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Applied and Environmental Microbiology, March 2004, p. 1698-1707, Vol. 70, No. 3
0099-2240/04/$08.00+0 DOI: 10.1128/AEM.70.3.1698-1707.2004
Copyright © 2004, American Society for Microbiology. All Rights Reserved.
Molecular Evidence for the Evolution of Metal Homeostasis Genes by Lateral Gene Transfer in Bacteria from the Deep Terrestrial Subsurface
J. M. Coombs and T. Barkay*
Department of Biochemistry and Microbiology, Cook College, Rutgers University, New Brunswick, New Jersey 08901
Received 18 August 2003/
Accepted 27 November 2003

ABSTRACT
Lateral gene transfer (LGT) plays a vital role in increasing
the genetic diversity of microorganisms and promoting the spread
of fitness-enhancing phenotypes throughout microbial communities.
To date, LGT has been investigated in surface soils, natural
waters, and biofilm communities but not in the deep terrestrial
subsurface. Here we used a combination of molecular analyses
to investigate the role of LGT in the evolution of metal homeostasis
in lead-resistant subsurface bacteria. A nested PCR approach
was employed to obtain DNA sequences encoding P
IB-type ATPases,
which are proteins that transport toxic or essential soft metals
such as Zn(II), Cd(II), and Pb(II) through the cell wall. Phylogenetic
incongruencies between a 16S rRNA gene tree and a tree based
on 48 P
IB-type ATPase amplicons and sequences available for
complete bacterial genomes revealed an ancient transfer from
a member of the ß subclass of the
Proteobacteria (ß-proteobacterium)
that may have predated the diversification of the genus
Pseudomonas.
Four additional phylogenetic incongruencies indicate that LGT
has occurred among groups of ß- and

-proteobacteria.
Two of these transfers appeared to be recent, as indicated by
an unusual G+C content of the P
IB-type ATPase amplicons. This
finding provides evidence that LGT plays a distinct role in
the evolution of metal homeostasis in deep subsurface bacteria,
and it shows that molecular evolutionary approaches may be used
for investigation of this process in microbial communities in
specific environments.

INTRODUCTION
The role of lateral gene transfer (LGT) in the evolution of
microorganisms becomes more and more apparent with every new
microbial genome that is sequenced and annotated (
54,
58), which
has led many workers to question our basic concepts of microbial
speciation (
18,
23). The prevalence of laterally transferred
genes clearly suggests that this mode of evolution is advantageous
to microbial life, possibly by providing the means for genetic
innovation in the absence of frequent sexual recombination (
37).
This variation is likely to increase metabolic diversity, and
consequently competence, in environments subject to frequent
change (
13,
61). The possibility that LGT is an important force
in shaping the structure and function of microbial communities
in their natural habitats is suggested by (i) the fact that
abundant and diverse plasmids (
12,
73), viruses (
8,
89), insertion
sequences (
70), transposons (
59,
78), integrons (
49), and other
elements that contribute to genomic plasticity are commonly
isolated from environmental samples and strains; (ii) the fact
that natural competence is common among microbes (
11) and occurs
in soils (
17,
50) and natural water (
88); (iii) the fact that
LGT has been demonstrated in model ecosystems (i.e., microcosms)
(
52,
62,
75,
80) and in intact environmental samples (
19); and
(iv) the fact that seeding soils with bacteria carrying conjugal
catabolic plasmids results in transfer of the plasmids to indigenous
soil microbes and the stimulation of plasmid-specified activities
as detected by enhanced degradation of specific substrates (
14,
48).
In contrast to the large body of research that has explored gene transfer in microbial communities of topsoils and natural waters, little is known about this phenomenon in the deep subsurface. Nevertheless, the deep subsurface is the habitat for a large proportion of the world biomass (86), and major lineages of Bacteria and Archaea have been detected in aquifer sediments and vadose zone samples. Microbial communities of the deep subsurface are constrained by the scarcity of growth substrates (60), water availability, and spatial separation (77), which result in low metabolic rates (28) and the dominance of chemolithoautotrophic metabolism (10, 77). Because population densities (52) and metabolic activities (72) stimulate LGT, this process may be limited in the deep subsurface. Nevertheless, anecdotal evidence indicates that LGT affects the genetic and metabolic diversities of subsurface microbial communities. Plasmids of various sizes were observed in aerobic heterotrophs that were isolated from deep Savannah River sediments (22); the molecular structure of some of these plasmids suggested a common evolutionary origin (29), and conjugal transfer of catabolic plasmids was monitored in subsurface microcosms (71). Here we employed approaches and tools derived from molecular evolution studies (9, 54, 61) to examine evolution by LGT in subsurface microbial communities; in this study we focused on metal cation homeostasis genes encoding the PIB-type ATPases, which are known for their broad distribution in the bacterial world (2).
PIB-type ATPases are involved in fundamental cellular processes, such as the transport of essential micronutrients, delivery of ion cofactors to specific proteins, and extrusion of toxic ions from the cytoplasm (3). These transporters prevent the overaccumulation of essential but highly reactive ions, such as Cu(I), Zn(II), or Co(II) (5, 63, 66), and further protect the cell by removing toxic ions, such as Ag(I), Cd(II), and Pb(II), from the cytoplasm (53, 65, 74). PIB-type ATPases specific for monovalent Cu(I) and Ag(I) are found in all three domains of life, while divalent ion-specific Zn(II)-Co(II)-Cd(II)-Pb(II)-transporting PIB-type ATPases are common in prokaryotes but have not been observed in animals and fungi (3).
Several PIB-type ATPases are associated with mobile genetic elements. A plasmid location has been reported for Lactococcus lactis (56), Staphylococcus aureus (53), Ralstonia metallidurans (7), and Arthrobacter spp. (K. Jerke and C. Nakatsu, personal communication). Transposons carrying PIB-type ATPases were described for Listeria monocytogenes (34) and S. aureus (Chikramane and Dubin, 1993, unpublished data), and in Pseudomonas aeruginosa the locus is a part of a gene island (31). LGT of a PIB-type ATPase has previously been documented in Stenotrophomonas maltophila (1) and Streptococcus thermophilus (67). To date, the locus has not been considered with respect to LGT and the genetic diversity of natural communities and their responses to metal stress.
The objective of this study was to use phylogenetic analyses to examine the role of LGT in the evolution of metal homeostasis in subsurface bacteria. We obtained PCR amplicons of zntA/cadA/copA-like genes from a group of previously described lead-resistant (Pbr) bacteria from the deep terrestrial subsurface (6). Phylogenetic analyses of the DNA and deduced amino acid sequences of these amplicons revealed that 4 of 48 subsurface zntA/cadA/copA-like loci may have evolved by LGT. Transfer among Comamonas spp. and between members of the ß subclass of the class Proteobacteria (ß-proteobacteria) and
-proteobacteria were noted, indicating that LGT, while not widespread, has played a distinct role in the evolution of metal resistance in deep subsurface bacteria.

MATERIALS AND METHODS
Bacterial strains.
The sources and the cultivation and storage conditions for 105
Pb
r subsurface strains obtained from the Subsurface Microbial
Culture Collection (Tallahassee, Fla.) were described previously
(
6). Pairs of Pb
r bacteria and lead-sensitive (Pb
s) mutants
of these bacteria used here to optimize amplification of
zntA/cadA/pbrA-like
genes are listed in Table
1. These strains, as well as a deletion
mutant of
Escherichia coli W3110 and host strains carrying
zntA/cadA/pbrA-like
genes on plasmids (Table
1), were grown as described previously
(
6).
