Previous Article | Next Article ![]()
Journal of Bacteriology, December 1999, p. 7493-7499, Vol. 181, No. 24
Department of Chemistry and Biochemistry, and
Cooperative Institute for Research in Environmental Sciences,
University of Colorado, Boulder, Colorado 80309-0215
Received 19 July 1999/Accepted 24 September 1999
There is current interest in biological sources of acetone, a
volatile organic compound that impacts atmospheric chemistry. Here, we
determined that leucine-dependent acetone formation is widespread in
the Vibrionaceae. Sixteen Vibrio isolates, two
Listonella species, and two Photobacterium
angustum isolates produced acetone in the presence of
L-leucine. Shewanella isolates produced much less acetone. Growth of Vibrio splendidus and P. angustum in a fermentor with controlled aeration revealed that
acetone was produced after a lag in late logarithmic or stationary
phase of growth, depending on the medium, and was not derived from
acetoacetate by nonenzymatic decarboxylation in the medium.
L-Leucine, but not D-leucine, was converted to
acetone with a stoichiometry of approximately 0.61 mol of acetone per
mol of L-leucine. Testing various potential leucine
catabolites as precursors of acetone showed that only
There is current interest in the
role of acetone in atmospheric chemistry and in determining
natural and anthropogenic sources of acetone. Acetone has been found in
the upper troposphere and lower stratosphere in surprisingly
large amounts and may be an important contributor to the formation of
odd hydrogen radicals (OH plus HO2) and the sequestration
of nitrogen oxides as peroxyacetylnitrate (2, 38, 44).
While some of the acetone found in the atmosphere results from
photochemical reactions of natural and anthropogenic hydrocarbons, direct emissions from biological sources may be important (10, 45). The atmospheric oxidation of various
biogenic hydrocarbons, such as 2-methyl-3-buten-2-ol and various
monoterpenes, also gives rise to the secondary production of
acetone (14, 27).
There are several known biological sources of acetone. Those best
characterized include enzymatic decarboxylation of acetoacetate in
certain bacteria, such as clostridia (16) and Bacillus
polymyxa (24), and nonenzymatic decarboxylation of
acetoacetate in animals (47). Other biogenic acetone sources
of uncertain magnitude and mechanism include seedlings of oil seed
plants (39), branches of various plants (22),
conifer buds (31), and wounded pasture grasses and clover
(10, 25). Recently, we described the production of acetone
in marine Vibrio species (40). Acetone formation was dependent on the presence of L-leucine in the growth
medium and was repressed by glucose. These findings suggested that an inducible leucine catabolic pathway, similar to that described for
pseudomonads (37), might give rise to this ketone. In the pathway worked out in Pseudomonas putida (36),
leucine oxidation occurs in the sequence shown in Fig.
1 (right), giving rise to acetoacetate
and acetyl-coenzyme A (CoA). In P. putida, the acetoacetate is further metabolized to acetyl-CoA via succinyl-CoA transferase and acetoacetyl-CoA thiolase (49). Possibly, a similar
leucine catabolic pathway may function in vibrios, but with
enzymatic or nonenzymatic decarboxylation of the acetoacetate
formed.
0021-9193/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
Acetone Formation in the Vibrio Family: a New
Pathway for Bacterial Leucine Catabolism
![]()
ABSTRACT
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
-ketoisocaproate was efficiently converted by whole cells to
acetone. Acetone production was blocked by a nitrogen atmosphere but
not by electron transport inhibitors, suggesting that an
oxygen-dependent reaction is required for leucine catabolism. Metabolic
labeling with deuterated
(isopropyl-d7)-L-leucine revealed that the
isopropyl carbons give rise to acetone with full retention of deuterium
in each methyl group. These results suggest the operation of a new
catabolic pathway for leucine in vibrios that is distinct from the
3-hydroxy-3-methylglutaryl-coenzyme A pathway seen in pseudomonads.
![]()
INTRODUCTION
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References

View larger version (19K):
[in a new window]
FIG. 1.
Metabolic pathway for leucine catabolism in
Pseudomonas species (right, solid arrows; redrawn from
reference 36) and possible pathways for
leucine-dependent acetone formation in Vibrio species (left
and right, dashed arrows). Pathways A and B are discussed in the text.
The isopropyl moiety of leucine is shown fully deuterated to help trace
the origin of acetone in each pathway as discussed in the text.
Abbreviations: HIV, 3-hydroxyisovaleric acid; HMG-CoA,
3-hydroxy-3-methylglutaryl-CoA; IV-CoA, isovaleryl-CoA;
-KIC,
-ketoisocaproic acid; MC-CoA, 3-methylcrotonyl-CoA; MG-CoA,
3-methylglutaconyl-CoA; FAD, flavin adenine dinucleotide.
