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Applied and Environmental Microbiology, October 1999, p. 4301-4312, Vol. 65, No. 10
Microbial Biochemistry Section,
Received 9 April 1999/Accepted 20 July 1999
A novel dehalogenating/transhalogenating enzyme,
halomethane:bisulfide/halide ion methyltransferase, has been isolated
from the facultatively methylotrophic bacterium strain CC495, which uses chloromethane (CH3Cl) as the sole carbon source.
Purification of the enzyme to homogeneity was achieved in high yield by
anion-exchange chromatography and gel filtration. The methyltransferase
was composed of a 67-kDa protein with a corrinoid-bound cobalt atom.
The purified enzyme was inactive but was activated by preincubation
with 5 mM dithiothreitol and 0.5 mM CH3Cl; then it
catalyzed methyl transfer from CH3Cl, CH3Br, or
CH3I to the following acceptor ions (in order of decreasing
efficacy): I Chloromethane (CH3Cl) is
the most abundant volatile halocarbon present in the atmosphere; the
atmospheric concentration of about 600 parts per 1012 (by
volume) represents a total tropospheric burden of 5 million metric
tons. Of chlorine-catalyzed ozone destruction in the stratosphere, 15 to 20% can be attributed to CH3Cl (35, 40).
Atmospheric CH3Cl appears to be predominantly of natural
origin, derived from biological and chemical processes in both marine
and terrestrial environments. Important sources identified to date
include oceanic emissions (27, 36), release by wood-rotting
fungi (20, 22, 23, 59), and biomass burning (1,
31). The major chemical sink for atmospheric CH3Cl is
reaction with hydroxyl radicals in the troposphere, although photolysis
and hydrolysis may also play minor roles (12). Studies of
biological sinks for CH3Cl have been largely neglected
until very recently, despite the observation that biodegradation of
bromomethane (CH3Br) by soil bacteria is a significant
route for the destruction of atmospheric CH3Br (25, 47). On the basis of measurements of soil-atmosphere exchange in
a Brazilian forest and in arctic grasslands and tundra, Khalil and
Rasmussen (28) have estimated that the annual global uptake of CH3Cl by soil is of the order of 0.5 million metric tons.
Cometabolism of CH3Cl by several microorganisms has been
observed (26, 43, 48), but there are few reports of the
isolation of organisms that can use it as a sole carbon and energy
source. A methylotrophic homoacetogenic bacterium which is capable of growing on CH3Cl (2% in the gas phase) as the sole carbon
source under strictly anaerobic conditions has been isolated from
sewage sludge (55). The organism contained an inducible
CH3Cl dehalogenase which transferred the methyl group of
CH3Cl to tetrahydrofolate, releasing inorganic chloride
(33). The enzyme has yet to be purified and characterized,
but preliminary studies indicate that activity apparently is dependent
on the presence of ATP (32). An aerobic methylotrophic
Hyphomicrobium sp. capable of growth on CH3Cl
was isolated from industrial sewage (24), and although the
mechanism of dehalogenation was not elucidated, it apparently did not
involve hydrolysis to methanol or oxidation by methane monooxygenase.
A number of aerobic methylotrophic bacteria able to use
CH3Cl as the sole C and energy source have been isolated
(10, 11), and all contained an inducible enzyme system
catalyzing the conversion of CH3Cl to Cl It is noteworthy that the anaerobic CH3Cl utilizer studied
(32, 33) and also the aerobic utilizers investigated
(24, 58) were obtained either from sewage sludge or from
soil at industrially polluted sites. We have adopted an alternative
approach to isolating CH3Cl-degrading microorganisms by
screening soil samples from pristine sites where natural production of
CH3Cl might be expected to occur. The microorganism used in
the investigation described here was isolated from the litter layer of
a woodland soil, an environment where biological release of
CH3Cl by wood-rotting fungi is likely (59). We
describe a study of the degradation of CH3Cl by this
organism and the purification and characterization of the unusual
corrinoid methyltransferase enzyme involved in its dehalogenation.
Isolation and culture of the organism.
A methylotrophic
microorganism designated strain CC495 was isolated from the top 5 cm of
soil in a beech wood in County Down, Northern Ireland, by enrichment
culture using CH3Cl as the sole carbon and energy source (1 g of soil/100 ml of minimal medium in 500-ml flasks containing 0.125 g
of CH3Cl). For enrichment culture and growth experiments,
strain CC495 was grown in 500-ml screw-cap conical flasks, each fitted
with a polytetrafluoroethylene (PTFE) septum and a Mininert valve and
containing minimal medium (100 ml) with the following composition (in
grams per liter): KH2PO4 (4.5),
K2HPO4 (10.5), MgSO4 · 7H2O (0.15), and NH4NO3 (1.5). The
pH of the medium was adjusted to 7.2 with 6 M NaOH, and the medium was
supplemented with a trace element solution (10 ml liter Preparation of cell extracts.
Bacterial cells from
CH3Cl-grown cultures (20 liters) in the late-exponential
phase were harvested by centrifugation for 1 h at
10,000 × g and washed with 50 mM phosphate buffer (pH
7.2). Cells (15 g) were suspended in 20 mM phosphate buffer (pH 7.2) (14 ml) containing 0.5 mM dithiothreitol (DTT) and disrupted by sonication for a total duration of 9 min with an MSE 150-W ultrasonic disintegrator at maximum amplitude. Cooling in an ice bath ensured that
the temperature did not rise above 10°C. The resulting homogenate was
centrifuged for 20 min at 30,000 × g to remove cell debris.
Measurement of oxygen uptake by cell suspensions.
Cells were
harvested as described above, and oxygen consumption by washed cell
suspensions was recorded at 25°C with a Clark-type glass oxygen
electrode (4 ml). Incubation mixtures contained 50 mM phosphate buffer
(pH 7.8), the cell suspension (100 mg [wet wt]), and 2 mM substrate
in a total volume of 3 ml.
Purification of enzyme.
Column chromatography was performed
at 4°C on a Pharmacia fast protein liquid chromatography (FPLC)
system. Cell extract (2 ml) prepared as described above was applied to
a Pharmacia FPLC Mono Q 10/10 anion-exchange column equilibrated with
20 mM phosphate buffer (pH 6.5) containing 0.5 mM DTT. The column was
washed with this buffer (16 ml, 2 ml/min) and then with a linear
gradient of 0 to 0.5 M NaCl in 20 mM phosphate buffer (pH 6.5)
containing 0.5 mM DTT (50 ml, 2 ml/min), and fractions (2 ml) were
collected. Each fraction was dialyzed against 5 liters of 20 mM
phosphate buffer (pH 7.2) containing 0.5 mM DTT for 12 h. Enzyme
activity emerged as a single discrete peak confined to the fractions
eluted at NaCl concentrations between 0.20 and 0.25 M. An aliquot (200 µl) of the fraction with the highest specific activity was applied to
a Pharmacia FPLC Superose 12 column equilibrated with 20 mM phosphate
buffer (pH 7.2) containing 0.5 mM DTT. The column was eluted with this
buffer, and fractions (0.5 ml) were collected. The enzyme eluted from
the column at an elution volume of 1.67 relative to the void volume of
the column.