DNA preparation.
Bacterial strains were removed from glycerol stocks and cultured
on Luria-Bertani agar, pH 6.8 (containing [per liter] 10 g of
tryptone, 5 g of peptone, 5 g of NaCl, and 15 g of agar). Isolated
colonies were transferred to 5 ml of Luria-Bertani broth and
incubated at 37°C overnight. One-milliliter samples of each
overnight culture were centrifuged and resuspended in 1 ml of
phosphate-buffered saline (containing [per liter] 8 g of NaCl,
0.2 g of KCl, 1.15 g of Na
2HPO
4 · 7H
2O, and 0.2 g of
KH
2PO
4). The cells were washed three times in phosphate-buffered
saline and then resuspended in 100 µl of cold 1:10 Tris-EDTA
(10 mM Tris-Cl [pH 7.4], 1 mM EDTA [pH 8.0]). The cells were
subjected to three freeze-thaw cycles at -75 and 65°C and
then dialyzed for 2 to 3 h by depositing them onto 0.025-µm-pore-size
nitrocellulose filters (Millipore, Bedford, Mass.) floating
on Tris-EDTA. The lysates were stored at -20°C or used immediately.
When other cell components interfered with PCR, 1 to 5 ml of
a culture was centrifuged and used for extraction of chromosomal
DNA (Puregene kit; Gentra, Minneapolis, Minn.). Purified DNA
samples were quantitated with a spectrophotometer (260 and 280
nm; Ultrospec 3000; Amersham Biosciences, Piscataway, N.J.)
and stored at -20°C until they were used.
PCR of 16S rDNA genes.
Amplification of the 16S ribosomal DNA (rDNA) gene from genomic DNA was carried out by using 50 pmol of primer fD1 (30), 50 pmol of primer rP2 (85), 5 µl of crude cell lysate or 50 to 250 ng of purified DNA, each deoxynucleoside triphosphate at a concentration of 0.2 mM, 5 µl of 5x PCR buffer (Promega Corporation, Madison, Wis.), 0.02 U of Taq polymerase (Promega), and 1.5 mM (final concentration) MgCl2. The PCR conditions included a 10-min hot start step at 94°C, followed by 30 cycles of 94°C for 1.5 min, 55°C for 1.5 min, and 72°C for 2 min (GeneAmp PCR System 9700; Applied Biosystems, Foster City, Calif.). After cycling, PCR mixtures were incubated for 7 min at 72°C and then kept at 4°C. PCR products were electrophoresed on a 0.75% agarose Tris-acetate-EDTA (0.04 M Tris-acetate and 0.001 M EDTA) gel at 70 V, stained in a solution containing 0.4 µg of ethidium bromide per ml, and destained in double-distilled H2O. DNA bands that were approximately 1.5 kb long (as determined with
HindIII markers [Invitrogen, Carlsbad, Calif.]) were excised from the gel and purified by using a Nucleotrap gel purification kit (Clontech, Palo Alto, Calif.) before storage at -20°C.
PCR primer design and specificity range.
Novel primers for a two-step nested PCR approach were developed to obtain zntA/cadA/pbrA-like amplicons. Multiple primer sets were designed by using eight bacterial sequences whose gene products have a documented role in metal homeostasis of Zn(II), Cd(II), and/or Pb(II) (E. coli zntA [5], S. aureus cadA [53], L. monocytogenes cadA [35], Pseudomonas putida cadA [36], L. lactis cadA [41], Synechocystis sp. strain PCC6803 ziaA [79], R. metallidurans pbrA [7], and Helicobacter pylori cadA [26]) and sequences homologous to these loci in whole bacterial genomes (Chlamydophila pneumoniae [accession no. AE001363], Halobacterium sp. strain NRC-1 [AE004437], Mycobacterium tuberculosis [AL123456], Synechocystis sp. strain PCC6803 [BA000022], R. metallidurans contig 649 [AAAI01000310], R. metallidurans contig 691 [AAAI01000352], Ralstonia solanacearum megaplasmid [NC_003296], P. aeruginosa PA1549, PA2435, PA3690, and PA3920 [NC_002516], Pseudomonas syringae PSPTO0570, PSPTO5532, PSPTO5279, and PSPTO1996 [NC_004578], Pseudomonas fluorescens Pflu0176 [NZ_AAAT02000118], P. fluorescens Pflu4370 [NZ_AAAT02000008], P. fluorescens Pflu2473 [NZ_AAAT02000032], and P. fluorescens PFO-1 [NZ_AAAT00000000]). Deduced amino acid sequences were aligned with MegAlign (DNAStar, Inc.), and the alignments were used to detect conserved regions in the encoding DNA. Sequences encoding the phosphatase and the ATP-binding domains were used as forward and reverse PCR primer binding sites, respectively, for the first PCR step. The transmembrane metal-binding domain (forward) and the ATP-binding domain (reverse) were selected as sites for the development of primers for the second nested PCR step (Fig. 1A). For primer design we utilized the most frequently occurring base at each position and included degeneracies for those that contained two or more base pairs in nearly equal proportions. Primer sequences were tested against the nontarget P-type ATPases encoded by kdpB (PIA type), mgtA (PIIIB type), and copA (PIB type) and were rejected if the level of match was the same as or greater than the worst level of zntA/cadA/pbrA match. KdpB, MgtA, and CopA are the bacterial P-type ATPases that have the highest degrees of homology to ZntA/CadA/PbrA (57). Base pair substitutions in the final primer sequence were made only in cases in which severe secondary structure formation was predicted (VectorNTI Suite; Informax, Frederick, Md.).
One reverse primer, 84JC, was used in combinations with five
first-reaction forward primers and four second-reaction forward
primers to obtain
zntA/cadA/pbrA PCR amplicons (Table
2). Combinations
with primers 79JC and 81JC were used to obtain PCR products
from
E. coli W3110 and
S. aureus K10 (Fig.
1B) and one product
each from subsurface strains of
Bacillus,
Acinetobacter, and
Pseudomonas spp. Forward primers 87JC and 88JC amplified
zntA/cadA/pbrA-like
genes of 25 of 31 Pb
r subsurface
Comamonas spp. and the control
ß-proteobacterium
R. metallidurans CH34. Forward primers
101JC, 102JC, and 103JC, designed by aligning ZntA/CadA/PbrA-like
amino acid sequences from complete pseudomonad genomes, were
used with 17 of 27 Pb
r subsurface
Pseudomonas spp. Finally,
amplicons from 2 of 15 subsurface
Arthrobacter spp. were obtained
by using primers 132JC and 133JC, which were designed to target
a known
pbrA sequence of
Arthrobacter sp. strain VN23-1 (Jerke
and Nakatsu, personal communication).
Nested PCR optimization.
The initial conditions for nested PCR were established by using
purified plasmid pCGR2 (a gift from C. Rensing) carrying the
E. coli zntA gene. With the exception of the primers (Table
2), the nested PCR mixture was identical to that used for the
16S rDNA PCR described above. The first and second PCRs were
performed for 30 cycles, with a 94°C melting step for 0.5
min, 59 and 49°C annealing steps for 0.5 min for the first
and second reactions, respectively, and a 72°C elongation
step for 1.5 min. After each PCR, the product was electrophoresed
in a 0.75% agarose gel and gel purified (Clontech). The identity
of the
zntA-like gene product was verified by restriction analysis
(by using enzymes and buffers supplied by Invitrogen) and DNA
sequencing (see below).
