography gel filtration demonstrated that all
of the activity resided in only one fraction with a molecular mass of
about 200 kDa. MT formation was found after addition of the following
substrates: 3,4-dimethoxybenzoate, TMB, 4-hydroxy-3-methoxybenzoate
(vanillate), and 4-hydroxy-3,5-dimethoxybenzoate (syringate). No MT
formation was found after addition of 3,5-dimethoxybenzoate.
Phylogenetic and taxonomic analysis.
A 1,530-bp DNA fragment
homologous to the rRNA gene of strain SYR1 was amplified in vitro,
cloned in the pCR II vector, transformed in E. coli, and
sequenced. Use of the Chimera Check analysis of the Ribosomal Database
Project (29) showed that the sequence was indeed derived
from a single target DNA sequence. Database searches revealed
that the highest similarity value (91.8%) was found for the sequences
of strain SYR1 and Sporobacterium olearium. A phylogenetic
tree based on a matrix of distances of a 1,487-bp fragment of the 16S
rRNA gene clearly shows that strain SYR1 clusters within subclass XIVa
of the very polymorphic Clostridiales (Fig. 5). Besides 16S rRNA sequences of closely
related microorganisms, those of several other methoxylated aromatic
compound-degrading bacteria, including H. foetida and
Sporobacter termitidis, are incorporated in this tree.

View larger version (23K):
[in this window]
[in a new window]
|
FIG. 5.
Phylogenetic tree based on a distance matrix prepared
from an alignment of a partial 16S rRNA sequences (1,478 bp) of
P. paucivorans and other selected closely related
bacteria. Bootstrap values indicate the percentage of occurrence of 100 bootstrap trees. Only values above 80 are given. Reference sequences
were from the GenBank and EMBL databases: X95624, Ruminococcus
hydrogenotrophicus; X94966, Ruminococcus
productus; X85101, Ruminococcus obeum; AF116854,
Sporobacterium olearium; Z49863, Sporobacter
termitidis; X77215, Holophaga foetida; X77216,
Pelobacter acidigallici; X96954, Acetobacterium
woodii; X71858, Clostridium polysaccharolyticum;
X71853, Clostridium populeti; AF028351,
Clostridium indolis; X71855, Clostridium
xylanolyticum; AF067965, Clostridium
methoxybenzovorans; X73449, Clostridium
sphenoides; X71848, Clostridium celerecrescens;
AF028349, Clostridium fusiformis; AF202259,
Eubacterium oxidoreducens. Sporobacter termitidis was
used as the outgroup. Bar, 10 base substitutions per 100 bases. Names
of MT- or DMS-producing microorganisms are underlined.
|
|
 |
DISCUSSION |
Isolation and physiology of strain SYR1.
The in situ
concentrations of the most dominant VOSC, MT and DMS, showed strong
correlation with the rate of methane formation and the sulfide
concentration in the sediment, the dominant compartment in VOSC
formation of freshwater ecosystems (25). Methylation of
sulfide with methoxylated aromatic compounds as methyl group donors is
the major mechanism for VOSC formation in freshwater sediments
(10, 17, 25). Addition of syringate or TMB to slurries
prepared from various freshwater sediments immediately resulted in
elevated levels of DMS, indicating an active bacterial population. From
one of the sediments an anaerobic bacterium was isolated with syringate
as the sole carbon source. The isolated strain, SYR1, has a very
limited substrate spectrum, being capable of anaerobic growth only on
syringate, TMB, and gallate as sole carbon and energy sources. The fact
that the production of MT and DMS was restricted to growth on syringate
or TMB with sulfide (it was absent with gallate plus sulfide)
demonstrates that the carbon atoms in the produced MT and DMS are
derived from the methoxy groups of syringate or TMB, as is the case for
the previously described isolates strain SA2, H. foetida,
Sporobacter termitidis, and Sporobacterium
olearium (3, 13, 31). Similar to the case for
H. foetida and SA2, strain SYR1 is likely to degrade syringate via O demethylation of the methoxy groups , since the strain
does not grow on methanol. In contrast to H. foetida
(3), however, the demethylation by strain SYR1 appeared to
be strictly sulfide dependent. Sulfide could not be replaced by
cysteine, thiosulfate, or sulfate. A similar dependency was reported
for strain SA2 (3). However, this organism could grow on
gallate without addition of sulfide.