Activation of enzyme.
For experiments on the
characterization and kinetics of the pure enzyme, activation was
routinely conducted by preincubating the enzyme preparation in 50 mM
phosphate buffer, pH 7.0 (1.7 ml, 0.5 mg of protein/ml), for 60 min at
25°C in the presence of 5 mM DTT and 0.5 mM (aqueous-phase
concentration) CH3Cl in a 20-ml crimped-cap vial. The vial
was then uncapped and allowed to stand at 25°C for 60 min prior to
experimental use of the enzyme so as to ensure that any residual
CH3Cl diffused from the solution. Gas chromatographic
analysis of the activated enzyme preparation detected no
CH3Cl in the solution after this period. In experiments where the effect of reductants other than DTT on activation was examined, the above procedure was used, with the reductant replacing DTT in the preincubation mixture. The enzyme was activated enzymically by replacing DTT with 0.2 mg (0.01 U) of NADH-flavin mononucleotide (FMN) oxidoreductase, 1 mM NADH, and 50 µM FMN. During initial purification of the enzyme, no preassay activation was conducted. Consequently, activation occurred during the assay, resulting in a lag
period during which the reaction rate became progressively faster, but
ultimately it became linear with respect to time. In these experiments
reaction rates were measured only after linearity was achieved.
Enzyme and protein assays.
Methyltransferase activity was
routinely assayed by measuring the production of CH3I when
the activated enzyme preparation was incubated with KI and
CH3Cl. The standard assay was conducted at 25°C in
duplicate 20-ml crimped-cap vials sealed with silicone-PTFE discs and
containing (in a total volume of 1 ml) phosphate buffer (50 mM; pH
7.0), KI (3 mM), CH3Cl (0.5 mM in the aqueous phase), and
0.1 ml of the enzyme preparation (corresponding to ~0.02 mg of enzyme
protein). After incubation for 1.5 to 6 h, the CH3I level was determined by gas chromatography. Glutathione-dependent formaldehyde dehydrogenase, serine hydroxymethyltransferase,
hydroxypyruvate reductase, and 3-hexulose phosphate synthase in cell
extracts were assayed by methods described previously (4, 8, 30, 44). Methanethiol oxidase was assayed by measuring the formation of NADH at 340 nm in the presence of NAD, CH3SH, and
formaldehyde dehydrogenase (50). Formate dehydrogenase was
assayed by measuring the formation of NADH at 340 nm in the presence of
50 mM formate (13). Protein was determined with a Coomassie
Protein Assay Kit (Pierce Chemical Co., Rockford, Ill.) by using bovine
serum albumin as a standard.
Determination of halomethanes and methanethiol.
A
modification of the gas chromatographic method of Harper and Kennedy
(22) was used. Samples of headspace (2 ml) were withdrawn from vials and injected into a Hewlett-Packard (HP) 6890 gas
chromatograph that was fitted with a flame ionization detector and a
glass column (1.5 m by 2 mm) packed with Tenax TA 60-80 and was
operated at a N2 gas flow of 20 ml min Determination of methylated products by GC-MS.
In studies of
the substrate specificity of the methyltransferase, a Hewlett-Packard
5890 series II gas chromatograph linked to an HP 5971 mass selective
detector was used to identify and quantify various methylated products.
For the determination of CH3CN,
CH3NO2, and CH3SCN, the gas
chromatograph was fitted with a Poraplot-Q capillary column (10 m by
0.32 mm). Helium (1 ml min
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
Halomethane:Bisulfide/Halide Ion Methyltransferase, an Unusual
Corrinoid Enzyme of Environmental Significance Isolated from an
Aerobic Methylotroph Using Chloromethane as the Sole Carbon
Source
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ABSTRACT
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
, HS
, Cl
,
Br
, NO2
, CN
, and
SCN
. Spectral analysis indicated that cobalt in the
native enzyme existed as cob(II)alamin, which upon activation was
reduced to the cob(I)alamin state and then was oxidized to methyl
cob(III)alamin. During catalysis, the enzyme shuttles between the
methyl cob(III)alamin and cob(I)alamin states, being alternately
demethylated by the acceptor ion and remethylated by halomethane.
Mechanistically the methyltransferase shows features in common with
cobalamin-dependent methionine synthase from Escherichia
coli. However, the failure of specific inhibitors of methionine
synthase such as propyl iodide, N2O, and Hg2+
to affect the methyltransferase suggests significant differences. During CH3Cl degradation by strain CC495, the physiological
acceptor ion for the enzyme is probably HS
, a hypothesis
supported by the detection in cell extracts of methanethiol oxidase and
formaldehyde dehydrogenase activities which provide a metabolic route
to formate. 16S rRNA sequence analysis indicated that strain CC495
clusters with Rhizobium spp. in the alpha subdivision of
the Proteobacteria and is closely related to strain IMB-1,
a recently isolated CH3Br-degrading bacterium (T. L. Connell Hancock, A. M. Costello, M. E. Lidstrom, and R. S. Oremland, Appl. Environ. Microbiol. 64:2899-2905, 1998). The presence of this methyltransferase in bacterial populations in soil and
sediments, if widespread, has important environmental implications.
![]()
INTRODUCTION
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
and
formaldehyde, with the latter compound undergoing either oxidation via
formate to CO2 or assimilation via the serine pathway. One
of these organisms, Methylobacterium sp. strain CM4,
isolated from soil at a petrochemical plant, has been subjected to more detailed physiological and genetic investigations (58). The observed growth yields with CH3Cl as substrate, and also
the properties of transposon Tn5 insertion mutants with
altered growth characteristics on CH3Cl and other
C1 substrates, suggested that it was unlikely that the
degradative pathway involved an oxygenase or hydrolase. It was
postulated that the bacterium metabolized CH3Cl by initial dehalogenation via a methyltransferase reaction followed by a series of
dehydrogenase-catalyzed oxidations which differed from those involved
in the metabolism of methanol or methylamine by the strain. However, no
CH3Cl dehalogenase activity was obtained in cell extracts
of strain CM4. Recently, a facultative methylotroph, strain IMB-1,
possibly related to strain CM4, was isolated independently by Connell
Hancock et al. (9) by enrichment culture on
CH3Br. Strain IMB-1 also grew on CH3Cl and
CH3I, but no investigation of the enzymology of halomethane
degradation has been reported.