Paired sets of reference strains of Pbr organisms and their Pbs derivatives were used to optimize amplification conditions for the target sequence from genomic DNA. PCR products were obtained from E. coli W3110, S. aureus K10, R. metallidurans CH34, and Arthrobacter sp. strain VN23-1 (Fig. 1B). Digestion with restriction enzymes (Invitrogen) and DNA sequencing (see below) verified the identities of these products. For most of the PCRs we utilized the conditions described above; the only exceptions were reactions with that the Arthrobacter-specific primers included an annealing temperature of 55°C in the first PCR and 1 mM MgCl2 in both the first and second PCRs. The PCR conditions used for the subsurface isolates were identical to those used for the related control strains with the corresponding primer sets (Table 2).
Sequencing and sequence analysis.
Sequencing was performed directly with zntA/cadA/pbrA-like and 16S rDNA PCR products with a BigDye version 3 reagent mixture (Applied Biosystems). In sequencing reactions for the former products we utilized the 84JC, 81JC, 88JC, 103JC, and 133JC primers, with additional primer walking as needed. Of the 16S rDNA PCR products we utilized the fD1 and 519r primers (30, 85). The sequencing reactions were performed with an ABI 3100 genetic analyzer (Applied Biosystems) at the Biotechnology Center for Agriculture and the Environment, Cook Campus, Rutgers University. Sequence data were compiled in Contig Express (VectorNTI Suite; Informax), translated into amino acid sequences in the case of PIB-type ATPase amplicons, and aligned with ClustalX (81) by using default program settings, followed by verification by eye. Construction of unrooted trees was performed by using the parsimony and distance functions of PAUP*, version 4.0 beta 10 (Sinaur and Associates, Sunderland, Mass.). Bootstrap analyses were performed for all completed trees.
The G+C content and codon usage of each zntA/cadA/pbrA-like amplicon were calculated by using the countcodon program available at the Codon Usage Database website (46). The G+C content of each subsurface amplicon was then compared to the G+C contents of all other organisms belonging to the same genus listed in the database. The ranges given below were verified by using values published in The Prokaryotes (27, 69, 87) when available. Indel analysis was performed visually by observing alignments created in BioEdit (25) by using Clustal W (82). A gap was labeled as an indel only if it was the same length in the organisms in which it was present.
Nucleotide sequence accession numbers.
The nucleotide sequences of the 48 subsurface zntA/cadA/pbrA-like amplicons (average length, 750 bp) have been deposited in the GenBank database under accession numbers AY463172 to AY463192. The nucleotide sequences of the partial 16S rDNA genes (average length, 500 bp) have been deposited in the GenBank database under accession numbers AY463193 to AY463212.

RESULTS
Amplification of zntA/cadA/pbrA-like genes from deep subsurface isolates.
Resistance to Pb(II) in
E. coli (
65),
R. metallidurans (
7),
S. aureus (
53,
65), and possibly
Arthrobacter (Jerke and Nakatsu,
personal communication) is mediated by a P
IB-type ATPase-based
efflux pump. In
E. coli, substrates for this pump also include
Cd(II) and Zn(II) (
65). In a previous study, 105 of 261 deep
subsurface bacterial strains were found to be Pb
r (
6). To investigate
if Pb
r evolved by LGT in subsurface strains, we developed a
nested PCR approach (Fig.
1A) that specifically amplified
zntA/cadA/pbrA-like
amplicons for subsequent sequencing and phylogenetic analysis.
The specificity of the approach for
zntA/cadA/pbrA-like genes
was tested by using three different categories of templates:
(i) purified plasmids carrying a
zntA gene (pCGR2) or a
pbrA-like
gene (pB23F) (Table
1), which tested the ability of the
zntA/
cadA/pbrA-like
primers to recognize the target; (ii) positive controls consisting
of genomic DNA containing
zntA,
cadA,
pbrA, or, in the case
of
Arthrobacter sp. strain VN23-1 and
Staphylococcus sp. strain
K10,
zntA/cadA/pbrA-like genes, which tested the ability of
the primers to recognize
zntA/cadA/pbrA-like genes in the presence
of excess heterologous DNA; and (iii) negative controls consisting
of genomic DNA from deletion mutants or cured strains in which
the target genes are not present, which tested the ability of
the primers to distinguish
zntA/cadA/pbrA-like genes from genes
encoding other P
IB-type ATPases (
copA/silA-like genes) and phylogenetically
related bacterial P
IA- and P
IIIB-type ATPases (
kdpB- and
mgtA-like
genes, respectively) (
57) that may be present. Using four sets
of paired positive and negative control strains belonging to
ß- and

- proteobacteria and the low- and high-G+C-content
gram-positive bacteria, we were able to specifically obtain
zntA/cadA/pbrA-like products (Fig.
1B). These products included
the product of
Staphylococcus sp. strain K10, in which the mechanism
of Pb
r has not been characterized previously (
38), suggesting
that resistance in this strain is mediated by an efflux pump,
as it is in
Staphylococcus plasmid pI258 (
53).
Using genomic DNA as a template, we obtained zntA/cadA/pbrA-like amplicons from 48 of the 105 Pbr subsurface strains. 16S rDNA amplicons were amplified from all genomic DNA samples, suggesting that any PCR failures with our primers were due to either the absence of the target gene or the presence of genes with divergent sequences in the regions targeted by the PCR primers. Multiple zntA/cadA/pbrA-like amplicons were found in at least four subsurface isolates, all Pseudomonas spp. (data not shown). As the complete genome sequences of Pseudomonas alcaligenes (76) and P. fluorescens (unfinished genome; accession no. NZ_AAAT00000000) also contain multiple zntA/cadA/pbrA-like sequences, this may be a general feature of pseudomonads. However, our primers were strongly biased for a specific zntA/cadA/pbrA-like locus because we were able to obtain readable DNA sequence from mixed populations of PCR products. Nevertheless, sequences for the four Pseudomonas spp. strains were not included in the phylogenetic analysis. The bias of the primers for a specific locus was also evident in the recovery of a single zntA/cadA/pbrA-like amplicon from R. metallidurans CH34, which was identified as pbrA from plasmid pMOL30 (44), although a minor zntA/cadA/pbrA-like amplicon was obtained from cured R. metallidurans AE104 (Fig. 1B). The sequence of the AE104 amplicon indicates that it most likely originated from a gene in contig 649 that was recently identified as a chromosomal cadA locus (43). This locus exhibits only 62% identity to the pMOL30-encoded pbrA gene.
Phylogenetic analysis of zntA/cadA/pbrA-like genes of deep subsurface isolates.
Evolution by LGT may be identified by examining the congruency between gene phylogenies (33). A neighbor-joining tree was created by using the amino acid sequences deduced from the zntA/cadA/pbrA-like amplicons (Fig. 2B). Heuristic analysis of the same sequences yielded a tree with the same branching order, although the tree lacked bootstrap support for several of the internal nodes (data not shown). A neighbor-joining tree was also created for a 500-bp section of the 16S rDNA genes from the same strains (Fig. 2A). Some organisms yielded amplicons from both zntA/cadA/pbrA-like and 16S rDNA that were >99% identical, and in these cases selected representatives were chosen for inclusion in the final trees.
