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Applied and Environmental Microbiology, December 2005, p. 8949-8953, Vol. 71, No. 12
0099-2240/05/$08.00+0 doi:10.1128/AEM.71.12.8949-8953.2005
Copyright © 2005, American Society for Microbiology. All Rights Reserved.
Analysis of fae and fhcD Genes in Mono Lake, California
Olivier Nercessian,1,
Marina G. Kalyuzhnaya,1
Samantha B. Joye,2
Mary E. Lidstrom,1,3 and
Ludmila Chistoserdova1*
Department of Chemical Engineering,1
Department of Microbiology, University of Washington, Seattle, Washington 98195,3
Department of Marine Sciences, University of Georgia, Athens, Georgia 306022
Received 3 June 2005/
Accepted 11 August 2005

ABSTRACT
Genes for two enzymes of the tetrahydromethanopterin-linked
C
1 transfer pathway (
fae and
fhcD) were detected in hypersaline,
hyperalkaline Mono Lake (California), via PCR amplification
and analysis. Low diversity for
fae and
fhcD was noted, in contrast
to the diversity previously detected in a freshwater lake, Lake
Washington (Washington).

INTRODUCTION
Methylotrophic bacteria are a group of organisms that consume
a wide range of C
1 compounds, such as methane, methanol, methylated
amines, methylated glycines, halomethanes, and methylated sulfur
species (
1,
17). They are found in a variety of environments,
such as freshwater, marine, and terrestrial habitats, as well
as habitats characterized by extreme conditions, such as highly
saline, alkaline, or acidic habitats (
2,
4-
6,
8,
11,
18,
21,
24,
25,
28). Along with the classic cultivation approaches,
molecular tools have been in use for culture-independent detection
and characterization of natural methylotroph populations. The
traditional molecular tools include oligonucleotide probes and
PCR primer sets targeting genes conserved among specific groups
of methylotrophic bacteria, such as 16S rRNA genes (
3,
8,
23,
24,
26,
27), or functional genes encoding specific methylotrophic
functions, such as particulate and soluble methane monooxygenases
(
5,
8,
18,
20), methanol dehydrogenase (
8,
19,
24), corrinoid-linked
methyltransferase (
21), or methanesulfonic acid monooxygenase
(
15). The phylogenetic probes have been used successfully to
uncover the diversity of

- and

-proteobacterial methylotrophs
(
3,
8,
23,
24,
25,
27), and the functional probes have been
used for detecting a range of methylotrophs possessing respective
primary oxidation genes (
5,
8,
15,
18-
21,
24). Recently, Kalyuzhnaya
and colleagues have developed a suite of novel primer sets designed
for a broader detection of C
1-oxidizing capacity in the environment
(
12,
13). These primer sets target four genes in the tetrahydromethanopterin
(H
4MPT)-linked pathway, the pathway widespread in methylotrophic
bacteria (
30) but also found in nonmethylotrophs:
fae,
mtdB,
mch, and
fhcD. These new tools, tested on microbial populations
in a freshwater lake (Lake Washington, Washington), uncovered
a broad diversity of
fae,
mtdB,
mch, and
fhcD phylotypes belonging
to