![]()
MATERIALS AND METHODS
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
1)
containing (in milligrams per liter) H3BO3
(500), CuSO4 · 5H2O (40), KI (100),
FeSO4 · 7H2O (200),
MnSO4 · 7H2O (400),
(NH4)6Mo7O24 · 4H2O (200), and ZnSO4 (400). In culture of the
pure organism, the medium was further supplemented with a vitamin
solution (5 ml liter
1) containing (in milligrams per
liter) folic acid (4), p-aminobenzoic acid (200),
and cyanocobalamin (200). CH3Cl (0.15 g) was added as an
aqueous solution to give a concentration in the culture medium, after
equilibration of the gaseous and aqueous phases, of 11.8 mM (30 mM if
partitioning is neglected and the total CH3Cl present is
expressed as a concentration in the aqueous phase). During production
of large quantities of cells for preparation of cell extracts, cultures
were grown in 2-liter conical flasks fitted with PTFE-coated rubber
stoppers and containing 500 ml of medium with a CH3Cl
concentration of 6.9 mM in the aqueous phase after equilibration.
Cultures were incubated at 25°C on a rotary shaker (140 rpm).
CH3Br, CH3I, and CH3SH were tested as growth substrates by replacing CH3Cl in the medium by an
equivalent molar concentration of each compound. These substrates were
added either as a single supplement or as a series of discrete 1-mmol additions; each injection was made after the consumption of the previous pulse so as to avoid inhibition by high initial concentrations of the compounds (9, 34). Other carbon sources examined as growth substrates were methylamine (0.2%, wt/vol), methanol (0.1%, wt/vol), formaldehyde (0.03%, wt/vol), sodium formate (0.1%), glucose
(0.2%), glycerol (0.2%, wt/vol), sodium pyruvate (0.2%), veratric
acid (0.1%), and syringic acid (0.1%).
1. The
oven temperature was programmed from 60 to 120°C at 24°C min
1. Under these conditions, CH3Cl,
CH3Br, CH3I, and CH3SH eluted at
retention times of 1.35, 2.18, 3.47, and 2.18 min, respectively. For
the assay of CH3F, the oven temperature was programmed at a
rate of 24°C min
1 between 40 and 80°C, and
CH3F eluted at 0.25 min. Calibration was against samples of
the headspace above standard solutions (1 ml) of known concentrations
equilibrated at 25°C. The identities of eluting peaks were initially
confirmed by gas chromatography-mass spectrometry (GC-MS). Lower limits
of detection per vial were 0.15 nmol for CH3F, 0.20 nmol
for CH3Cl, 0.35 nmol for CH3Br, 0.35 nmol for
CH3I, and 0.30 nmol for CH3SH.
1) was used as the carrier gas.
After splitless injection of a sample (2 ml) of headspace, the oven
temperature was held at 30°C for 1 min, then programmed at 10°C
min
1 to 220°C. For identification of compounds, ion
currents were monitored at m/e 38, 40, and 41 (molecular
ion, M+) for CH3CN, at m/e 46 and 61 (M+) for CH3NO2, and at
m/e 45, 72, and 73 (M+) for CH3SCN.
For quantification of these compounds, the ion current of the molecular
ion at the retention time of the compound was compared with that given
by headspace above standard solutions of the authentic compound.
1.
Injection was splitless, and volatiles were initially focused on the
first 10 cm of the column by cooling this section in liquid N2. The mass spectrometer was operated in the scanning
mode, and ion currents between m/e 30 and 350 were monitored.
Determination of formate and identification of formaldehyde.
Formate in cell extracts was determined by GC-MS after derivatization
as the anilide (29) by using H13COOH as an
internal standard. Conditions were as described above, except that the
gas chromatograph was fitted with an Ultra 1 capillary column (12 m by
0.2 mm), and after splitless injection of the derivatized sample (1 µl), the oven temperature was held at 66°C for 1 min and then
programmed at 10°C min
1 to 300°C. Ion currents at
m/e 66, 93, 121 (M+), and 122 were monitored.
The molecular ion was used for quantification.
SDS-PAGE.
Sodium dodecyl sulfate-polyacrylamide gel
electrophoresis (SDS-PAGE) was performed with a Pharmacia Phastsystem
gel electrophoresis unit by using commercially prepared gels of 12.5%
polyacrylamide stained with Coomassie blue R. For molecular weight
determination, the following proteins were used in calibration (with
the molecular mass of the subunit in parentheses): rabbit muscle myosin
(205 kDa), Escherichia coli
-galactosidase (116 kDa),
rabbit muscle phosphorylase b (97 kDa), bovine serum albumin
(66 kDa), ovalbumin (45 kDa), rabbit glyceraldehyde-3-phosphate
dehydrogenase (36 kDa), bovine erythrocyte carbonic anhydrase (29 kDa),
bovine pancrease trypsinogen (24 kDa), soybean trypsin inhibitor (20 kDa), and bovine milk
-lactalbumin (14 kDa).
Isoelectric focusing. Isoelectric focusing on a polyacrylamide gel (Phastgel IEF [pH 4 to 6.5], 0.35 mm thick) was conducted by using a Pharmacia Phastsystem. Enzyme protein was dissolved in 20 mM phosphate buffer (pH 7.2), and an aliquot (1 µl, containing approximately 0.2 µg of protein) was run alongside a calibrating mixture of proteins of known pI values. Protein bands were located by staining with Coomassie blue R. Subsequently, gels were silver stained with a Bio-Rad kit to identify any minor protein components.
N-terminal amino acid sequencing. The purified enzyme was separated by electrophoresis on an SDS-12% polyacrylamide gel and electroblotted onto a nitrocellulose membrane. N-terminal sequencing was carried out by Edman degradation with an Applied Biosystems model 477A automated sequencing instrument equipped with on-line phenylthiohydantoin analysis and using a pulsed liquid delivery.
Molecular weight determination.
The molecular weight of the
enzyme was determined by both gel filtration and SDS-PAGE. Gel
filtration of the purified enzyme was conducted on a Pharmacia Superose
12 column eluted with 20 mM phosphate buffer (pH 7.2) containing 0.5 mM
DTT. The column was calibrated with the following reference proteins
(with the molecular mass in parentheses):
-amylase (200 kDa),
alcohol dehydrogenase (150 kDa), bovine serum albumin (67 kDa), and
peroxidase (40 kDa). The molecular weight of the enzyme was also
estimated by comparing the mobility of the purified enzyme with those
of standard reference proteins by SDS-PAGE as described above.
UV-visible light spectroscopy. The absorption spectrum of the purified enzyme between 250 and 750 nm was recorded on a Pye Unicam SP8-200 UV-visible light spectrophotometer at room temperature in a quartz cuvette with a 1-cm light path. The spectrum of the enzyme as isolated was initially obtained, and the cuvette was scanned again after addition of 5 mM DTT and then after subsequent addition of 10 mM CH3Cl.