The grouping that is immediately noticeable (Fig.
2B) is the
large cluster of
Pseudomonas (

-proteobacterial) amplicons that
group within the ß-proteobacteria (neighbor-joining
bootstrap support at the basal node of the clade, 84). One of
two
zntA/cadA/pbrA-like sequences from the completed genome
of
P. aeruginosa and a single
zntA/cadA/pbrA-like gene from
the genomes of both
P. fluorescens and
P. syringae (data not
shown) also clustered with this group. The most parsimonious
explanation for this incongruency is a single ancient transfer
event involving a ß-proteobacterium that happened
prior to the divergence of the pseudomonads.
In four instances the 16S rDNA tree and the zntA/cadA/pbrA-like tree of the subsurface strains were incongruent (Fig. 2). (i) Comamonas sp. strain B0173 contained a 16S rDNA gene that grouped in the tight cluster of Comamonas spp. genes with nearly identical sequences (Fig. 2A) (bootstrap value for the basal node of the clade, 100) and a zntA/cadA/pbrA-like gene that branched outside most of the ß-proteobacterial cluster (Fig. 2B) (bootstrap value, 68). The sequence did not cluster closely with any known zntA/cadA/pbrA-like sequences, and thus the origin of the gene could not be deduced. (ii) The zntA/cadA/pbrA-like gene of Comamonas sp. strain B0669 clustered with the large group of Comamonas spp. zntA/cadA/pbrA-like genes (bootstrap value for the basal node of the clade, 100), yet the 16S rDNA gene was more closely related to the Comamonas sp. strain B0329 gene on a separate Comamonas spp. branch (bootstrap value, 98). Thus, strain B0669 may have acquired its zntA/cadA/pbrA-like gene from an organism resembling the organisms found in the larger Comamonas cluster. (iii) The 16S rDNA gene of Acinetobacter sp. strain B0064 grouped with the
-proteobacterial genes (bootstrap value, 84), and its zntA/cadA/pbrA-like gene clustered with genes from members of the ß-proteobacterial group (bootstrap value, 89), suggesting that there was a transfer from a ß-proteobacterium to a
-proteobacterium. (iv) Ralstonia sp. strain B0665 contained a zntA/cadA/pbrA-like gene that grouped very closely with the cluster of Pseudomonas spp. loci (bootstrap value, 100) within the ß-proteobacterial clade (see above), suggesting that there was a possible transfer from this source. Thus, an analysis of the incongruencies between the zntA/cadA/pbrA-like and 16S rDNA gene sequences suggested that 4 of 48 zntA/cadA/pbrA-like loci in subsurface bacteria evolved by LGT.
Unusual sequence features of subsurface zntA/cadA/pbrA-like amplicons.
Transferred genes ameliorate to the new host's transcriptional and translational machinery over time (32). Consequently, unusual G+C contents may provide evidence only for recent LGT events. Therefore, the subsurface zntA/cadA/pbrA-like amplicons were examined for unusual DNA base compositions that might indicate recent transfer. Comamonas sp. strain B0173 contained a zntA/cadA/pbrA-like gene with a G+C content lower than those of other known Comamonas strains (60 mol% instead of 61 to 67 mol% [87]), and Acinetobacter sp. strain B0064 had a G+C content higher than those of other Acinetobacter spp. (65 mol% rather than 31 to 63 mol%). Evolution by LGT of the zntA/cadA/pbrA-like genes of these two strains was also suggested by the incongruence analysis (see above). The G+C content of Pseudomonas sp. strain B0188's zntA/cadA/pbrA-like gene (68 mol%) was at the very high end of the range reported for pseudomonads (46), exceeded only by the G+C contents of three open reading frames from Pseudomonas marginata with a combined G+C content of 70.6 mol% (46). The G+C contents of the remaining subsurface zntA/cadA/pbrA-like loci fell within the known range for the genomes of the organisms most closely related to their subsurface hosts.
Codon bias (45, 90) and shared insertions and deletions (indels) (24) are additional indications of evolution by LGT. The former could not be used here, most likely because of the small size of the deduced amino acid sequences (250 amino acids) obtained from the zntA/cadA/pbrA-like amplicons. However, two zntA/cadA/pbrA-like amplicons, one from Comamonas sp. strain B0329 and one from Bacillus sp. strain B0624, contained unique indels on the large cytoplasmic loop connecting transmembrane helices 6 and 7 (63, 83; data not shown). The 4-bp indel of Bacillus sp. strain B0624 was located within a variable region following the phosphorylation domain, and the 1-bp indel of Comamonas sp. strain B0329 was located close to the ATP-binding domain.

DISCUSSION
In this paper we describe one of the first documented accounts
of the application of molecular evolutionary approaches to the
study of microbial LGT in a specific environment, and this study
was the first thorough examination of this process as it relates
to the evolution of metal homeostasis genes in deep subsurface
bacteria. To date, previous retrospective studies have had limited
application to the study of LGT as a process that shapes the
genetic diversity of natural communities. Rather, this issue
has been addressed either by demonstrating transfer in microcosms
(
4,
15) or by examining the potential for LGT by isolation,
identification, and characterization of mobile genetic elements
obtained from environmental strains (
12) or exogenously from
the environment (
70). The time scale for the acquisition of
new genetic material by LGT, estimated to occur at a rate of
31 kb per 10
6 years in
E. coli (
32), may mean that microcosm
studies have little relevance. Indeed, in many cases, LGT could
be detected only following nutrient amendment (
15), by inoculation
of unrealistically high numbers of donor and recipient strains
(
4), or in the presence of selection for phenotypes encoded
by the transferred genes (
81). Observing LGT in microcosm studies
simulating deep subsurface environments may be particularly
difficult, as low population densities and metabolic rates may
require prohibitively long incubation times before transformants
and transconjugants are obtained. Thus, retrospective molecular
evolutionary approaches, which can trace specific LGT events
that have occurred over long time spans, may be the best approach
to study LGT in subsurface environments.
Here we used phylogenetic incongruency, unusual G+C contents, and the presence of indels to trace the probable evolutionary path of metal homeostasis genes in 48 representative isolates belonging to four different groups of common soil bacteria: high- and low-G+C-content gram-positive bacteria and
- and ß-proteobacteria. Table 3 summarizes our findings. For two of the strains, Acinetobacter sp. strain B0064 and Comamonas sp. strain B0173, evidence of LGT determined by phylogenetic incongruency was supported by unusual G+C contents, suggesting that there was relatively recent transfer of the zntA/cadA/pbrA-like locus. As determined by this reasoning, Pseudomonas sp. strain B0188 may also have acquired its zntA/cadA/pbrA-like locus through LGT, since the G+C content of the amplicon does not fall within the known range for Pseudomonas spp. The use of sequence composition alone as a marker for LGT is controversial since it has been shown that G+C contents of genes can vary greatly depending upon the position in the genome (68), amelioration through time (32), and level of expression. Since the phylogenetic position of B0188 is not supported by bootstrap analysis (Fig. 2B), we have not ruled out the possibility that chromosome positioning and/or a higher-than-usual mutation rate, rather than LGT, affected both the G+C content of the gene and its position in the phylogenetic tree. In the case of Ralstonia sp. strain B0665 and in the case of Comamonas sp. strain B0669, phylogenetic evidence was not supported by the G+C content of the zntA/cadA/pbrA-like amplicon (Table 3). These cases may represent transfers from unidentified organisms having similar G+C contents or ancient transfer events.