-, ß-, and

-proteobacteria, including methanotrophs,
nonmethanotrophic methylotrophs, and bacteria not known for
methylotrophic ability, such as
Burkholderia spp. (
12,
13).
In addition, sequences belonging to highly divergent bacterial
groups, such as
Planctomycetes, and yet unaffiliated divergent
species have been uncovered (
12,
13). The broadest range of
divergent sequences was detected using two of the primer sets,
those targeting
fae and
fhcD. Most of the phylotypes detected
in Lake Washington were not closely related to known organisms,
suggesting that the majority of the population potentially involved
in C
1 metabolism in this environment remain unidentified (
12,
13). Mono Lake (California) is an extreme environment characterized
by high rates of methane production and methane oxidation (
10).
Initial insights into the methane-oxidizing bacterial population
in the site were recently obtained via fluorescence in situ
hybridization and denaturing gradient gel electrophoresis employing
oligonucleotide primers specific for known methanotroph groups
(
4). The goal of this work was the assessment of the diversity
of C
1-utilizing bacteria in Mono Lake by use of tools with a
broader detection range, i.e., PCR primers targeting
fae and
fhcD.
Water samples from Mono Lake were collected from 20 discrete depths, between 5 and 38 m, near a permanently moored buoy in the central basin of Mono Lake (station 6; 37°57.822' N, 119°01.305' W) by using 5-liter Niskin bottles deployed from a small boat in August 2002. Dissolved methane concentrations were determined using headspace extraction followed by gas chromatography (10). Dissolved oxygen concentrations were determined using an O2 sensor (Yellow Spring Instruments) (4). Rates of methane oxidation were determined using a [3H]CH4 tracer technique (4). Oxygen concentrations in the upper water column were high (>100 µM), while methane concentrations were low (Table 1). Rates of methane oxidation increased at the base of the oxycline as methane concentrations increased and oxygen concentrations decreased (Table 1).
Water samples for DNA extraction were stored in clean sample-rinsed
plastic cubitainers at 4°C until filtration through a Sterivex
filter cartridge (0.22 µm; Millipore). Excess water was
expelled, and the cartridge was filled with 1.8 ml of lysis
buffer (
22). Total community DNA was extracted from 20 discrete
samples from different depths by using a previously described
method (
9), and these were used as templates to PCR amplify
fae and
fhcD, as described previously (
12,
13). Nine samples
(between the depths of 5 and 15 m) were positive for
fae, and
13 samples (between the depths of 5 and 20 m) were positive
for
fhcD (Table
1). PCR products were then pooled, cloned into
the pCR2.1 vector (Invitrogen), and analyzed, as described below.
A total of 189 plasmids containing fae inserts were analyzed based on their restriction fragment length polymorphism (RFLP) patterns, as described before (12). A total of five RFLP patterns were identified. Two to five representatives of each pattern were sequenced, and the sequences were categorized into phylotypes, based on a 94% DNA similarity cutoff value, a value recently suggested for discriminating between microbial species (16, 29), based on extensive comparisons between closely related bacterial strains (16). A total of four unique phylotypes were identified, and these were distributed as follows: phylotype FaeML1, 155 clones (82.5%); phylotype FaeML2, 23 clones (12%); phylotype FaeML3, 10 clones (5%); and phylotype FaeML4, 1 clone (0.5%). The homologous coverage value (7) for this library was calculated at 0.99, suggesting that the sampling effort was adequate and covered the major phylotypes present in the library. Comparisons with the sequences deposited with GenBank as well as with our proprietary databases showed that only one phylotype, FaeML3, showed over 94% identity at the DNA level with known fae sequences, those belonging to Methylomicrobium species that are
-proteobacterial methanotrophs. A representative of each unique phylotype was included in the phylogenetic analyses, along with the sequences from a variety of cultured bacteria, as well as the sequences previously recovered from Lake Washington by use of the same primer set, as previously described (12). Phylogenetic analyses (Fig. 1) revealed that, while phylotype FaeML3, as expected, tightly clustered with Methylomicrobium sequences, the three remaining phylotypes loosely clustered with known sequences belonging to
-proteobacteria.
A total of 186 plasmids containing
fhcD inserts were analyzed
in a similar fashion, as previously described (
13). A total
of five RFLP patterns and a total of five phylotypes were identified,
based on a 94% cutoff at the DNA level, and these were distributed
as follows: phylotype FhcDML1, 139 clones (75%); phylotype FhcDML2,
15 clones (8%); phylotype FhcDML3, 14 clones (8%); phylotype
FhcDML4, 10 clones (5%); and phylotype FhcDML5, 8 clones (4%).
The homologous coverage value (
7) for this library was calculated
at 1. Comparisons with the sequences deposited with GenBank
as well as with our proprietary databases revealed that only
one phylotype, FhcDML5, showed significant identity at the DNA
level (90%) with known
fhcD sequences that belonged to
Methylomicrobium.
The remaining four phylotypes were only distantly related to
known
fhcD sequences (67 to 87% identity at the amino acid level).
Phylogenetic analyses (Fig.
2) revealed that, as expected, phylotype
FhcDML5 tightly clustered with
Methylomicrobium sequences, while
phylotypes FhcDML1 and FhcDML3 loosely clustered with known