Metal determinations. Cobalt, copper, iron, magnesium, manganese, nickel, and zinc contents of purified enzyme preparations were measured by flameless atomic absorption spectroscopy on a Varian Spectra AA 300 instrument equipped with a graphite furnace and a Zeeman background corrector. All values were corrected for the metal content of the buffer in which the sample was dissolved.
Chloride analysis. Chloride was determined coulometrically by the Volhard procedure by using a Corning Chloride Analyzer 926.
Chemicals. Sodium [37Cl]chloride (95 atom% 37Cl) and [13C]formic acid (99 atom% 13C) were obtained from Sigma Aldrich Co. Ltd., Poole, Dorset, United Kingdom. Nitromethane, methyl isothiocyanate, ethyl chloride, and methanethiol were also obtained from Sigma Aldrich. Titanium(III) citrate was prepared from titanium(III) chloride as described by Zehnder and Wuhrmann (61). NADH-FMN oxidoreductase (EC 1.6.99.3) from Vibrio harveyii was obtained from Sigma Aldrich, as was formaldehyde dehydrogenase (EC 1.2.46) from Pseudomonas putida.
Determination of 16S rRNA gene sequence. Total DNA was isolated from CC495 cells grown in 50 ml of 2YT medium (45) to an optical density at 590 nm of 0.8 to 1.0. An almost-complete 16S rRNA gene was amplified from total DNA preparations by PCR using the following universal primers (38): forward, 5'-AGAGTTTGATCCTGGCTCAG (positions 8 to 27 [E. coli numbering]); reverse, 5'-AAGGAGGTGATCCAGCCGCA (positions 1541 to 1522). Amplification of the CC495 16S rRNA gene was conducted with Taq+ DNA polymerase (Stratagene) in a buffer supplied by the manufacturer. Reactions were carried out in volumes of 25 µl with deoxynucleoside triphosphates at 200 µM concentrations, 0.15 µM each primer, DNA at 100 to 200 ng, and Taq+ at 0.5 U per reaction. The following temperature profile was used: denaturation at 95°C for 3 min, followed by 30 cycles of 94°C for 40 s, 60°C for 30 s, and 72°C for 1 min. The amplification reactions were performed with a Perkin-Elmer DNA Thermal Cycler 480. The PCR products were purified by using GFX PCR DNA and a Gel Band Purification Kit (Pharmacia Biotech).
Purified PCR products were used in sequencing reactions with the Taq Dye-Deoxy Terminator Cycle Sequencing Kit (Applied Biosystems). The primers used for PCR amplification were also used for sequencing, and more primers were designed after the initial sequencing information was obtained. The nucleotide sequences of both strands were determined by using an automatic sequencer (Applied Biosystems, model 373A). Editing and initial analysis of the sequences were performed with the DNASIS (Hitachi) software package. Searches for nucleotide and amino acid sequence similarities were carried out by using the FASTA and BLAST programs (39) and the EMBL and GenBank databases. Alignments of the sequences were performed with the ClustalW program (53). Phylogenetic analysis of the alignment was accomplished by using the PHYLIP (version 3.57c) package (15) and the TREECON program (56). For the PHYLIP analysis, bootstraps were obtained with the SEQBOOT program (100 data sets were generated). Parsimony analyses were conducted with the DNAPARS programs by using ordinary parsimony and a randomized input order of sequences. For the analyses with the TREECON program, Tajima and Nei correction (51) was used and trees were generated by neighbor joining.Nucleotide sequence accession number. The nucleotide sequence of the 16S rRNA gene of strain CC495 has been assigned GenBank accession no. AF107722.
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RESULTS |
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Characterization and growth of strain CC495.
Cells of strain
CC495 were gram-negative rods which formed round, shiny, smooth, and
faintly pink colonies when grown on agar plates composed of mineral
medium supplemented with vitamins and incubated in an atmosphere of
CH3Cl (2%, vol/vol). Strain CC495 was able to use glucose,
glycerol, pyruvate, and methylamine as growth substrates, but not
methane, methanol, formaldehyde, formate, veratrate, or syringate. When
first isolated, strain CC495 could be cultured on CH3Cl
only as part of a stable consortium with another microorganism.
However, supplementation of the culture medium with cyanocobalamin (1 mg liter
1) allowed the organism to be grown in pure
culture on CH3Cl. In the absence of cyanocobalamin or when
an equimolar concentration of inorganic cobalt was substituted for
cyanocobalamin, no growth was observed. Cyanocobalamin supplementation
of the medium was not required for the growth of the organism on methylamine.
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Induction of CH3Cl-degrading activity and pathway of
carbon assimilation.
Resting cells of strain CC495 grown on
CH3Cl rapidly oxidized CH3Cl,
CH3Br, CH3I, and formaldehyde. Formate and
CH3SH were also oxidized, although comparatively slowly,
but CH3F, chloroethane, methanol, and methylamine were not
(Table 1). These observations suggest
that oxidation of CH3Cl occurred via formaldehyde but did
not involve an initial hydrolytic cleavage to form methanol and
chloride. Cells consumed 1.48 ± 0.07 nmol of O2 for
each nanomole of CH3Cl degraded, indicating complete
oxidation of the compound to CO2 and Cl
. The
low rate of formate utilization could signify that oxidation of
formaldehyde does not proceed via the linear route through formate to
CO2. However, hexulose-6-phosphate activity was not detected in cell extracts, implying that oxidation did not occur by the
cyclic ribulose monophosphate pathway, which many non-methane-utilizing methylotrophs use (2). Moreover, substantial
glutathione-dependent formaldehyde dehydrogenase activity (19.5 nmol/min/mg) and significant formate dehydrogenase activity (1.9 nmol/min/mg) were present in cell extracts. It therefore seems probable
that the sluggish oxidation of formate by whole cells may reflect the
high Km (~15 mM) of bacterial formate
dehydrogenases isolated to date (3, 13).
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Degradation of CH3Cl in cell extracts.
When cell
extracts of strain CC495 were incubated with 1.4 mM CH3Cl
in 50 mM phosphate buffer (pH 7.8) in the presence of 1 mM NADH and 0.5 mM DTT, the halocarbon was consumed at a rate of 2.2 nmol/mg/min for
3 h, after which the rate of utilization slowly declined. In the
absence of supplemental NADH, degradation of CH3Cl
proceeded at a rate ca. 40% of that exhibited in the presence of the
cofactor, but only after an initial lag period of approximately 1 h. In both instances, disappearance of CH3Cl was
accompanied by stoichiometric release of Cl
. Although
formaldehyde could not be detected by GC-MS in cell extracts after
incubation with CH3Cl, formation of stoichiometric quantities of formate was demonstrated (Fig.