Because microbes are transported into and within the deep subsurface
(
21), it is not possible to determine whether the transfer events
detected here occurred prior to or following the deposition
of the strains in this environment. At least in the case of
Acinetobacter sp. strain B0064 and in the case of
Comamonas sp. strain B0173, in which transfer appears to have occurred
relatively recently, LGT may have occurred in the deep subsurface.
Unequivocal evidence for the occurrence of transfer in the subsurface
might be obtained by studying populations known to have evolved
in this environment for extended periods of time. Such an opportunity
may be presented by the discovery of coherence between the 16S
rRNA- and
recA-based phylogenies of
Arthrobacter spp. and the
geological strata from which the strains were isolated in the
Yakima Barricade at the U.S. Department of Energy's Hanford
Site, a finding interpreted to indicate spatial separation and
long-term evolution in the deep subsurface (
84).
The collection of bacteria examined here represented closely related phylogenetic groups. The more closely related microbes are phylogenetically, the more likely they are to exchange genetic material (23) but the less likely they are to have a detectable molecular footprint of this transfer in their genomes (20). Many of our isolates belong to the same genus or similar genera; therefore, our study may have underestimated the magnitude of LGT of the zntA/cadA/pbrA-like locus. To obtain a more accurate picture of LGT in a given environment, enrichments and selection methods could be used to obtain isolates representing a broad phylogenetic distance. Targeting this diversity would create its own problems, however, since it would entail a greater degree of diversification in the primary DNA sequence of the gene of interest. Even with the diversity of primers designed for the current collection of isolates (Table 2), amplicons were obtained from only 48 of 105 Pbr subsurface strains. Most likely the diversity of our PCR primer did not match that of the broadly distributed metal homeostasis genes in the bacterial world (2). This possibility, easily explored by Southern hybridization with zntA/cadA/pbrA-specific probes and relaxed stringency to encompass a greater diversity, was not pursued in the present work because our primary goal was to obtain DNA sequences for phylogenetic analysis. As demonstrated by our approach to the design of the ß-proteobacterium-specific primers 87JC and 88JC (Table 2), the challenge of primer and probe design may be lessened as more microbial genomes are sequenced. Furthermore, with the advances in metagenome applications in microbial ecology and the creation of databases linking 16S rDNA genes and functional genes in uncultured microbes (16, 40), studying LGT among uncultured members of the microbial community may be possible one day.
The evolution of metal homeostasis genes by LGT in subsurface bacteria may have ramifications for bioremediation in mixed-waste-contaminated subsurface environments, where the presence of toxic metals may inhibit bioremediation of metals, radionulcides, and organic contaminants. As conjugal transfer of catabolic plasmids from donor strains to soil bacteria enhanced degradation of organic contaminants in topsoils (14, 48) and stimulation of bacterially induced metal immobilization (47, 55) and biodegradation (42) is now practiced in the subsurface, manipulating the genetic potential of subsurface communities to enhance bioremediation may become feasible.
In summary, in this study we used approaches and tools from molecular evolution to examine the role of LGT in the evolution of an ecologically important phenotype in a subsurface microbial community. The integration of molecular evolution and microbial ecology as applied to organisms within a specific environment should expand our understanding of the processes that shape the genetic diversity of microbial communities in their natural habitats.

ACKNOWLEDGMENTS
We thank David Balkwill, Chris Rensing, Kurt Jerke, and Cindy
Nakatsu for providing background information and bacterial cultures,
Chris Rensing and Patty Sobecky for their comments and suggestions
on the manuscript, Shoshanna Tel-Or for technical assistance,
and Alan Kachel for his assistance with DNA sequencing.
This research was funded by the Natural and Accelerated Bioremediation Research (NABIR) program, Biological and Environmental Research (BER), U.S. Department of Energy (grant DE-FG02-99ER62864).

FOOTNOTES
* Corresponding author. Mailing address: Department of Biochemistry and Microbiology, 76 Lipman Dr., New Brunswick, NJ 08901. Phone: (732) 932-9763, ext. 333. Fax: (732) 932-8965. E-mail:
barkay{at}aesop.rutgers.edu.


REFERENCES
1 - Alonso, A., P. Sanchez, and J. L. Martínez. 2000. Stenotrophomonas maltophila D457R contains a cluster of genes from gram-positive bacteria involved in antibiotic and heavy metal resistance. Antimicrob. Agents Chemother. 44:1778-1782.[Abstract/Free Full Text]
2 - Axelsen, K. B., and M. G. Palmgren. 1998. Evolution of substrate specificities in the P-type ATPase superfamily. J. Mol. Evol. 46:84-101.[CrossRef][Medline]
3 - Axelsen, K. B., and M. G. Palmgren. 2001. Inventory of the superfamily of P-type ion pumps in Arabidopsis. Plant Physiol. 126:696-706.[Abstract/Free Full Text]
4 - Barkay, T., N. Kroer, L. D. Rasmussen, and S. J. Sørensen. 1995. Conjugal transfer at natural populations densities in a microcosm simulating an estuarine environment. FEMS Microbiol. Ecol. 16:43-54.