The transient accumulation of MT in cultures of strain SYR1
demonstrates that DMS is formed via MT as an intermediate. In
this
respect strain SYR1 differs from the closely related
Sporobacterium olearium, which only produces MT from the
methoxy groups of syringate
(
31). The use of MT or sulfide
as a methyl group acceptor is
likely to depend on the actual
concentration of either of the
two compounds, since MT formation was
higher in sulfide-rich cultures,
whereas DMS was the dominant product
under sulfide-limited conditions.
The
Ks
for sulfide of strain SYR1 (200 to 400 µM) was on the same
order of
magnitude as that found for the freshwater sediment from
which it had
been isolated (
25).
The different isolation procedures for
H. foetida and strain
SA2 (most-probable-number series) and strain SYR1 (chemostat)
is
reflected in the fact that strain SYR1 has a higher maximum
specific
growth rate (0.2 h
1) than
H. foetida
(0.06 h
1), strain SA2 (0.10 h
1), and
Sporobacter termitidis
(0.05 h
1) (
3,
13). The maximum
specific growth rate of
Sporobacterium olearium was not
reported (
31). On the basis of the experiments
outlined in
Fig.
2 and Table
1, we assume the following stoichiometries
for acetate
and butyrate formation, respectively:
C
9H
10O
5
(syringic acid) + H
2S + 3H
2O

3CH
3COOH + CH
3SCH
3 + CO
2
5C
9H
10O
5
(syringic acid) + 5H
2S + 9H
2O

6CH
3CH
2CH
2COOH + 5CH
3SCH
3 + 11CO
2
Biochemical analysis of a cell extract of strain SYR1
revealed that several methoxylated aromatic compounds, which do not
support growth, were also demethylated. This lack of growth might
be
caused by the absence of the appropriate transport mechanism
for the
demethylated products. Moreover, it was demonstrated that
the
demethylating enzyme system was ATP dependent and oxygen sensitive,
making MT and DMS synthesis a strictly anaerobic process, as was
the
case for
H. foetida (
18,
19). The absence of
inhibition
by propyliodide revealed that the enzyme systems of strain
SYR1
are likely to be corronoid
independent.
Phylogenetic and taxonomic analysis.
Strain SYR1 appeared to
be a member of cluster XIVa of the genus Clostridiales
(4, 5). Phylogenetically, strain SYR1 appeared to be most
closely related to Sporobacterium olearium; however, there
are numerous physiological differences between the two isolates. Strain
SYR1 has a very limited substrate range, whereas Sporobacterium
olearium could use a wide variety of substrates. Moreover, strain
SYR1 did not produce spores, whereas Sporobacterium olearium
did. Gram staining of Sporobacterium olearium was positive, whereas that of strain SYR1 was negative. Finally, our isolate produces
both MT and DMS from methoxy groups of syringate, whereas Sporobacterium olearium produced MT only. Also, the
syringate metabolism of strain SYR1 did not appear to be influenced by
the presence of H2 in the culture like that of
Sporobacterium olearium (31).
In contrast to most of the other closely related organisms of the
genera
Clostridium,
Eubacterium, and
Ruminococcus, both
strain SYR1 and
Sporobacterium
olearium could not utilize common
carbohydrates (e.g., glucose and
fructose) as carbon and energy
sources. Remarkably, the feature of
(methoxylated) aromatic compound
metabolism is distributed among
various genera (
2,
3,
13,
20,
22,
23,
24,
31,
32,
34,
35).
On the basis of its low 16S rRNA sequence similarity (91.8%) with the
closest related bacterium,
Sporobacterium olearium,
as well
as its physiological properties, we propose that strain
SYR1 is a
representative of a novel genus. The isolate was named
Parasporobacterium paucivorans.
Ecological niche of P. paucivorans.
The
formation and degradation of VOSC in situ are well balanced
(25). Production of MT and DMS occurs mainly anaerobically because of the steep oxygen gradient at the water column-sediment interface (26, 27). The major part of the endogenous
produced MT and DMS is formed by means of the methylation of sulfide
and subsequently MT (17, 25). According to its
physiological properties (VOSC production and apparent
Ks for sulfide), P. paucivorans strain SYR1 is likely to be responsible for the production of MT and
DMS in freshwater sediments in situ. The degradation of methoxylated
aromatic compounds in sulfide-poor sediments is likely to be dominated
by acetate-producing bacteria such as Acetobacterium woodii,
whereas in sulfide-rich sediment MT- and DMS-producing organisms like
P. paucivorans will dominate. In sediments with alternating
conditions (sulfide rich and sulfide poor), bacteria like H. foetida and Sporobacter termitidis will have an
advantage compared to the other organisms. The transient accumulation
of MT and DMS in slurry experiments confirms the interaction between syringate-degrading and methanogenic bacteria (10, 11). A representative methanogen, Methanomethylovorans hollandica,
was previously isolated (28).