4). Over 10 h, approximately 50%
conversion of 17 mM CH3Cl to formate was observed. After
dialysis of cell extracts against 5 liters of 20 mM phosphate buffer
(pH 7.8) containing 0.5 mM DTT, CH3Cl-degrading activity in
the presence of 1 mM NADH showed an increase to 5.7 nmol/mg/min, while
activity in the absence of NADH was similarly enhanced.
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(up to 500 mM) used in
gradient elution, the effects of Cl
and other anions on
CH3Cl-degrading activity in dialyzed cell extracts were
examined (Table 2). Preliminary
experiments had established that phosphate buffer did not inhibit the
enzyme reaction at concentrations below 100 mM. All the anions tested,
including many which were not halide or pseudohalide ions, showed
significant inhibition of CH3Cl degradation at 20 mM, and
all displayed substantial inhibition of activity at 100 mM. To shed
light on this phenomenon, dialyzed cell extracts were incubated with 3 mM I
, 0.5 mM DTT, and 0.5 mM CH3Cl in 50 mM
phosphate buffer, and the headspace was monitored by gas
chromatography. The formation of substantial quantities of a compound
with a retention time similar to that of CH3I was observed,
and its identity was confirmed by GC-MS. After an initial lag period of
about 7 h, during which the rate of CH3I formation
gradually increased, the production of CH3I became linear
with respect to time (Fig. 5). The
addition of 1 mM NADH increased the lag period slightly but did not
significantly affect the maximal rate of CH3I formation.
CH3I was not detectable in control samples to which boiled
cell extract had been added. The behavior of the CH3Cl
degradation system as a transhalogenation system in the presence of
halide ions allowed the development of a much more sensitive assay for
the enzyme based on the methylation of I
in the presence
of CH3Cl rather than on CH3Cl disappearance. By
measuring the rate of CH3I formation after the initial lag period (which presumably represents the period required for
activation), enzyme activity was monitored where indicated during the
purification of the CH3Cl-degrading system described below.
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Purification of enzyme.
The results of a typical enzyme
purification are summarized in Table 3,
and results of SDS-PAGE of the fractions obtained at each purification
stage are shown in Fig. 6. Purification
by this procedure was 20-fold, and the overall yield was 46%. SDS-PAGE of the purified enzyme yielded a single band, indicating the apparent homogeneity of the preparation (Fig. 6).
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N-terminal amino acid sequence. The N-terminal amino acid sequence of the purified enzyme was identified as H2N- Ala-Thr-Val-Gly-Lys-Met-Thr-Ser-Arg-Glu-Arg-Met-Phe-Ala-Ala-Val-Thr-Met. A search of the EMBL and SwissProt databases using the FASTA and BLITZ programs revealed no significant homology with other cobalamin-containing enzymes for which sequences are known or with any other reported sequence.
Enzyme activation. As cell extracts passed through the various stages of purification, the initial lag period displayed by the enzyme during the assay became progressively shorter, signifying faster activation of the enzyme. Pure enzyme required a period of about 1 h before the rate of enzyme reaction became linear with respect to time when it was assayed without preincubation under standard assay conditions in the presence of 0.5 mM DTT. The effects of preincubation of pure enzyme with CH3Cl and various concentrations of DTT on the duration of the lag period and on the extent of enzyme activation were investigated by using pure enzyme previously dialyzed against 20 mM phosphate buffer (pH 7.0) (Fig. 7).
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Stability of the enzyme.
Preparations of the purified enzyme
had a half-life of 90 h in 50 mM phosphate buffer (pH 7.0)
containing 0.5 mM DTT at 4°C and could be frozen at
70°C for 3 months without significant loss of activity. Normal laboratory lighting
did not affect the stability of the enzyme.
Influence of enzyme concentration.
Under standard assay
conditions with 3 mM I
as the substrate, the initial
velocity of the reaction was directly proportional to the enzyme
concentration at protein concentrations from 15 to 120 µg
ml
1. The rate of CH3I formation was linear
with respect to time over approximately 6 h at 25°C.
Molecular weight. Upon gel filtration of the purified enzyme, activity emerged as a single discrete peak at a relative elution volume corresponding to a molecular weight of 68,000. SDS-PAGE of the pure enzyme yielded a single band corresponding to a molecular weight of 66,000, indicating that the enzyme was monomeric (Fig. 6).
Metal content, spectral properties, and isoelectric point of the
enzyme.
Purified enzyme preparations were analyzed for various
metal ions by atomic absorption spectroscopy. The mean cobalt content of several preparations was 13.7 ± 0.6 nmol mg
1 of
protein. Based on a molecular weight of 67,000 for the enzyme, a molar
ratio of cobalt to enzyme of 0.92 was calculated. No iron, zinc,
manganese, copper, nickel, or magnesium was detected in enzyme preparations.
1 cm
1 for
cob(II)alamin (18), measurement of the absorbance of the unactivated enzyme gave a molar ratio of cobalt to enzyme of 0.83, a
value consistent with that obtained by atomic absorption.
|
Influence of pH and temperature.
The effect of pH on enzyme
activity was measured under standard conditions in 50 mM
2,2-dimethylsuccinate, phosphate, Tris, and glycine buffers spanning a
pH range from 5 to 10. The activated enzyme showed maximal
methyltransferase activity between pH 6.0 and 7.0, with the velocity of
the reaction falling rapidly below pH 6.0 and above pH 8.5. When
assayed under standard conditions for 2 h, the optimum temperature
for the enzyme reaction was 45°C. Rapid denaturation of the enzyme
occurred at 60°C. The activation energy of the enzyme reaction
between 15 and 40°C, determined by an Arrhenuis plot, was 58.4 kJ
mol
1.
Substrate range.
The relative rates of methylation of a
variety of monovalent anions by the enzyme were measured by using
CH3Cl as the methyl donor and 10 mM acceptor ion (Table
4). Under these conditions the best
substrate was I
, but methyl transfer to the other halide
ions, Br
and Cl
, also occurred readily.
However, there was no detectable formation of CH3F from
F
, even at concentrations of 50 mM F
. The
pseudohalide ions, CN
and SCN
, were poor
substrates; the latter ion showed detectable methylation only at a
concentration of 50 mM. Some enzymic conversion of
NO2
to CH3NO2 was
also observed. Most significantly in terms of the metabolic role of the
enzyme, methyl transfer to HS
occurred readily, resulting
in the formation of CH3SH.
|
Kinetic parameters.