5 - Beard, S. J., R. Hashim, J. Membrillo-Hernandez, M. N. Hughes, and R. K. Poole. 1997. Zinc(II) tolerance in Escherichia coli K-12: evidence that the zntA gene (o732) encodes a cation transport ATPase. Mol. Microbiol. 25:883-891.[CrossRef][Medline]
6 - Benyehuda, G., J. Coombs, P. L. Ward, D. Balkwill, and T. Barkay. 2003. Metal resistance among aerobic chemoheterotrophic bacteria from the deep terrestrial subsurface. Can. J. Microbiol. 49:151-156.[CrossRef][Medline]
7 - Borremans, B., J. L. Hobman, A. Provoost, N. L. Brown, and D. van der Lelie. 2001. Cloning and functional analysis of the pbr lead resistance determinant of Ralstonia metallidurans CH34. J. Bacteriol. 183:5651-5658.[Abstract/Free Full Text]
8 - Breitbart, M., P. Salamon, B. Andresen, J. M. Mahaffy, A. M. Segall, D. Mead, F. Azam, and F. Rohwer. 2002. Genomic analysis of uncultured marine viral communities. Proc. Natl. Acad. Sci. 99:14250-14255.[Abstract/Free Full Text]
9 - Campbell, A. M. 2000. Lateral gene transfer in prokaryotes. Theor. Pop. Biol. 57:71-77.[CrossRef][Medline]
10 - Chapelle, F. H., K. O'Neill, P. M. Bradley, B. A. Methe, S. A. Ciufo, L. L. Knobel, and D. R. Lovley. 2002. A hydrogen-based subsurface microbial community dominated by methanogens. Nature 415:312-315.[CrossRef][Medline]
11 - Claverys, J. P., and B. Martin. 2003. Bacterial "competence" genes: signatures of active transformation, or only remnants? Trends Microbiol. 11:161-165.[CrossRef][Medline]
12 - Cook, M. A., A. M. Osborn, J. Bettandorff, and P. A. Sobecky. 2001. Endogenous isolation of replicon probes for assessing plasmid ecology of marine sediment microbial communities. Microbiology 147:2089-2101.[Abstract/Free Full Text]
13 - Davison, J. 1999. Genetic exchange between bacteria in the environment. Plasmid 42:73-91.[CrossRef][Medline]
14 - Dejonghe, W., J. Goris, S. El Fantroussi, M. Hofte, P. De Vos, W. Verstraete, and E. M. Top. 2000. Effect of dissemination of 2,4-dichlorophenoxyacetic acid (2,4-D) degradation plasmids on 2,4-D degradation and on bacterial community structure in two different soil horizons. Appl. Environ. Microbiol. 66:3297-3304.[Abstract/Free Full Text]
15 - de Lipthay, J. R., T. Barkay, and S. J. Sørensen. 2001. Enhanced degradation of phenoxyacetic acid in soil by horizontal transfer of the tfdA gene encoding a 2,4-dichlorophenoxyacetic acid dioxygenase. FEMS Microbiol. Ecol. 35:75-84.[Medline]
16 - DeLong, E. F. 2002. Microbial population genomics and ecology. Curr. Opin. Microbiol. 5:520-524.[CrossRef][Medline]
17 - Demaneche, S., F. Bertolla, F. Buret, R. Nalin, A. Sailland, P. Auriol, T. M. Vogel, and P. Simonet. 2001. Laboratory-scale evidence for lightning-mediated gene transfer in soil. Appl. Environ. Microbiol. 67:3440-3444.[Abstract/Free Full Text]
18 - Doolittle, W. F. 1999. Phylogenetic classification and the universal tree. Science 284:2124-2129.[Abstract/Free Full Text]
19 - Dröge, M., A. Pühler, and W. Selbitschka. 1999. Horizontal gene transfer among bacteria in terrestrial and aquatic habitats as assessed by microcosm and field studies. Biol. Fertil. Soils 29:221-245.[CrossRef]
20 - Eisen, J. A. 2000. Horizontal gene transfer among microbial genomes: new insights from complete genome analysis. Curr. Opin. Genet. Dev. 10:606-611.[CrossRef][Medline]
21 - Fletcher, M., and E. Murphy. 2001. Transport of microorganisms in the subsurface: the role of attachment and colonization of particle surfaces, p. 39-68. In J. K. Fredrickson and M. Fletcher (ed.), Subsurface microbiology and biogeochemistry. Wiley-Liss, Inc., New York, N.Y.
22 - Fredrickson, J. K., R. J. Hicks, S. W. Li, and F. J. Brockman. 1988. Plasmid incidence in bacteria from deep subsurface sediments. Appl. Environ. Microbiol. 54:2916-2923.[Abstract/Free Full Text]
23 - Gogarten, J. P., W. F. Doolittle, and J. G. Lawrence. 2002. Prokaryotic evolution in light of gene transfer. Mol. Biol. Evol. 19:2226-2238.[Abstract/Free Full Text]
24 - Gupta, R. S. 2001. The branching order and phylogenetic placement of species from completed bacterial genomes, based on conserved indels found in various proteins. Int. Microbiol. 4:187-202.[CrossRef][Medline]
25 - Hall, T. A. 1999. BioEdit: a user-friendly biological sequence alignment editor and analysis program for Windows 95/98/NT. Nucleic Acids Symp. Ser. 41:95-98.
26 - Herrmann, L., D. Schwan, R. Garner, H. L. Mobley, R. Haas, K. P. Schafer, and K. Melchers. 1999. Helicobacter pylori cadA encodes an essential Cd(II)-Zn(II)-Co(II) resistance factor influencing urease activity. Mol. Microbiol. 33:524-536.[CrossRef][Medline]
27 - Jones, D., and R. M. Keddie. May 1999, posting date. The genus Arthrobacter. In M. Dworkin et al. (ed.), The prokaryotes: an evolving electronic resource for the microbiological community, 3rd ed., release 3.0. [Online.] Springer-Verlag, New York, N.Y. http://link.springer-ny.com/link/service/books/10125.
28 - Kieft, T. L., D. B. Ringelberg, and D. C. White. 1994. Changes in ester-linked phospholipid fatty acid profiles of subsurface bacteria during starvation and desiccation in a porous medium. Appl. Environ. Microbiol. 60:3292-3299.[Abstract/Free Full Text]
29 - Kim, E., P. J. Aversano, M. F. Romine, R. P. Schneider, and G. J. Zylstra. 1996. Homology between genes for aromatic hydrocarbon degradation in surface and deep-subsurface Sphingomonas strains. Appl. Environ. Microbiol. 62:1467-1470.[Abstract]
30 - Lane, D. J. 1991. 16S/23S rRNA sequencing. Wiley, Chichester, United Kingdom.
31 - Larbig, K. D., A. Christmann, A. Johann, J. Klockgether, T. Hartsch, R. Merkl, L. Wiehlmann, H. J. Fritz, and B. Tummler. 2002. Gene islands integrated into tRNAGly genes confer genome diversity on a Pseudomonas aeruginosa clone. J. Bacteriol. 184:6665-6680.[Abstract/Free Full Text]
32 - Lawrence, J. G., and H. Ochman. 1997. Amelioration of bacterial genomes: rates of change and exchange. J. Mol. Evol. 44:383-397.[CrossRef][Medline]
33 - Lawrence, J. G., and H. Ochman. 2002. Reconciling the many faces of lateral gene transfer. Trends Microbiol. 10:1-4.[CrossRef][Medline]
34 - LeBrun, M., A. Audurier, and P. Cossart. 1994. Plasmid-borne cadmium resistance genes in Listeria monocytogenes are present on Tn5422, a novel transposon closely related to Tn917. J. Bacteriol. 176:3049-3061.[Abstract/Free Full Text]
35 - LeBrun, M., A. Audurier, and P. Cossart. 1994. Plasmid-borne cadmium resistance genes in Listeria monocytogenes are similar to cadA and cadC of Staphylococcus aureus and are induced by cadmium. J. Bacteriol. 176:3040-3048.[Abstract/Free Full Text]
36 - Lee, S.-W., E. Glickmann, and D. A. Cooksey. 2001. Chromosomal locus for cadmium resistance in Pseudomonas putida consisting of a cadmium-transporting ATPase and a MerR family response regulator. Appl. Environ. Microbiol. 67:1437-1444.[Abstract/Free Full Text]
37 - Levin, B. R., and C. T. Bergstrom. 2000. Bacteria are different: observations, interpretations, speculations, and opinions about the mechanisms of adaptive evolution in prokaryotes. Proc. Natl. Acad. Sci. 97:6981-6985.[Abstract/Free Full Text]
38 - Levinson, H. S., and I. Mahler. 1998. Phosphatase activity and lead resistance in Citrobacter freundii and Staphylococcus aureus. FEMS Microbiol. Lett. 161:135-138.[CrossRef][Medline]
39 - Levinson, H. S., I. Mahler, P. Blackwelder, and T. Hood. 1996. Lead resistance and sensitivity in Staphylococcus aureus. FEMS Microbiol. Lett. 145:421-425.[CrossRef][Medline]
40 - Liles, M. R., B. F. Manske, S. B. Bintrim, J. Handelsman, and R. M. Goodman. 2003. A census of rRNA genes and linked genomic sequences within a soil metagenomic library. Appl. Environ. Microbiol. 69:2684-2691.[Abstract/Free Full Text]
41 - Liu, C.-Q., N. Khunajakr, L. G. Chia, Y.-M. Deng, P. Charoenchai, and N. W. Dunn. 1997. Genetic analysis of regions involved in replication and cadmium resistance of the plasmid pND302 from Lactococcus lactis. Plasmid 38:79-90.[CrossRef][Medline]
42 - Madsen, E. L. 2001. Intrinsic bioremediation of organic subsurface contaminants, p. 249-278. In J. K. Fredrickson and M. Fletcher (ed.), Subsurface microbiology and biogeochemistry. Wiley-Liss, Inc., New York, N.Y.