Other pathways for leucine catabolism in bacteria result in the
production of either 3-methyl-1-aminobutane or 3-methylbutanal. Proteus vulgaris is known to have a neutral amino acid
decarboxylase that is very active with L-leucine
yielding 3-methyl-1-aminobutane (12). However, the
metabolic role of this decarboxylation pathway is uncertain
(5). Studies with P. vulgaris and
Streptococcus lactis have also revealed significant
metabolism of L-leucine via transamination to
-ketoisocaproic acid, followed by decarboxylation to 3-methylbutanal
(33, 43). Whether 3-methyl-1-aminobutane and 3-methylbutanal
are further metabolized in these bacteria is uncertain. Here we have
examined the underlying mechanism of acetone formation in
Vibrio, Listonella, and Photobacterium
isolates metabolizing L-leucine. In contrast to what
was found for the leucine-degradative pathway in pseudomonads and the
acetoacetate decarboxylation pathway for acetone formation in bacilli
and clostridia, it appears that these marine bacteria form acetone by a
new type of pathway.
| |
MATERIALS AND METHODS |
|---|
|
|
|---|
Chemicals. L-Leucine-5,5,5-d3 (98 atom% deuterium [D]) was obtained from Cambridge Isotope Laboratories (Andover, Mass.). (Isopropyl-d7) L-leucine (98.4 atom% D) was obtained from CDN Isotopes (Quebec, Canada). 3-Hydroxyisovaleric acid was obtained from TCI America (Portland, Oreg.). All of the other chemicals were of analytical grade and were obtained from Sigma Chemical Co. (St. Louis, Mo.) or Aldrich Chemicals (Milwaukee, Wis.).
Bacterial strains and media.
The sources of strains used
here are summarized in Table 1.
Additional marine Vibrio isolates were obtained from estuary sediments at two coastal sites in southern California (Del Mar and Los
Penasquitos marsh) by plating on TCBS agar (35) as described previously (40). The strains were characterized as
Vibrio splendidus by the methods described earlier
(40) and the methods of Ortigosa et al. (41). All
strains were maintained frozen at
70°C in 7% (vol/vol) dimethyl
sulfoxide.
|
1. For acetone analysis, 3-ml samples were removed for
determination of optical density at 600 nm (OD600), the
cells were then removed by microcentrifugation (3 min at
10,000 × g), and acetone in the culture fluid was
determined as described below.
For the growth of P. putida PpG2, a wild-type strain used to
deduce the pseudomonad leucine catabolic pathway (36), two media were used: a mineral salts medium H (13), containing
20 mM L-leucine as the sole carbon source, and a tryptone
leucine medium, containing medium H minus ammonium chloride, 1%
tryptone, and 20 mM L-leucine.
Analytical methods.
Acetone in bacterial cultures was
routinely assayed by a headspace method (gas
chromatography-photoionization detection [GC-PID] method). Samples
(0.5 to 1 ml) of cell-free medium, obtained by centrifugation, were
placed in 4.8-ml vials sealed with Teflon-lined septa and allowed to
equilibrate for 1 h at 30°C. A sample of the headspace (250 µl) was removed with a gas-tight syringe and injected onto a gas
chromatograph (Photovac model 10S) equipped with a capillary column
(CPSil-5; 6 ft) and a photoionization detector. The carrier gas was
purified nitrogen (8 cm3 min
1), and the
column was typically operated at 23°C; under these conditions acetone
typically eluted at 115 ± 5 s. For each experiment the
headspace of fresh solutions of acetone ranging from 10 µM to 10 mM
were sampled identically to establish a calibration curve. For
verification of acetone formation, samples of culture supernatants were treated with 2,4-dinitrophenyl hydrazine (DNPH) and the
resulting hydrazone derivative of acetone was analyzed by high-pressure liquid chromatography (HPLC) as described previously
(40). For some cultures acetone formation was also verified
by GC-mass spectrometry (MS) analysis (see below).
Bacterial conversion of L-leucine,
deutero-L-leucine, and leucine metabolites to acetone.
For these experiments V. splendidus D2 or P5 cells were
grown at room temperature on MT leucine medium to logarithmic phase (OD600 of 0.5 to 0.7) and the cells were harvested by
centrifugation and washed twice with marine salts (MT medium with
tryptone deleted). Washed cells were suspended in approximately 1/10
the original volume of marine salts, adjusted to contain 2 mM
L-leucine or potential leucine metabolites including
3-methyl-1-aminobutane, 3-methylbutanal, sodium
3-hydroxy-3-methylbutanoate, or sodium
-ketoisocaproate (each at 2 mM), and then incubated with shaking at room temperature for 1 to
3 h. Aliquots were taken for measurement of cell density
(OD600) and acetone content; for the latter, cells were
removed by centrifugation, 0.5-ml samples of the supernatants were
equilibrated in sealed vials for 1 h at 30°C, and then headspace acetone was determined as described above. In some experiments cells
were incubated with potential inhibitors added in water, or in
dimethylformamide (20 µl per 2 ml of incubation mixture) in the case
of rotenone. For inhibition by a N2 atmosphere, cell suspensions were bubbled with N2 gas for 1 min before and
after L-leucine or
-ketoisocaproate was added and the
vial was quickly sealed with a Teflon-lined septum and then incubated
and processed as described above.