The steady-state kinetics of the
methyltransferase reaction were investigated by using Cl
,
Br
, I
, and HS
as acceptor
ions and CH3Cl, CH3Br, and CH3I as
methyl donors. Normal Michaelis-Menten kinetics were observed with all
substrate combinations except at concentrations of I
and
HS
above 3 and 0.2 mM, respectively. Under these
conditions significant departures from linearity were noted, indicating
some substrate inhibition at higher concentrations. In the case of
HS
, inhibition was apparently due to deactivation of the
enzyme, and this could be greatly reduced by increasing the
concentration of DTT to 20 mM in the enzyme assay. This modification
allowed normal Michaelis-Menten kinetics to be exhibited up to 1 mM
HS
. Lineweaver-Burk treatment of the data yielded
apparent Km and Vmax
values for methyl donors and acceptor ions (Table
5). Experiments were not conducted with
CH3SH as the methyl donor because no detectable methyl
transfer from this compound to any acceptor ion was observed (Fig.
9). The apparent
Km and Vmax values of the
enzyme for CH3Br and CH3Cl as methyl donors
were measured in the presence of 3 mM I
as the acceptor
ion, while the kinetic parameters for CH3I were measured by
using 120 mM Cl
as the acceptor ion. The apparent
Km and Vmax values of the
enzyme for Cl
, Br
, and HS
as
acceptor ions were determined in the presence of 0.4 mM
CH3I as the methyl donor, while these parameters for
I
were measured with 0.5 mM CH3Br as the
methyl donor.
|
|
,
Br
, and HS
as acceptor ions are not
strictly analogous to that obtained for I
because of the
difference in methyl donors. Nevertheless, on mechanistic grounds it
seems unlikely that the apparent Vmax for CH3I with I
as the acceptor ion will diverge
substantially from the value given in Table 5 for the apparent
Vmax for CH3I with Cl
as the acceptor ion. One measure of the internal consistency of results
in Table 5 can be obtained by a comparison of the apparent
Vmax for CH3I with Cl
as the acceptor ion with the apparent Vmax of
Cl
with CH3I as the methyl donor. The level
of agreement appears reasonable, considering that concentrations of the
acceptor ion and methyl donor, while high (~10
Km), were not sufficient to completely saturate
the enzyme. Additional confirmation that the kinetic parameters
obtained for a given acceptor ion can be considered largely independent
of the methyl donor is provided by the very similar
Km and Vmax values for
Cl
obtained with CH3Br as a methyl donor
(11.1 mM and 120 U/mg, respectively) compared with those obtained with
CH3I as a methyl donor, which are shown in Table 5.
Effect of inhibitors. Methylating activity was examined in the presence of a variety of possible inhibitors. The purified enzyme was activated in the presence of 5 mM DTT and 0.5 mM CH3Cl and then preincubated with the putative inhibitor for 20 min before the addition of substrate. In the presence of DTT, propyl iodide is a specific inhibitor of most cobalamin-dependent enzymes, blocking enzyme action by forming a propylcob(III)alamin derivative of the enzyme. The inhibition can normally be reversed by photolysis of the propyl-cobalt bond with light (52). However, no inhibition of methyl transfer by propyl iodide at a final concentration of 0.05 or 0.5 mM was observed either in the light or in the dark. Incubation of unactivated enzyme with this compound prior to normal activation also failed to produce detectable inhibition.
A number of substrate analogues of the methyl donor (CH3F, CH3OH, CH2Cl2, CHCl3, CCl4, and CH3CH2Cl) which had previously been shown to be inactive as substrates for the methyltransferase were tested at a concentration of 0.5 mM as possible competitive inhibitors, but all failed to display significant inhibition of methyl transfer. The monovalent ions F
and NO3
,
neither of which would serve as acceptor ion substrates for the
methyltransferase, were also not effective as competitive inhibitors at
a concentration of 1 mM. The chelating agent EDTA (1 mM) did not
inhibit the enzyme, nor did Hg2+ (0.1 mM), which is known
to demethylate methylcob-(III)alamin (42). Enzyme
activity was, however, completely abolished by 6 M urea and could not
be restored upon dialysis and addition of aquocobalamin or
methylcobalamin. When activated enzyme was incubated in the standard
assay under an atmosphere of N2O, a specific inhibitor of
cobalamin-dependent methionine synthase (6), no decrease in
the rate of enzyme reaction was observed.
Metabolism of the product of the methyltransferase reaction in
vivo.
The irreversible formation of methanethiol from
CH3Cl and HS
catalyzed by the
methyltransferase suggests that the metabolism of CH3Cl in
vivo by strain CC495 may proceed via this compound. A methanethiol
oxidase has previously been purified and characterized from a
Hyphomicrobium sp. and has been shown to catalyze the
formation of formaldehyde, sulfide, and hydrogen peroxide from
methanethiol in the presence of oxygen (50). Extracts of
cells of strain CC495 in the late-exponential phase were therefore
assayed for the presence of methanethiol oxidizing activity by
measuring formaldehyde formation from methanethiol by a coupled assay
with formaldehyde dehydrogenase. A methanethiol oxidase activity of 1.6 nmol/mg of protein/min was found.
| |
DISCUSSION |
|---|
|
|
|---|
The facultative methylotroph strain CC495 is the first aerobic CH3Cl-degrading organism from which a specific dehalogenating enzyme has been isolated. Phylogenetic analysis (Fig. 2) indicates that the organism is closely related to two other facultative methylotrophs recently isolated: strain ER2, which utilizes the methyl groups of N-methylcarbamates as its sole carbon source (54), and strain IMB-1, which is capable of growth on CH3Cl, CH3Br, and CH3I (9). Like both of these organisms, strain CC495 is incapable of growth on methanol and formate but can use methylamine as its sole carbon source. However, during growth on C1 substrates, neither strain ER2 nor strain IMB-1 has the exceedingly high requirement for cyanocobalamin exhibited by strain CC495 during growth on CH3Cl. These strains, together with three other recently isolated novel strains assigned to a new genus, Pseudoaminobacter, form a distinct clade within the Rhizobium cluster of the alpha subdivision of the Proteobacteria (Fig. 2). The Rhizobium genus consists of aerobes capable of fixing atmospheric nitrogen, often in symbiotic associations with plant hosts. Strain CC495 does not appear to have a close phylogenetic relationship to Methylobacterium extorquens CM4, an organism, isolated from Russian soil, which is capable of growth on CH3Cl but, unlike strain CC495, can utilize methanol as a carbon source (10, 11, 58).
CH3Cl degradation in strain CC495 was clearly inducible.