43 - Mergeay, M., S. Monchy, T. Vallaeys, V. Auquier, A. Benotmaine, P. Bertin, S. Taghavi, J. Dunn, D. van der Lelie, and R. Wattiez. 2003. Ralstonia metallidurans, a bacterium specifically adapted to toxic metals: towards a catalogue of metal-responsive genes. FEMS Microbiol. Rev. 27:385-410.[CrossRef][Medline]
44 - Mergeay, M., D. Nies, H. G. Schlegel, J. Gerits, P. Charles, and F. van Gijsegem. 1985. Alcaligenes eutrophus CH34 is a facultative chemolithotroph with plasmid-bound resistance to heavy metals. J. Bacteriol. 162:328-334.[Abstract/Free Full Text]
45 - Mrazek, J., and S. Karlin. 1999. Detecting alien genes in bacterial genomes. Ann. N. Y. Acad. Sci. 870:314-329.[CrossRef][Medline]
46 - Nakamura, Y., T. Gojobori, and T. Ikemura. 2000. Codon usage tabulated from international DNA sequence databases: status for the year 2000. Nucleic Acids Res. 28:292.[Abstract/Free Full Text]
47 - Nevin, K. P., K. T. Finneran, and D. R. Lovley. 2003. Microorganisms associated with uranium bioremediation in a high-salinity subsurface sediment. Appl. Environ. Microbiol. 69:3672-3675.[Abstract/Free Full Text]
48 - Newby, D. T., K. L. Josephson, and I. L. Pepper. 2000. Detection and characterization of plasmid pJP4 transfer to indigenous soil bacteria. Appl. Environ. Microbiol. 66:290-296.[Abstract/Free Full Text]
49 - Nield, B. S., A. J. Holmes, M. R. Gillings, G. D. Recchia, B. C. Mabbutt, K. M. Nevalainen, and H. W. Stokes. 2001. Recovery of new integron classes from environmental DNA. FEMS Microbiol. Lett. 195:59-65.[CrossRef][Medline]
50 - Nielsen, K. M., K. Smalla, and J. D. van Elsas. 2000. Natural transformation of Acinetobacter sp. strain BD413 with cell lysates of Acinetobacter sp., Pseudomonas fluorescens, and Burkholderia cepacia in soil microcosms. Appl. Environ. Microbiol. 66:206-212.[Abstract/Free Full Text]
51 - Nies, D. H., and S. Silver. 1989. Plasmid-determined inducible efflux is responsible for resistance to cadmium, zinc, and cobalt in Alcaligenes eutrophus. J. Bacteriol. 171:896-900.[Abstract/Free Full Text]
52 - Normander, B., B. B. Christensen, S. Molin, and N. Kroer. 1998. Effect of bacterial distribution and activity on conjugal gene transfer on the phylloplane of the bush bean (Phaseolus vulgaris). Appl. Environ. Microbiol. 64:1902-1909.[Abstract/Free Full Text]
53 - Nucifora, G., L. Chu, T. K. Misra, and S. Silver. 1989. Cadmium resistance from Staphylococcus aureus plasmid pI258 cadA gene results from a cadmium-efflux ATPase. Proc. Natl. Acad. Sci. 86:3544-3548.[Abstract/Free Full Text]
54 - Ochman, H., J. G. Lawrence, and E. A. Groisman. 2000. Lateral gene transfer and the nature of bacterial innovation. Nature 405:299-304.[CrossRef][Medline]
55 - Oliver, D. S., F. J. Brockman, R. S. Bowman, and T. L. Kieft. 2003. Microbial reduction of hexavalent chromium under vadose zone conditions. J. Environ. Qual. 32:317-324.[Abstract/Free Full Text]
56 - O'Sullivan, D., R. P. Ross, D. P. Twomey, G. F. Fitzgerald, C. Hill, and A. Coffey. 2001. Naturally occurring lactococcal plasmid pAH90 links bacteriophage resistance and mobility functions to a food-grade selectable marker. Appl. Environ. Microbiol. 67:929-937.[Abstract/Free Full Text]
57 - Palmgren, M. G., and K. B. Axelsen. 1998. Evolution of P-type ATPases. Biochim. Biophys. Acta 1365:37-45.[Medline]
58 - Paulsen, I. T., L. Banerjei, G. S. Myers, K. E. Nelson, R. Seshadri, T. D. Read, D. E. Fouts, J. A. Eisen, S. R. Gill, J. F. Heidelberg, H. Tettelin, R. J. Dodson, L. Umayam, L. Brinkac, M. Beanan, S. Daugherty, R. T. DeBoy, S. Durkin, J. Kolonay, R. Madupu, W. Nelson, J. Vamathevan, B. Tran, J. Upton, T. Hansen, J. Shetty, H. Khouri, T. Utterback, D. Radune, K. A. Ketchum, B. A. Dougherty, and C. M. Fraser. 2003. Role of mobile DNA in the evolution of vancomycin-resistant Enterococcus faecalis. Science 299:2071-2074.[Abstract/Free Full Text]
59 - Pearson, A. J., K. D. Bruce, A. M. Osborn, D. A. Ritchie, and P. Strike. 1996. Distribution of class II transposase and resolvase genes in soil bacteria and their association with mer genes. Appl. Environ. Microbiol. 62:2961-2965.[Abstract]
60 - Pedersen, K. 1997. Microbial life in deep granitic rock. FEMS Microbiol. Rev. 20:399-414.[CrossRef]
61 - Ragan, M. A. 2001. Detection of lateral gene transfer among microbial genomes. Curr. Opin. Genet. Dev. 11:620-626.[CrossRef][Medline]
62 - Ravel, J., E. M. Wellington, and R. T. Hill. 2000. Interspecific transfer of Streptomyces giant linear plasmids in sterile amended soil microcosms. Appl. Environ. Microbiol. 66:529-534.[Abstract/Free Full Text]
63 - Rensing, C., B. Fan, R. Sharma, B. Mitra, and B. P. Rosen. 2000. CopA: an Escherichia coli Cu(I)-translocating ATPase. Proc. Natl. Acad. Sci. 97:652-656.[Abstract/Free Full Text]
64 - Rensing, C., B. Mitra, and B. P. Rosen. 1997. The zntA gene of Escherichia coli encodes a Zn(II) translocating P-type ATPase. Proc. Natl. Acad. Sci. 94:14326-14331.[Abstract/Free Full Text]
65 - Rensing, C., Y. Sun, B. Mitra, and B. P. Rosen. 1998. Pb(II)-translocating P-type ATPases. J. Biol. Chem. 273:32614-32617.[Abstract/Free Full Text]
66 - Rutherford, J. C., J. S. Cavet, and N. J. Robinson. 1999. Cobalt-dependent transcriptional switching by a dual-effector MerR-like protein regulates a cobalt-exporting variant CPx-type ATPase. J. Biol. Chem. 274:25827-25832.[Abstract/Free Full Text]
67 - Schirawski, J., W. Hagens, G. F. Fitzgerald, and D. van Sinderen. 2002. Molecular characterization of cadmium resistance in Streptococcus thermophilus strain 4134: an example of lateral gene transfer. Appl. Environ. Microbiol. 68:5508-5516.[Abstract/Free Full Text]
68 - Sharp, P. M., D. C. Shields, K. H. Wolfe, and W. H. Li. 1989. Chromosomal location and evolutionary rate variation in enterobacterial genes. Science 246:808-810.[Abstract/Free Full Text]
69 - Slepecky, R. A., and H. E. Hemphill. 21 May 1999, posting date. The genus Bacillusnonmedical. In M. Dworkin et al. (ed.), The prokaryotes: an evolving electronic resource for the microbiological community, 3rd ed., release 3.0. [Online.] Springer-Verlag, New York, N.Y. http://link.springer-ny.com/link/service/books/10125.