175°C). Collected volatiles were then
thermally desorbed at 75°C and injected onto a DB-1 column (0.32 mm
by 60 m; 1-mm film thickness; J & W Scientific, Folsom, Calif.)
programmed from 0 to 72°C, and eluting analytes were analyzed by a
Hewlett-Packard MSD 5970 mass spectrometer.
| |
RESULTS |
|---|
|
|
|---|
Leucine-dependent acetone formation is widespread in the Vibrionaceae. Previously we had isolated Vibrio spp. from estuarine samples and determined that acetone formation in these isolates was dependent on the presence of L-leucine and was repressed by glucose. These cultures did not survive storage, so new isolates were obtained from similar coastal estuary sites in southern California. Again, enrichment for Vibrio isolates by plating on TCBS agar (35) led to a high frequency of isolation of colonies that exhibit L-leucine-dependent acetone formation. Isolates D2 and P5 were further examined here. They were each identified as a Vibrio sp. by the methods we described previously (40) and were most similar to nonluminescent V. splendidus (phenon 3), as determined by the taxonomic methods of Ortigosa et al. (41).
During these experiments we wondered if acetone formation is widespread in the Vibrionaceae. We obtained a variety of characterized Vibrio species, some of which were reported to utilize L-leucine as the sole carbon source (41), and also obtained a few Listonella, Photobacterium, and Shewanella isolates; these genera are generally included in the Vibrionaceae (11, 32). These isolates and their ability to produce leucine-dependent acetone are summarized in Table 1. All of the Vibrio species tested produced detectable acetone in the presence of L-leucine, although the amount detected ranged widely from 145 to 4,320 µM/OD600 unit. As discussed below, this variation was found to be due to the effect of the growth stage on leucine-dependent acetone formation. In each case acetone formation was almost completely absent in cells grown on marine broth supplemented with glucose as the carbon source (Table 1), consistent with our earlier results (40). Two Listonella species and two Photobacterium angustum strains also produced leucine-dependent acetone. Acetone formation was much more variable in Shewanella isolates; only Shewanella woodyi formed significant amounts of acetone under these growth conditions. Acetone formation in several of the bacterial strains was verified by derivatization with DNPH followed by HPLC analysis, and for four strains GC-MS analysis also confirmed the production of acetone (Table 1). During these experiments we also analyzed cultures of P. putida PpG2 for production of acetone during growth on L-leucine; this strain was used to elucidate the leucine catabolic pathway shown in Fig. 1 (36). When grown on L-leucine as the sole carbon source or in a tryptone medium containing 20 mM L-leucine to mimic the medium used to culture marine vibrios, strain PpG2 produced little or no acetone (data not shown).Effects of growth conditions on acetone formation in V. splendidus and P. angustum. Previously we found that Vibrio isolates produced acetone primarily in the stationary phase of growth (40); however these experiments were complicated by the oxygen depletion that occurred during the incubation of culture samples in sealed vials. Here we grew V. splendidus P5 and P. angustum 25915 in a stirred fermentor under controlled aerobic conditions and at various times obtained samples, removed bacteria by centrifugation, and analyzed acetone in the resulting supernatants. Figure 2A illustrates that for V. splendidus P5 grown in marine broth, acetone was produced in stationary cells; some carryover of acetone from the inoculum was seen at early times. The decline in acetone after 8 h of culture can be attributed to volatilization of the ketone by the large volume of air passed through the culture. This experiment, repeated twice, also illustrated that acetone was not produced in response to a low pH, since the pH of the culture remained in the range of 7.7 to 7.9. To examine whether acetone formation might be due to excretion of acetoacetate into the medium with accompanying nonenzymatic decarboxylation, samples throughout the fermentation were analyzed for acetone in the presence and absence of acetoacetate decarboxylase (23). There was no significant difference in acetone levels in these samples (data not shown), indicating that acetone and not acetoacetate was released from the cells.
|
Specificity and stoichiometry of L-leucine conversion to acetone. Since leucine-degrading pseudomonads can metabolize either D- or L-leucine (36), we tested whether this was also true for Vibrio isolates. V. splendidus P5 was cultured in MT leucine medium, and log-phase cells were washed twice with marine salts and resuspended in marine salts with 2 mM leucine (D, L, or DL isomers). Acetone formation at 1 and 2.5 h was measured, and only the L isomer and the DL racemate were metabolized in this Vibrio strain. No acetone was detected in cells incubated with the D isomer.
To determine the fraction of L-leucine metabolized that was converted to acetone, washed cells were incubated with L-leucine and the disappearance of leucine was quantified with leucine dehydrogenase (7) and the appearance of acetone was quantified by the GC-PID method. The results are shown in Table 2. In the series of experiments shown, all or a large fraction of the added leucine was taken up by the bacteria by 3 h, and 45 to 84% (average of 55%) of the L-leucine metabolized was recovered as acetone. Since some acetone (about 10%) was lost by volatilization during the incubations and handling of the samples, acetone formation was underestimated. The corrected average conversion of L-leucine to acetone was 61%. It should be mentioned that sealed incubations were complicated by semianaerobic conditions that developed and inhibited acetone formation.
|
Bacterial conversion of putative leucine metabolites to acetone. It was expected that vibrios might degrade leucine by the well-known pseudomonad pathway, leading to the production of acetoacetic acid and acetyl-CoA (Fig. 1). However, to explain acetone formation in this case, a plausible pathway would involve acetoacetate decarboxylation to acetone rather than acetoacetic acid metabolism by the glyoxylate pathway (36). As shown above, we had ruled out the secretion of acetoacetic acid into the medium. Several attempts to demonstrate acetoacetic acid or acetoacetate decarboxylase in extracts of V. splendidus D2 or P5, by the methods of Kimura et al. (24), were unsuccessful.