Although CH3Br degradation by strain IMB-1 initially
appeared constitutive (9), it has now been shown to be
induced by very low concentrations of CH3Br
(46). Growth of strain CC495 on CH3Cl caused
induction of at least two additional proteins not present in
methylamine-grown cells (Fig. 3). It is perhaps significant that the
molecular masses of these proteins, 67 and 29 kDa, are very similar to
those of two proteins with masses of 65 and 35 kDa induced by growth of M. extorquens CM4 on CH3Cl but not on methanol
(55). On the basis of the latter evidence, inter alia, it
was proposed that a methyltransferase reaction, rather than a
hydrolytic cleavage to yield methanol, was involved in the initial
dehalogenation of CH3Cl by M. extorquens CM4.
Whole-cell studies with strain CC495 also suggested that the metabolism
of CH3Cl, although proceeding via formaldehyde, did not
involve an initial hydrolysis to methanol (Table 1). Cell extracts from
strain CC495 showed rapid and quantitative conversion of
CH3Cl to formate when incubated in the presence of NADH and
DTT (Fig. 4). Attempts to purify the CH3Cl-degrading activity by anion-exchange chromatography were initially unsuccessful because of the inhibitory effects of high concentrations of anions on
CH3Cl degradation (Table 2). This phenomenon is
attributable in the case of Cl
to the ability of the ion
to act as an acceptor for methyl transfer from methylcobalamin, leading
to resynthesis of CH3Cl. Inhibition by the pseudohalide
ions SCN
and CN
and also
NO2
is probably due to these rather poor
substrates for the methyltransferase blocking the active site of the
enzyme and effectively acting as competitive inhibitors. Inhibition by
Br
and I
is more difficult to explain but
may be related to these halide ions or the halomethanes formed from
them behaving as inhibitors of a subsequent stage in enzymic processing
of the methyl group, e.g., methanethiol oxidase.
In the absence of information regarding the identity of the normal
acceptor ion substrate for the methyltransferase enzyme in vivo, the
use of I
as an acceptor ion enabled assay of the enzyme
during purification by measurement of CH3I formation in the
presence of CH3Cl. The purified enzyme displayed
considerable stability, and in contrast to many cobalamin-containing
enzymes (49, 52), catalysis was not affected by light in the
visible range. As isolated the enzyme was inactive and exhibited a lag
period in the standard assay during which activation of the enzyme
occurred (Fig. 5). In order to eliminate this lag period, activation of
the enzyme before assay was necessary by preincubation with 5 mM DTT
and a methyl donor (normally 0.5 mM CH3Cl). Other thiols
such as mercaptoethanol and reduced glutathione could also be used as
reductants but were less effective than DTT in the activation process.
Aquocobalamin, which promotes the activation of methionine synthase by
DTT (52), did not stimulate DTT-mediated activation of the
methyltransferase. Neither NADH nor titanium citrate, which is required
in reductive activation of some corrinoid-dependent methyl transfer
reactions (49), produced measurable activation of the
purified enzyme. Spectral analysis showed that in the unactivated
enzyme the cobalt of the prosthetic group existed as cob(II)alamin,
which upon activation by treatment with DTT and CH3Cl, was
first reduced to the cob(I)alamin state and then oxidized to
methylcob(III)alamin. This change in the valence of the cobalt atom
upon activation was reflected in the observed change in the isoelectric
point of the protein.
The substrate range of the enzyme as regards methyl donors appears
restricted to CH3Cl, CH3Br, and
CH3I, with CH3Cl, on the basis of the relative
specificity constant
Vmax/Km, acting as the
best substrate (Table 5). A variety of monovalent anions behave as
acceptor substrates for the enzyme, of which I
and
HS
are by far the best in terms of
Vmax/Km, but
CI
and Br
were also rapidly methylated
(Table 5). The enzyme catalyzed significant methylation, albeit at a
comparatively low level, of the pseudohalide ions, CN
and
SCN
, and in addition NO2
behaved as an acceptor ion, but F
did not (Table 4).
Both the reductive methylation process involved in enzyme activation
and the nature of the reaction catalyzed by the methyltransferase have
features in common with those of the cobalamin-dependent methionine
synthase from E. coli (5, 6, 16, 52). Methionine synthase catalyzes the transfer of a methyl group from
methyltetrahydrofolate to homocysteine, generating tetrahydrofolate and
methionine. Methionine synthase requires initial reductive methylation
in which a reductant such as a thiol converts the cob(II)alamin enzyme
to a cob(I)alamin intermediate, which is then methylated by
S-adenosylmethionine to form the catalytically active
methylcob(III)alamin enzyme. During catalysis the enzyme then shuttles
between the methyl cob(III)alamin and cob(I)alamin states, being
alternatively demethylated by homocysteine and remethylated by
methyltetrahydrofolate. A broadly similar model for the mechanism of
the methyltransferase reaction can be proposed, differing principally
in that the methyl donor substrate (CH3X, where X is Cl,
Br, or I) also acts as the methyl donor in the reductive activation
process. Nevertheless, as with methionine synthase, reductive
activation of the enzyme can be accomplished not only by chemical
reductants such as DTT but also by physiological reducing systems such
as NADH-FMN oxidoreductase. This observation probably accounts for the
stimulatory effects of NADH on CH3Cl degradation in
unpurified cell extracts. A major difference between methionine
synthase and the methyltransferase is that with the latter enzyme, the
methylated product CH3Y (where Y is Cl, Br, or I) can be
recycled as the methyl donor substrate (Fig. 9). If the acceptor ion is
HS
, the reaction proceeds in one direction only, because
CH3SH cannot act as a methyl donor substrate. However, if
the halogen of the acceptor ion differs from that of the halomethane
initially present as the methyl donor, the relative proportions of each
halomethane and each halide ion at equilibrium will vary depending on
the initial concentration of each substrate and the kinetic parameters associated with each. Consequently, the methyltransferase effectively behaves as a transhalogenation system which can be driven in a given
direction by manipulating the concentrations of each substrate.
The failure of the specific methionine synthase inhibitor, propyl iodide, and various substrate analogues, such as ethyl chloride, CH2Cl2, and CHCl3, to cause detectable inhibition of the methyltransferase betokens a highly specific and sterically constrained binding site on the enzyme for the methyl donor substrate. The surprising observation that Hg2+, which is known to demethylate methylcob(III)alamin in a nonphysiological reaction (42), did not affect enzyme activity could imply that the cobalamin prosthetic group is in a site in the protein that is inaccessible to cations of this size. Such a protected location would also help to explain the unusual stability of this corrinoid enzyme to both light and oxygen. However, the complete insensitivity of the methyltransferase to the specific methionine synthase inhibitor, N2O, is difficult to rationalize.
An important point with regard to the functioning of the
methyltransferase in vivo is the identity of the acceptor ion. The ready catalysis of the reaction of HS
with
CH3Cl to form CH3SH seems to implicate
HS
as the physiological acceptor ion, particularly since
the reaction is highly exergonic (7) and hence is unlikely
to be reversible under the conditions of enzyme catalysis.