Description of Parasporobacterium paucivorans gen.
nov., sp. nov.
Parasporobacterium paucivorans
(Pa.ra.spo.ro.bac.te.'ri.um. Gr. prefix
para, besides, next to; Gr. n. sporos, seed,
spore; Gr. n. bacterion, small rod; N.L. neut. n.
Parasporobacterium, a genus similar to
Sporobacterium; pau.ci.vo'rans. L. plur. pron. pauci, a few; L. adj. part. vorans, devouring; L. adj. paucivorans, degrading a limited number of substrates),
double rod-shaped cells (length, 1.5 to 2 µm; width, 0.3 to 0.5 µm)
which exhibit a negative Gram reaction. Cells normally occur as double
rods. Cells were not sensitive to lysis by 0.1 g of SDS per liter.
Syringate, TMB, and gallate are catabolic substrates. Sulfide is
essential for growth and demethylation of methoxylated aromatic
compounds. Growth was most rapid at 0 to 1.8 g of NaCl; some MT
and DMS formation occurred at up to 8 g of NaCl. Growth is most
rapid at pH 6.5 to 7.0. Growth is most rapid at 34 to 37°C, and no
growth was obtained at temperatures of above 40°C. The type strain
SYR1 was isolated from a slurry of a eutrophic lake sediment (campus of the Dekkerswald Institute, Nijmegen, The Netherlands). Strain SYR1T, named P. paucivorans, has been
deposited in the DSMZ culture collection (Braunschweig, Germany)
(accession number not yet available) and in The Netherlands Culture
Collection of Bacteria under accession number NCCB100009.
 |
ACKNOWLEDGMENTS |
We thank Hans Hippe of the Deutsche Sammlung von Mikroorganismen
und Zellkulturen GmbH for his advice on the nomenclature for our isolate.
This work was supported by The Netherlands Organization for the
Advancement of Pure Research (NWO) as part of the program "Verstoring
van Aardsystemen."
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
Microbiology, Faculty of Science, University of Nijmegen, Toernooiveld 1, NL-6525 ED Nijmegen, The Netherlands. Phone: 31 (0) 24 3652657. Fax:
31 (0) 24 3652830. E-mail: huubcamp{at}sci.kun.nl.
 |
REFERENCES |
| 1.
|
Achenbach, L., and C. Woese.
1995.
16S and 23S rRNA-like primers, p. 521-523.
In
F. T. Robb, A. R. Place, K. R. Sowers, H. J. Scheier, S. DasSarma, and E. M. Fleischmann (ed.), Archaea, a laboratory manual. Cold Spring Harbor Laboratory Press, Cold Spring Harbor, N.Y.
|
| 2.
|
Bache, R., and N. Pfennig.
1981.
Selective isolation of Acetobacterium woodii on methoxylated aromatic acids and determination of growth yields.
Arch. Microbiol.
130:255-261[CrossRef].
|
| 3.
|
Bak, F.,
K. Finster, and F. Rothfuss.
1992.
Formation of dimethyl sulfide and methanethiol from methoxylated aromatic compounds and inorganic sulfide by newly isolated anaerobic bacteria.
Arch. Microbiol.
157:529-534.
|
| 4.
|
Cazemier, A. E.,
H. J. M. Op den Camp,
J. H. P. Hackstein, and G. D. Vogels.
1997.
Fibre digestion in arthropods.
Comp. Biochem. Physiol.
118A:101-109.
|
| 5.
|
Collins, M. D.,
P. A. Lawson,
A. Willems,
J. J. Cordoba,
J. Fernandez-Garayzabal,
P. Garcia,
J. Cai,
H. Hippe, and J. A. E. Farrow.
1994.
The phylogeny of the genus Clostridium: proposal of five new genera and eleven new species combinations.
Int. J. Syst. Bacteriol.
44:812-826[Abstract/Free Full Text].
|
| 6.
|
Derikx, P. J. L.,
H. J. M. Op den Camp,
C. van der Drift,
L. J. L. D. Van Griensven, and G. D. Vogels.
1990.
Odorous sulfur compounds emitted during production of compost used as a substrate in mushroom cultivation.
Appl. Environ. Microbiol.
56:176-180[Abstract/Free Full Text].
|
| 7.
|
Drotar, A.,
G. A. Burton, Jr.,
J. E. Tavernier, and R. Fall.
1987.