Other bacterial pathways for L-leucine catabolism are described in the literature. For example, Proteus vulgaris is known to metabolize L-leucine by decarboxylation to 3-methyl-1-aminobutane or by transamination to
-ketoisocaproic acid,
which can then be decarboxylated to 3-methylbutanal (12,
43). To test the possibility that these L-leucine
metabolites might be converted to acetone by vibrios, we incubated
cells with each and determined if they would give rise to acetone. In
addition, as indicated from work on L-leucine catabolism in
Galactomyces reesii (29), 3-hydroxyisovaleric acid is a likely intermediate (Fig. 1), so it was
also tested. Of the metabolites tested, only
-ketoisocaproic acid, the product of transamination of leucine, was a precursor of
acetone in V. splendidus P5, Listonella
pelagia 33784, and P. angustum 25915. For
example, with V. splendidus P5 acetone formation in washed
cells in two duplicate experiments was 1,327 to 1,561 µM/h/OD600 unit with L-leucine and 1,314 to
1,462 µM/h/OD600 unit with sodium
-ketoisocaproate. Neither 3-methyl-1-aminobutane, 3-methylbutanal,
nor 3-hydroxyisovaleric acid stimulated acetone formation in any
of these three strains, and in addition, with V. splendidus P5, neither isovaleric acid nor 3-methylcrotonic acid,
precursors of intermediates in the 3-methylcrotonyl-CoA pathway (Fig.
1), was converted to acetone (data not shown).
Effects of inhibitors of leucine-dependent acetone formation.
To gain some insight into the metabolic pathway involved in
L-leucine conversion to acetone the effects of the
following metabolic inhibitors were tested: azide, rotenone and a
nitrogen atmosphere (to block electron transport), and arsenite (to
block branched-chain keto acid dehydrogenase) (9, 17). These
experiments were conducted with V. splendidus P5, P. angustum, and L. pelagia (Table 3). The most potent inhibition was seen
with removal of oxygen (i.e., a nitrogen atmosphere); for all three
bacterial species inhibition ranged from 92 to 97% in different
experiments. Since sodium azide and rotenone, electron transport
inhibitors, had little or no inhibitory effect, these findings suggest
that the oxygen dependence of acetone formation may be indicative of an oxidase or oxygenase reaction. Inhibition by arsenite ranged from 41 to
65%, which is consistent with inhibition of a lipoamide-dependent keto
acid dehydrogenase of the type used by P. putida PpG2
(46) in the conversion of
-ketoisocaproic acid to
isovaleryl-CoA (Fig. 1). Very similar results were seen with V. splendidus P5 incubated with
-ketoisocaproic acid in place of
L-leucine.
|
Bacterial conversion of deutero-L-leucine to
acetone.
In order to directly test whether acetone formation
occurs by the pseudomonad pathway or some other pathway,
(isopropyl-d7)-L-leucine with a label in the
isopropyl moiety was incubated with washed cells that had been pregrown
on MT leucine broth. Deuterated acetone that accumulated in the
headspace was analyzed by GC-MS; control incubation mixtures contained
nondeuterated L-leucine. These experiments were conducted
with L. pelagia, P. angustum, and V. splendidus strains, and the results are summarized in Table 4. The
positions of the deuterium labels and expected labeled products of the
pseudomonad and vibrio pathways are shown in Fig. 1. For all three
bacterial strains the acetone produced by incubation with
(isopropyl-d7)-L-leucine led to >90%
enrichment of the molecular ion (m/z 64) over the nondeuterated acetone
(m/z 58). This result is indicative of the retention of all six methyl
deuterium atoms in the acetone produced. This labeling pattern is
inconsistent with metabolism of
(isopropyl-d7)-L-leucine by the
pseudomonad pathway (ignoring deuterium isotope effects), which
would be expected to remove a methyl deuterium during the 3-methylcrotonyl-CoA carboxylase reaction, resulting in the
eventual formation of acetoacetate with five deuterium atoms (Fig. 1). Decarboxylation of acetoacetate (enzymatic or nonenzymatic) would produce acetone with five deuterium atoms (molecular ion m/z 63). In
the experiments shown in Table 4 no significant amount of molecular ion
at m/z 63 was seen. Analysis of the major acetone fragment ion due to
loss of methyl would be expected to give m/z 43 for the nondeuterated
fragment and m/z 46 for the trideuterated fragment; only the latter
pattern was seen for all three strains of Vibrionaceae
(Table 4).
|
| |
DISCUSSION |
|---|
|
|
|---|
We have been interested in identifying new biological sources of the volatile organic compound acetone, which, as described in the introduction, has a significant impact on the chemistry of the atmosphere. Here we have extended our earlier finding that marine vibrios produce acetone in the presence of L-leucine (40). Now we show that this metabolic trait is widespread in the Vibrio genus and other Vibrionaceae, such as Listonella and Photobacterium. However, Shewanella isolates, which some include in the Vibrionaceae (11), produced little or no acetone in the presence of L-leucine. Perhaps these results are indicative of differences in metabolism in aerobic versus anaerobic environments. The metabolism of L-leucine was shown here to be an aerobic process. Shewanella grows naturally in anaerobic environments (6, 28).