Nevertheless, the rather high Km of the enzyme
with HS
and the low turnover number of the enzyme (15 min
1 with HS
as the substrate) tends to
militate against such a role. However, the use of DTT as a chemical
activation system for the enzyme may be partly responsible for the low
turnover number observed. Studies on the methionine synthase from
E. coli have demonstrated that the use of an endogenous
reduced triphosphopyridine nucleotide-dependent flavoprotein system for
activation rather than DTT doubled the turnover number of the enzyme
(17). Also, the methyltransferase constitutes a
comparatively high proportion (~5%) of the total soluble protein of
the cells, which may compensate for its relative inefficiency as a
catalyst. Moreover, cell extracts contain significant methanethiol
oxidase activity, providing a metabolic route from CH3SH to
formaldehyde within the organism. Although compelling, this evidence is
not conclusive, and further investigations are clearly necessary to
establish unequivocally that HS
is the physiological
acceptor for the enzyme during CH3Cl degradation. A
demonstration that the 29-kDa protein that is coinduced with the
methyltransferase by the growth of strain CC495 on CH3Cl is involved in the metabolism of methanethiol would provide strong support
for this hypothesis.
It seems quite feasible that the other two CH3Cl-degrading strains recently isolated, M. extorquens CM4 (58) and strain IMB-1 (9), share a methyltransferase pathway for metabolic degradation of CH3Cl similar to that of strain CC495. The molecular weights of the two proteins induced by the growth of M. extorquens CM4 on CH3Cl are very similar to those induced by the growth of strain CC495 on CH3Cl. Moreover, in a very recent report (57) it has been concluded, on the basis of Tn5 mutagenesis and subsequent DNA sequence analysis of the genes, that catabolism of CH3Cl by strain CM4 probably involves a corrinoid-dependent methyltransferase enzyme. However, studies with cell extracts suggest that in this organism, unlike strain CC495, the methyl group is apparently transferred from CH3Cl to tetrahydrofolate. The failure of CH3F to act either as a substrate or as a competitive inhibitor for the methyltransferase of strain CC495 is also significant in the light of the observations that CH3F was not a growth substrate for IMB-1 and did not affect its ability to grow on or oxidize CH3Br.
It is interesting to speculate on the possible ecological niches occupied by such CH3Cl-degrading bacteria and the environmental implications of the widespread distribution in microorganisms of methyltransferase enzymes of the type described in this paper. It is difficult to envisage an organism utilizing atmospheric CH3Cl as a major carbon and energy source, given the low background concentrations of the gas in the troposphere. However, strain CC495 was isolated from an environment where, as a result of CH3Cl release by wood-rotting fungi (59), the concentrations of CH3Cl were probably locally enhanced sufficiently to allow the induction of the CH3Cl-degrading system and the utilization of the halocarbon as a significant source of carbon and energy for the organism. In view of the high vitamin B12 requirement by strain CC495 during CH3Cl metabolism, such degradation would have to occur within a consortium of two or more microorganisms which could satisfy the demand for this coenzyme. A variety of microhabitats where biological CH3Cl production can lead to sufficiently elevated concentrations of the gas to permit CH3Cl-dependent growth probably exist both in the soil and on the surfaces of plants. Investigations by Harper et al. (21) have suggested the presence of colonies of CH3Cl-metabolizing microorganisms in the lenticels of potato tubers. These pores represent the main points of efflux of CH3Cl generated within the tuber.
If the methyltransferase found in strain CC495 occurs widely in the
bacterial populations of soil and sediments, several environmentally significant biotransformations could be mediated. We postulate that,
under aerobic conditions, the methyltransferase will simply convert
CH3Cl to CH3SH, which will be oxidized by the
organism via HCHO with concomitant HS
release.
HS
will then be recycled to act as an acceptor ion for
further degradation of CH3Cl or, alternatively, for
degradation of CH3Br and CH3I, since these
halomethanes are also enzyme substrates even if they are not
necessarily inducers of enzyme expression. By contrast, under low
O2 tensions or in the presence of high concentrations of
sulfide, where the limiting degradative step is oxidation of CH3SH, the methyltransferase provides a mechanism for the
conversion of CH3Cl, CH3Br, and
CH3I to CH3SH as the end product. Such
conditions are likely to exist in anoxic sediments. Oremland et al.
(37) showed that the conversion of CH3Br to
CH3SH could take place abiotically in salt marsh sediments,
which consequently may behave as sinks for CH3Br. Little
abiotic transformation of CH3Cl was recorded under such
conditions by these workers, but if bacterial populations with the
methyltransferase activity of strain CC495 are present in these
environments, they could represent an important biological sink for
CH3Cl. Preliminary, as yet unpublished studies by Coulter
et al. (9a) with CH3Cl-grown resting-cell
suspensions of strain CC495 incubated in 4 mM CH3Cl and 2 mM H2S demonstrate almost stoichiometric conversion of
HS
to CH3SH within 2 h even under fully
aerobic conditions. The transhalogenating potential of the
methyltransferase in the presence of halide ions raises the possibility
that in marine environments, where Cl
concentrations will
normally be of the order of 0.5 M, rapid conversion of
CH3Br and CH3I to CH3Cl may also
occur, particularly under anoxic conditions. Unpublished studies in
this laboratory with CH3Cl-grown resting-cell suspensions
of strain CC495, incubated under N2 in seawater diluted
1:4, indicate quantitative conversion of CH3Br and
CH3I to CH3Cl within 2 h; even under
aerobic conditions, conversion exceeded 70%. Considered in the context
of the fact that chemical reaction of CH3I and
CH3Br with Cl
at average surface temperatures
in the sea has a half-life of about 3 weeks (14, 60), these
observations suggest that the implications for atmospheric halomethane
budgets of the presence of bacteria possessing the methyltransferase
enzyme in the marine environment are of some significance.
One possible application for strain CC495 is to enhance the biodegradation of CH3Br after it is used for agricultural fumigation of soils in the field and under glass. Connell Hancock et al. (9) have argued that seeding soils with live cells of mass-cultured strain IMB-1 might be a viable option for reducing the postfumigation release of CH3Br to the atmosphere, thereby minimizing the undesirable effects of the use of the bromocarbon on stratospheric ozone.
| |
ACKNOWLEDGMENT |
|---|
This study was supported by EC Environment and Climate Research Programme contract ENV4-CT95-0086.
| |
FOOTNOTES |
|---|
* Corresponding author. Mailing address: Microbial Biochemistry Section, School of Agriculture and Food Science, The Queen's University of Belfast, Newforge Lane, Belfast, BT9 5PX, United Kingdom. Phone: 44-1232-255343. Fax: 44-1232-669551. E-mail: D.Harper{at}qub.ac.uk.
| |
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