-proteobacterial sequences, phylotype FhcDML4 clustered with
the sequences of uncultured ß-proteobacteria, and
phylotype FhcDML2 clustered with sequences of unaffiliated uncultured
bacteria previously identified in Lake Washington (
13).
Overall, our data suggest that only a few species possessing
the genes for the H
4MPT-linked C
1 transfer pathway are present
in Mono Lake and that of these, only one group, the
Methylomicrobium group, is identifiable. Sequences highly similar to the 16S
rRNA sequences from
Methylomicrobium strains isolated from soda
lakes (
11,
18,
28) have recently been detected in Mono Lake
(
4), pointing toward the ubiquitous nature of these species
in environments characterized by high salinity and high alkalinity.
The remaining sequences detected in this work, including the
most abundant
fae and
fhcD phylotypes, only loosely clustered
with sequences of known

-proteobacterial methanotrophs. Based
on the abundance of these phylotypes in PCR-amplified libraries,
they likely represent species with an ecologically important
function, which may be in methane oxidation or in oxidation
of other C
1 compounds. Carini et al. have recently reported
on the presence of

-proteobacterial 16S rRNA gene sequences,
including those closely related to
Methylosinus sequences (
4).
However, no

-proteobacterial
fae or
fhcD sequences were recovered
in this work. This is unlikely to be due to primer bias, as
the same primers have readily detected

-proteobacterial
fae or
fhcD sequences from Lake Washington (
12,
13), or to insufficient
sampling in the clone libraries (see above) but is likely due
to the low abundance of these sequences in the samples. The
low diversity of detected
fae and
fhcD sequences in Mono Lake
is in contrast with the diversity previously uncovered in a
freshwater lake, Lake Washington, where a variety of sequences
belonging to

-, ß-, and

-proteobacteria have been
identified using the same molecular tools (
12,
13). In addition,
sequences clustering with planctomycete-related sequences have
been identified, as have sequences deeply diverging from the
sequences affiliated with known organisms, suggesting the presence
of novel phyla with no cultured representatives (
12,
13).
The presence of a phylotype in the fhcD Mono Lake library (FhcDML2) that is related to this latter group of sequences is intriguing, but nothing is known about the phylogenetic position of the organisms possessing these sequences, their physiological properties, or their role in the environment. Work is under way to address these questions, including metagenomic analysis of the Lake Washington microbial community and specific cell separation using flow cytometry.
In conclusion, we provided evidence that the pathway involved in C1 transfers mediated by H4MPT is present in microbial populations inhabiting an extreme environment, a soda lake, but that the diversity of the detected genes is very limited compared to the diversity previously found in a freshwater lake. The observed lower diversity may result from special adaptations required for C1 microbes to survive in the unique geochemical environment present in Mono Lake. The dominant groups of fae and fhcD sequences recovered in PCR-based libraries belong to unknown bacterial species likely to be involved in oxidation of C1 compounds, while about 5% of the sequences belong to the well characterized genus Methylomicrobium.

ACKNOWLEDGMENTS
This work, part of the Microbial Observatories program, was
funded by the National Science Foundation (MCB-0131957 and MCB
99-77886) and in part by CRDF grant RBI-2509-MO-03.
We gratefully acknowledge P. Dunfield for providing DNA of Methylohalobius crimeensis, D. Stahl for sharing a Unix server, and J. T. Hollibaugh for providing DNA extracts.

FOOTNOTES
* Corresponding author. Mailing address: Department of Chemical Engineering, University of Washington, Seattle, WA 98195. Phone: (206) 543-6683. Fax: (206) 616-5721. E-mail:
milachis{at}u.washington.edu.

Present address: CEA/Cadarache, DSV/DEVM/LEMiR, Bât 161, 13108 St. Paul lez Durance, France. 

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Applied and Environmental Microbiology, December 2005, p. 8949-8953, Vol. 71, No. 12
0099-2240/05/$08.00+0 doi:10.1128/AEM.71.12.8949-8953.2005
Copyright © 2005, American Society for Microbiology. All Rights Reserved.
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