Given these results it is possible that leucine catabolism in marine environments gives rise to some of the acetone found in seawater. Small amounts of acetone at concentrations of 3 to 50 nM have been measured in open seawater (50); however these levels of the compound might be derived from partitioning with atmospheric acetone (4). Measurement of acetone in estuaries which contain abundant Vibrio populations (41) is complicated by the presence of anthropogenic sources of the ketone (50). At this point it is not possible to predict whether bacterial conversion of leucine in marine systems would be a significant contributor to atmospheric acetone.
When acetone formation in vibrios was discovered to be dependent on the presence of L-leucine, we assumed that the pathway was similar to those seen in animals, plants, and pseudomonads, involving 3-methylcrotonyl-CoA as an intermediate (Fig. 1) (1, 37). In animals L-leucine is a ketogenic amino acid that is metabolized to acetoacetate, which can break down nonenzymatically to produce acetone (47). However, we could not detect substantial pools of acetoacetate or acetoacetate decarboxylase in V. splendidus cultures. To further determine if the 3-methylcrotonyl-CoA-type pathway is operative in vibrios, we incubated cells with a deuterated L-leucine substrate, (isopropyl-d7)-L-leucine, containing fully deuterated methyl groups. If acetone is derived from the isopropyl end of the leucine molecule, one would expect to see acetone with five deuterium atoms since a proton is removed at the 3-methylcrotonyl-CoA carboxylase step (Fig. 1). This was not the case for L. pelagia 33784, P. angustum 25915, or V. splendidus P5, and instead the acetone produced from (isopropyl-d7)-L-leucine retained all six methyl group deuterium atoms (Table 4).
For this metabolic transformation to occur, an oxygen atom must be
introduced at C-4 of the leucine carbon skeleton to provide the
keto oxygen of the resulting acetone. There are two precedents for the transformation of leucine to metabolites with this type of
oxygen substitution; both involve
-ketoisocaproic acid as an
intermediate. First, transformation might occur as a result of an
-ketoisocaproate dioxygenase reaction, such as that described for
rat liver (42). A putative bacterial dioxygenase would
convert
-ketoisocaproic acid to 3-hydroxyisovaleric acid as
shown in Fig. 1 (pathway A), and subsequently its oxidative
cleavage, probably as the acyl-CoA derivative, could produce acetone
and acetyl-CoA. Acetone would be released as a by-product, and
the acetyl-CoA would be metabolized by the acetate assimilation pathway
known to occur in most free-living vibrios (19).
Consistent with pathway A is the finding that production of acetone
from L-leucine or
-ketoisocaproic acid was
dependent on oxygen but not blocked by electron transport inhibitors.
Although an
-ketoisocaproate dioxygenase has apparently not
been demonstrated in bacteria, it is noteworthy that a related
enzyme, 4-hydroxyphenylpyruvate dioxygenase, has been described
for the Vibrionaceae, V. cholerae, and
Shewanella colwelliana (26). Both enzymes
catalyze a similar reaction: the atoms of molecular oxygen are
introduced into both the
-keto carbon and the side chain accompanied
by decarboxylation of the keto acid (30, 42). The failure of
3-hydroxyisovaleric acid to support acetone formation in whole cells is
inconsistent with pathway A, although this result might be explained by
lack of uptake of the acid.
A second scheme for introduction of the requisite oxygen atom would involve production of isovaleryl-CoA, and 3-methylcrotonyl-CoA as in the pseudomonad leucine catabolic pathway (37), followed by a hydration reaction, such as that catalyzed by enoyl-CoA hydratase, resulting in the formation of 3-hydroxyisovaleryl-CoA (Fig. 1, pathway B). The latter metabolic sequence has recently been demonstrated in the yeast G. reesii, which converts isovaleric acid via isovaleryl-CoA and 3-methylcrotonyl-CoA to 3-hydroxyisovaleryl-CoA (29). As in pathway A, 3-hydroxyisovaleryl-CoA could be cleaved to produce acetone and acetyl-CoA. The operation of pathway B is supported by the finding that acetone production was inhibited by arsenite, a known inhibitor of lipoic acid-dependent enzymes such as branched-chain keto acid dehydrogenase; however, arsenite is not very specific, inhibiting a variety of enzymes (48). The role of oxygen in acetone formation in pathway B could be explained by a branched-chain acyl-CoA oxidase reaction. This type of enzyme has been described in relation to leucine catabolism in plant peroxisomes (15); in the Pseudomonas leucine degradation pathway isovaleryl-CoA is oxidized by a flavin-dependent acyl-CoA dehydrogenase (37) (Fig. 1).