70 - Smalla, K., H. Heuer, A. Gotz, D. Niemeyer, E. Krogerrecklenfort, and E. Tietze. 2000. Exogenous isolation of antibiotic resistance plasmids from piggery manure slurries reveals a high prevalence and diversity of IncQ-like plasmids. Appl. Environ. Microbiol. 66:4854-4862.[Abstract/Free Full Text]
71 - Smets, B. F., J. B. Morrow, and C. P. Arango. 2003. Plasmid introduction in metal-stressed subsurface-derived microcosms: plasmid fate and community response. Appl. Environ. Microbiol. 69:4087-4097.[Abstract/Free Full Text]
72 - Smets, B. F., B. E. Rittmann, and D. A. Stahl. 1995. Quantification of the effect of substrate concentration on the conjugal transfer rate of the TOL plasmid in short-term batch mating experiments. Lett. Appl. Microbiol. 21:167-172.[Medline]
73 - Smit, E., A. Wolters, and J. D. van Elsas. 1998. Self-transmissible mercury resistance plasmids with gene-mobilizing capacity in soil bacterial populations: influence of wheat roots and mercury addition. Appl. Environ. Microbiol. 64:1210-1219.[Abstract/Free Full Text]
74 - Solioz, M., and A. Odermatt. 1995. Copper and silver transport by CopB-ATPase in membrane vesicles of Enterococcus hirae. J. Biol. Chem. 270:9217-9221.[Abstract/Free Full Text]
75 - Sørensen, S. J., and L. E. Jensen. 1998. Transfer of plasmid RP4 in the spermosphere and rhizosphere of barley seedling. Antonie Leeuwenhoek 73:69-77.
76 - Stover, C. K., X.-Q. T. Pham, A. L. Erwin, S. D. Mizoguchi, P. Warrener, M. J. Hickey, F. S. L. Brinkman, W. O. Hufnagle, D. J. Kowalik, M. Lagrou, R. L. Garber, L. Goltry, E. Tolentino, S. Westbrook-Wadman, Y. Yuan, L. L. Brody, S. N. Coulter, K. R. Folger, A. Kas, K. Larbig, R. M. Lim, K. A. Smith, D. H. Spencer, G. K.-S. Wong, Z. Wu, I. T. Paulsen, J. Reizer, M. H. Saier, R. E. W. Hancock, S. Lory, and M. V. Olson. 2000. Complete genome sequence of Pseudomonas aeruginosa PA01, an opportunistic pathogen. Nature 406:959-964.[CrossRef][Medline]
77 - Takai, K., M. R. Mormile, J. P. McKinley, F. J. Brockman, W. E. Holben, W. P. Kovacik, Jr., and J. K. Fredrickson. 2003. Shifts in archaeal communities associated with lithological and geochemical variations in subsurface Cretaceous rock. Environ. Microbiol. 5:309-320.[CrossRef][Medline]
78 - Tan, H. M. 1999. Bacterial catabolic transposons. Appl. Microbiol. Biotechnol. 51:1-12.[CrossRef][Medline]
79 - Thelwell, C., N. J. Robinson, and J. S. Turner-Cavet. 1998. An SmtB-like repressor from Synechocystis PCC 6803 regulates a zinc exporter. Proc. Natl. Acad. Sci. 95:10728-10733.[Abstract/Free Full Text]
80 - Thimm, T., A. Hoffmann, I. Fritz, and C. C. Tebbe. 2001. Contribution of the earthworm Lumbricus rubellus (Annelida, Oligochaeta) to the establishment of plasmids in soil bacterial communities. Microb. Ecol. 41:341-351.[Medline]
81 - Thompson, J. D., T. J. Gibson, F. Plewniak, F. Jeanmougin, and D. G. Higgins. 1997. The Clustal X windows interface: flexible strategies for multiple sequence alignment aided by quality analysis tools. Nucleic Acids Res. 25:4876-4882.[Abstract/Free Full Text]
82 - Thompson, J. D., D. G. Higgins, and T. J. Gibson. 1994. CLUSTAL W: improving the sensitivity of progressive multiple sequence alignment through sequence weighting, position-specific gap penalties, and weight matrix choice. Nucleic Acids Res. 22:4673-4680.[Abstract/Free Full Text]
83 - Tsai, K.-J., Y.-F. Lin, M. D. Wong, H. H.-C. Yang, H.-L. Fu, and B. P. Rosen. 2002. Membrane topology of the pI258 CadA Cd(II)/Pb(II)/Zn(II)-translocating P-type ATPase. J. Bioenerg. Biomembr. 34:147-156.[CrossRef][Medline]
84 - van Waasbergen, L. G., D. L. Balkwill, F. H. Crocker, B. N. Bjornstad, and R. V. Miller. 2000. Genetic diversity among Arthrobacter species collected across a heterogeneous series of terrestrial deep-subsurface sediments as determined on the basis of 16S rRNA and recA gene sequences. Appl. Environ. Microbiol. 66:3454-3463.[Abstract/Free Full Text]
85 - Weisburg, W. G., S. M. Barns, D. A. Pelletier, and D. J. Lane. 1991. 16S ribosomal DNA amplification for phylogenetic study. J. Bacteriol. 173:697-703.[Abstract/Free Full Text]
86 - Whitman, W. B., D. C. Coleman, and W. J. Wiebe. 1998. Prokaryotes: the unseen majority. Proc. Natl. Acad. Sci. 95:6578-6583.[Abstract/Free Full Text]
87 - Willems, A., P. de Vos, and J. de Ley. 27 September 2002, posting date. The genus Comamonas. In M. Dworkin et al. (ed.), The prokaryotes: an evolving electronic resource for the microbiological community, 3rd ed., release 3.1. [Online.] Springer-Verlag, New York, N.Y. http://link.springer-ny.com/link/service/books/10125.
88 - Williams, H. G., M. J. Day, J. C. Fry, and G. J. Stewart. 1996. Natural transformation in river epilithon. Appl. Environ. Microbiol. 62:2994-2998.[Abstract]
89 - Wommack, K. E., and R. R. Colwell. 2000. Virioplankton: viruses in aquatic ecosystems. Microbiol. Mol. Biol. 64:69-114.[Abstract/Free Full Text]
90 - Wright, F. 1990. The effective number of codons used in a gene. Gene 87:23-29.[CrossRef][Medline]
Applied and Environmental Microbiology, March 2004, p. 1698-1707, Vol. 70, No. 3
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