Widespread occurrence of bacterial thiol methyltransferases and the biogenic emission of methylated sulfur gases.
Appl. Environ. Microbiol.
53:1626-1631[Abstract/Free Full Text].
|
| 8.
|
Edwards, U.
1989.
Isolation and direct complete nucleotide determination of entire genes. Characterization of a gene coding for 16S ribosomal RNA.
Nucleic Acids Res.
17:7843-7853[Abstract/Free Full Text].
|
| 9.
|
Felsenstein, J.
1982.
Numerical methods of inferring evolutionary trees.
Q. Rev. Biol.
57:379-404[CrossRef].
|
| 10.
|
Finster, K.,
G. M. King, and F. Bak.
1990.
Formation of methyl mercaptan and dimethyl sulfide from methoxylated aromatic compounds in anoxic marine and freshwater sediments.
FEMS Microbiol. Ecol.
74:295-302[CrossRef].
|
| 11.
|
Finster, K.,
Y. Tanimoto, and F. Bak.
1992.
Fermentation of methanethiol and dimethylsulfide by a newly isolated methanogenic bacterium.
Arch. Microbiol.
157:425-430[CrossRef].
|
| 12.
|
Fitch, W. M., and E. Margoliash.
1967.
Construction of phylogenetic trees: a method based on mutation distances as estimated by cytochrome c sequences is of general applicability.
Science
155:279-284[Free Full Text].
|
| 13.
|
Grech-Mora, I.,
M.-L. Fardeau,
B. K. C. Patel,
B. Ollivier,
A. Rimbault,
G. Prensier,
J.-L. Garcia, and E. Garnier-Sillam.
1996.
Isolation and characterization of Sporobacter termitidis gen. nov., sp. nov., from the digestive tract of the wood-feeding termite Nasutitermes lujae.
Int. J. Syst. Bacteriol.
46:512-518[Abstract/Free Full Text].
|
| 14.
|
Kadota, H., and Y. Ishida.
1972.
Production of volatile sulfur compounds by microorganisms.
Annu. Rev. Microbiol.
26:127-138[CrossRef][Medline].
|
| 15.
|
Kelly, D. P., and N. A. Smith.
1990.
Organic sulfur compounds in the environment: biochemistry, microbiology and ecological aspects.
Adv. Microb. Ecol.
11:345-385.
|
| 16.
|
Kiene, R. P., and D. G. Capone.
1988.
Microbial transformations of methylated sulfur compounds in anoxic salt marsh sediments.
Microb. Ecol.
15:275-291[CrossRef].
|
| 17.
|
Kiene, R. P., and M. E. Hines.
1995.
Microbial formation of dimethyl sulfide in anoxic Sphagnum peat.
Appl. Environ. Microbiol.
61:2720-2726[Abstract].
|
| 18.
|
Kreft, J.-U.
1995.
The methyl ester cleaving enzyme system of the anaerobic bacterium Holophaga foetida. PhD thesis.
Universität Konstanz, Konstanz, Germany.
|
| 19.
|
Kreft, J.-U., and B. Schink.
1993.
Demethylation and degradation of phenylmethylethers by the sulfide-methylating homoacotogenic bacterium strain TMBS4.
Arch. Microbiol.
159:308-315[CrossRef].
|
| 20.
|
Krumholz, L. R., and M. P. Bryant.
1986.
Eubacterium oxidoreducens sp. nov. requiring H2 or formate to degrade gallate, pyrogallol, phloroglucinol and quercetin.
Arch. Microbiol.
144:8-14[CrossRef].
|
| 21.
|
Larsen, G. L.
1985.
Distribution of cysteine -lyase in gastro-intestinal bacteria and in the environment.
Xenobiotica
15:199-209[Medline].
|
| 22.
|
Liesack, W.,
F. Bak,
J. U. Kreft, and E. Stackebrandt.
1994.
Holophaga foetida gen. nov., sp. nov., a new homoacetogenic bacterium degrading methoxylated aromatic compounds.
Arch. Microbiol.
162:85-90[CrossRef][Medline].
|
| 23.
|
Liu, S., and J. M. Suflita.
1993.
H2-CO2-dependent anaerobic O-demethylation activity in subsurface sediments by an isolated bacterium.
Appl. Environ. Microbiol.
59:1325-1331[Abstract/Free Full Text].
|
| 24.
|
Liu, S., and J. M. Suflita.
1995.