Clarification of the leucine degradation pathway in vibrios will
require demonstration of key enzymes such as an
-ketoisocaproate dioxygenase, isovaleryl-CoA oxidase, and the putative
3-hydroxyisovaleryl-CoA lyase. The last enzyme would use a
-lyase
mechanism analogous to the well-known
3-hydroxy-3-methylglutaryl-CoA lyase, which catalyzes a
Claisen-type cleavage reaction (Fig. 1) (20). However, this type of lyase has apparently not been previously described. We
have noted that growth of V. splendidus P5 on leucine but
not glucose led to the induction of isocitrate lyase (data not shown). This finding is consistent with the idea that leucine catabolism gives
rise to an acetate equivalent that is processed by the glyoxylate pathway known to exist in Vibrio species (21).
Clarification of the vibrio leucine degradation pathway is in progress. It will be interesting to see if this new pathway is present in other biological systems, such as the buds, stems, and leaves of plants, that can produce significant amounts of acetone by an unknown mechanism (10, 22, 25, 31, 39).
| |
ACKNOWLEDGMENTS |
|---|
This work was supported by the National Science Foundation (grants ATM-9418073 and ATM-9805191).
We thank John Bowman, Frank Caccavo, Jr., John Makemson, Kenneth Nealson, María-Jesús Pujalte, and John Sokatch for providing bacterial strains, Robert Barkley and Detlev Helmig for assistance with GC-MS experiments, and Cindy Barnes and Megan Shirk for excellent technical assistance.
| |
FOOTNOTES |
|---|
* Corresponding author. Mailing address: Department of Chemistry and Biochemistry, University of Colorado, Boulder, CO 80309-0215. Phone: (303) 492-7914. Fax: (303) 492-1149. E-mail: fall{at}colorado.edu.
| |
REFERENCES |
|---|
|
|
|---|
| 1. |
Anderson, M. D.,
P. Che,
J. Song,
B. K. Nikolau, and E. S. Wurtele.
1998.
3-Methylcrotonyl-coenzyme A carboxylase is a component of the mitochondrial leucine catabolic pathway in plants.
Plant Physiol.
118:1127-1138 |
| 2. | Arnold, F., V. Bürger, B. Droste-Fanke, F. Grimm, A. Krieger, J. Schneider, and T. Stilp. 1977. Acetone in the upper troposphere and lower stratosphere: impact on trace gases and aerosols. Geophys. Res. Lett. 23:3017-3020. |
| 3. | Baumann, P., and L. Baumann. 1981. The marine Gram-negative eubacteria: genera Photobacterium, Beneckea, Alteromonas, Pseudomonas and Alcaligenes, p. 1302-1331. In M. P. Starr, H. Stolp, H. G. Trüper, A. Ballows, and H. G. Schlegel (ed.), The prokaryotes, vol. II. Springer-Verlag, Berlin, Germany |
| 4. | Benkelberg, H. J., S. Hamm, and P. Warneck. 1995. Henry's law coefficients for aqueous solutions of acetone, acetaldehyde and acetonitrile, and equilibrium constants for the addition compounds of acetone and acetaldehyde with bisulfite. J. Atmos. Chem. 20:17-34. |
| 5. | Boeker, E. A., and E. E. Snell. 1972. Amino acid decarboxylases, p. 217-253. In P. D. Boyer (ed.), The enzymes. Academic Press, New York, N.Y |
| 6. |
Bowman, J. P.,
S. A. McCammon,
D. S. Nichols,
J. H. Skerratt,
S. M. Rea,
P. D. Nichols, and T. A. McMeekin.
1997.
Shewanella gelidimarina sp. nov. and Shewanella frigidimarina sp. nov., novel Antarctic species with the ability to produce eicosapentaenoic acid (20:5 3) and grow anaerobically by dissimilatory Fe(III) reduction.
Int. J. Syst. Bacteriol.
47:1040-1047 |
| 7. | Burrin, J. M., J. L. Paterson, and G. M. Hall. 1985. Simple enzymatic method for plasma branched-chain amino acids. Clin. Chim. Acta 153:37-42[Medline]. |
| 8. | Caccavo, F. J., N. B. Ramsing, and J. W. Costerson. 1996. Morphological and metabolic responses to starvation by the dissimilatory metal-reducing bacterium Shewanella alga BrY. Appl. Environ. Microbiol. 62:4678-4682[Abstract]. |
| 9. | Dagley, S., and P. J. Chapman. 1971. Evaluation of methods used to determine metabolic pathways, p. 217-268. In J. R. Norris, and D. W. Ribbons (ed.), Methods in microbiology. Academic Press, London, United Kingdom |
| 10. | de Gouw, J. A., C. J. Howard, T. G. Custer, and R. Fall. 1999. Emissions of volatile organic compounds from cut grass and clover are enhanced during the drying process. Geophys. Res. Lett. 26:811-814. |
| 11. | De Ley, J. 1992. The proteobacteria: ribosomal RNA cistron similarities and bacterial taxonomy, p. 2113-2140. In A. Balows, H. G. Trüper, M. Dworkin, W. Harder, and K.-H. Schleifer (ed.), The prokaryotes. A handbook on the biology of bacteria: ecophysiology, isolation, identification, applications, 2nd ed. Springer-Verlag, New York, N.Y |
| 12. |
Ekladius, L.,
H. K. King, and C. R. Sutton.
1957.
Decarboxylation of neutral amino acids in Proteus vulgaris.
J. Gen. Microbiol.
17:602-619 |
| 13. |
Fall, R. R.,
J. L. Brown, and T. S. Schaeffer.
1979.
Enzyme recruitment allows the biodegradation of recalcitrant branched hydrocarbons by Pseudomonas citronellolis.
Appl. Environ. Microbiol.
38:715-722 |
| 14. | Ferronato, C., J. J. Orlando, and G. S. Tyndall. 1998. The rate and mechanism of the reaction of OH and Cl with 2-methyl-3-buten-2-ol. J. Geophys. Res. 103:25579-25586. |
| 15. | Gerbling, H. 1993. Peroxisomal degradation of 2-oxoisocaproate. Evidence for free acid intermediates. Bot. Acta 106:380-387. |
| 16. | Girbal, L., and P. Soucaille. 1998. Regulation of solvent production in Clostridium acetobutylicum. Trends Biotechnol. 16:11-16. |
| 17. | Heinen, W. 1971. Inhibitors of electron transport and oxidative phosphorylation, p. 383-393. In J. R. Norris, and D. W. Ribbons (ed.), Methods in microbiology. Academic Press, London, United Kingdom |
| 18. | Helmig, D., L. F. Klinger, A. Guenther, L. Vierling, C. Geron, and P. Zimmerman. 1999. Biogenic volatile organic compound emissions (BVOCs). 1. Identifications from three continental sites in the U.S. Chemosphere 38:2163-2187[Medline]. |
| 19. | Holt, J. G., N. R. Krieg, P. H. A. Sneath, J. T. Staley, and S. T. Williams (ed.). 1994. Determinative bacteriology, 9th ed. Williams & Wilkins, Baltimore, Md |
| 20. | Hruz, P. W., C. Narasimhan, and H. M. Miziorko. 1992. 3-Hydroxy-3-methylglutaryl coenzyme A lyase: affinity labeling of the Pseudomonas mevalonii enzyme and assignment of cysteine-237 to the active site. Biochemistry 31:6842-6847[Medline]. |
| 21. |
Ishii, A.,
T. Ochiai,
S. Imagawa,
N. Fukunaga,
S. Sasaki,
O. Minowa,
Y. Mizuno, and H. Shiokawa.
1987.
Isozymes of isocitrate dehydrogenase from an obligately psychrophilic bacterium, Vibrio sp. strain ABE-1: purification and modulation of activities by growth conditions.
J. Biochem.
102:1489-1498 |
| 22. | Khalil, M. A. K., and R. A. Rasmussen. 1992. Forest hydrocarbon emissions: relationships between fluxes and ambient concentrations. J. Air Waste Manag. Assoc. 42:810-813. |
| 23. | Kimura, M., M. Shimosawa, K. Kobayashi, T. Sakoguchi, A. Hase, S. Takashima, A. Matsuoka, N. Yasuda, and Y. Kimura. 1984. Determination of acetoacetate in plasma by a combination of enzymatic decarboxylation and head-space gas chromatography. Chem. Pharm. Bull. 32:3588-3593. |
| 24. | Kimura, Y., N. Yasuda, H. Tanigaki-Nagae, T. Nakabayashi, H. Matsunaga, M. Kimura, and A. Matsuoka. 1986. Acetoacetate decarboxylase and a peptide with similar activity produced by Bacillus polymyxa A-57. Agric. Biol. Chem. 50:2509-2516. |
| 25. | Kirstine, W., I. Galbally, Y. Ye, and M. Hooper. 1998. Emissions of volatile organic compounds (primarily oxygenated species) from pasture. J. Geophys. Res. 103:10605-10619. |
| 26. | Kotob, S. I., S. L. Coon, E. J. Quintero, and R. M. Weiner. 1995. Homogentisic acid is the primary precursor of melanin synthesis in Vibrio cholerae, a Hyphomonas strain, and Shewanella colwelliana. Appl. Environ. Microbiol. 61:1620-1622[Abstract]. |
| 27. | Kotzias, D., C. Konidari, and C. Spartà. 1997. Volatile carbonyl compounds of biogenic origin. Emission and concentration in the atmosphere, p. 67-78. In G. Helas, S. Slanina, and R. Steinbrecher (ed.), Biogenic volatile organic compounds in the atmosphere. SPB Academic Publishing, Amsterdam, The Netherlands |
| 28. | Krause, B., and K. H. Nealson. 1997. Physiology and enzymology involved in denitrification by Shewanella putrefaciens. Appl. Environ. Microbiol. 63:2613-2618[Abstract]. |
| 29. |
Lee, I.-Y., and J. P. N. Rosazza.
1998.
Enzyme analyses demonstrate that -methylbutyric acid is converted to -hydroxy- -methylbutyric acid via the leucine catabolic pathway by Galactomyces reesii.