H2 as an energy source for mixotrophic acetogenesis from the reduction of CO2 and syringate by Acetobacterium woodii and Eubacterium limosum.
Curr. Microbiol.
31:245-250[CrossRef].
|
| 25.
|
Lomans, B. P.,
A. J. P. Smolders,
L. Intven,
A. Pol,
H. J. M. Op den Camp, and C. van der Drift.
1997.
Formation of dimethyl sulfide and methanethiol in anoxic freshwater sediments.
Appl. Environ. Microbiol.
63:4741-4747[Abstract].
|
| 26.
|
Lomans, B. P.,
H. J. M. Op den Camp,
A. Pol, and G. D. Vogels.
1999.
Anaerobic versus aerobic degradation of dimethyl sulfide and methanethiol in anoxic freshwater sediments Appl.
Environ. Microbiol.
65:438-443.
|
| 27.
|
Lomans, B. P.,
H. J. M. Op den Camp,
A. Pol,
C. van der Drift, and G. D. Vogels.
1999.
Role of methanogens and other bacteria in degradation of dimethyl sulfide and methanethiol in anoxic freshwater sediments.
Appl. Environ. Microbiol.
65:2116-2121[Abstract/Free Full Text].
|
| 28.
|
Lomans, B. P.,
R. Maas,
R. Luderer,
H. J. M. Op den Camp,
A. Pol,
C. van der Drift, and G. D. Vogels.
1999.
Isolation and characterization of Methanomethylovorans hollandica gen. nov., sp. nov., isolated from freshwater sediment, a methylotrophic methanogen able to grow on dimethyl sulfide and methanethiol.
Appl. Environ. Microbiol.
65:3641-3650[Abstract/Free Full Text].
|
| 29.
|
Maidak, B. L.,
J. R. Cole,
C. T. Parker, Jr.,
G. M. Garrity,
N. Larsen,
B. Li,
T. G. Lilburn,
M. J. McCaughey,
G. J. Olsen,
R. Overbeek,
S. Pramanik,
T. M. Schmidt,
J. M. Tiedje, and C. R. Woese.
1999.
A new version of the RDP (Ribosomal Database Project).
Nucleic Acids Res.
27:171-173[Abstract/Free Full Text].
|
| 30.
|
McBride, L. J.,
S. M. Koepf,
R. A. Gibbs,
W. Salser,
P. E. Mayrand,
M. W. Hunkapiller, and M. N. Kronick.
1989.
Automated DNA sequencing methods involving polymerase chain reaction.
Clin. Chem.
35:2196-2201[Abstract/Free Full Text].
|
| 31.
|
Mechichi, T.,
M. Labat,
J.-L. Garcia,
P. Thomas, and B. K. C. Patel.
1999.
Sporobacterium olearium gen. nov., sp. nov., a new methanethiol-producing bacterium that degrades aromatic compounds, isolated from an olive mill wastewater treatment digester.
Int. J. Syst. Bacteriol.
49:1741-1748[Abstract/Free Full Text].
|
| 32.
|
Mechichi, T.,
M. Labat,
B. K. C. Patel,
T. H. S. Woo,
P. Thomas, and J.-L. Garcia.
1999.
Clostridium methoxybenzovorans sp. nov., a new aromatic O-demethylating homoacetogen from an olive mill waste treatment digester.
Int. J. Syst. Bacteriol.
49:1201-1209[Abstract/Free Full Text].
|
| 33.
|
Saitou, N., and M. Nei.
1987.
The neighbor-joining method: a new method for reconstruction of phylogenetic trees.
Mol. Biol. Evol.
4:406-425[Abstract].
|
| 34.
|
Schink, B., and N. Pfennig.
1982.
Fermentation of trihydroxybenzenes by Pelobacter acidigallici gen. nov., sp. nov., a new strictly anaerobic non-spore-forming bacterium.
Arch. Microbiol.
133:195-201[CrossRef].
|
| 35.
|
Stupperich, E., and R. Konle.
1993.
Corronoid-dependent methyl transfer reactions are involved in methanol and 3,4-dimethoxybenzoate metabolism by Sporomusa ovata.
Appl. Environ. Microbiol.
59:3110-3116[Abstract/Free Full Text].
|
Applied and Environmental Microbiology, September 2001, p. 4017-4023, Vol. 67, No. 9
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.9.4017-4023.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
This article has been cited by other articles:
-
(2004). Validation of publication of new names and new combinations previously effectively published outside the IJSEM. Int. J. Syst. Evol. Microbiol.
54: 307-308
[Abstract]
[Full Text]