Arch. Microbiol.
169:257-262[Medline].
|
| 30. | Lindblad, B., G. Lindstedt, and S. Lindstedt. 1970. The mechanism of enzymic formation of homogentisate from p-hydroxyphenylpyruvate. J. Am. Chem. Soc. 92:7446-7449[Medline]. |
| 31. | MacDonald, R. C., and R. Fall. 1993. Acetone emission from conifer buds. Phytochemistry 34:991-994. |
| 32. | MacDonell, M. T. 1985. Phylogeny of the Vibrionaceae and recommendation for two new genera, Listonella and Shewanella. Syst. Appl. Microbiol. 6:171-182. |
| 33. |
MacLeod, P., and M. E. Morgan.
1956.
Leucine metabolism of Streptococcus lactis var. maltigenes. II. Transaminase and decarboxylase activity of acetone powders.
J. Dairy Sci.
39:1125-1133 |
| 34. |
Makemson, J. C.,
N. R. Fulayfil,
W. Landry,
L. M. V. Ert,
C. F. Wimpee,
E. A. Widder, and J. F. Case.
1997.
Shewanella woodyi sp. nov., an exclusively respiratory luminous bacterium isolated from the Alboran sea.
Int. J. Syst. Bacteriol.
47:1034-1039 |
| 35. |
Massad, G., and J. D. Oliver.
1987.
New selective and differential medium for Vibrio cholerae and Vibrio vulnificus.
Appl. Environ. Microbiol.
53:2262-2264 |
| 36. |
Massey, L. K.,
R. S. Conrad, and J. R. Sokatch.
1974.
Regulation of leucine catabolism in Pseudomonas putida.
J. Bacteriol.
118:112-120 |
| 37. |
Massey, L. K.,
J. R. Sokatch, and R. S. Conrad.
1976.
Branched-chain amino acid catabolism in bacteria.
Bacteriol. Rev.
40:42-54 |
| 38. | McKeen, S. A., T. Gierczak, J. B. Burkholder, P. O. Wennberg, T. F. Hanisco, E. R. Keim, R.-S. Gao, S. C. Liu, A. R. Ravishankara, and D. W. Fahey. 1997. The photochemistry of acetone in the upper troposphere: a source of odd-hydrogen radicals. Geophys. Res. Lett. 24:3177-3180. |
| 39. | Murphy, J. B. 1985. Acetone production during the germination of fatty seeds. Physiol. Plant. 63:231-234. |
| 40. | Nemecek-Marshall, M., C. Wojciechowski, J. Kuzma, G. M. Silver, and R. Fall. 1995. Marine Vibrio species produce the volatile organic compound acetone. Appl. Environ. Microbiol. 61:44-47[Abstract]. |
| 41. | Ortigosa, M., E. Garay, and M.-J. Pujalte. 1994. Numerical taxonomy of Vibrionaceae isolated from oysters and seawater along an annual cycle. Syst. Appl. Microbiol. 17:216-225. |
| 42. |
Sabourin, P. J., and L. L. Bieber.
1982.
The mechanisms of -ketoisocaproate oxygenase. Formation of -hydroxyisovalerate from -ketoisocaproate.
J. Biol. Chem.
257:7468-7471 |
| 43. |
Sasaki, S.
1962.
On the decarboxylase operating in the degradative pathway of L-leucine by Proteus vulgaris.
J. Biochem.
51:335-344 |
| 44. | Singh, H. B., M. Kanakidou, P. J. Crutzen, and D. J. Jacob. 1995. High concentrations and photochemical fate of oxygenated hydrocarbons in the global troposphere. Nature 378:50-54. |
| 45. | Singh, H. B., D. O'Hara, D. Herlth, W. Sachse, D. R. Blake, J. D. Bradshaw, M. Kanakidou, and P. J. Crutzen. 1994. Acetone in the atmosphere: distribution, sources, and sinks. J. Geophys. Res. 99:1805-1819. |
| 46. |
Sokatch, J. R.,
V. McCully, and C. M. Roberts.
1981.
Purification of a branched-chain keto acid dehydrogenase from Pseudomonas putida.
J. Bacteriol.
148:647-652 |
| 47. | Stryer, L. 1995. Biochemistry, 4th ed. W. H. Freeman, New York, N.Y |
| 48. | Webb, J. L. 1966. Enzyme and metabolic inhibitors. Iodoacetate, Maleate, N-Ethylmaleimide, Alloxan, Quinones, Arsenicals, vol. III. Academic Press, New York, N.Y |
| 49. | Winnacker, E. L., and H. A. Barker. 1971. Aerobic metabolism of b-amino-n-butyric acid by Pseudomonas putida. Biochim. Biophys. Acta 237:284-292[Medline]. |
| 50. | Zhou, X., and K. Mopper. 1990. Apparent partition coefficients of 15 carbonyl compounds between air and seawater and between air and freshwater; implications for air-sea exchange. Environ. Sci. Technol. 24:1864-1869. |
This article has been cited by other articles:
| |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Copyright © 2009 by the American Society for Microbiology. For an alternate route to Journals.ASM.org, visit: http://intl-journals.asm.org | More Info»