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Applied and Environmental Microbiology, July 2005, p. 4121-4126, Vol. 71, No. 7
0099-2240/05/$08.00+0 doi:10.1128/AEM.71.7.4121-4126.2005
Copyright © 2005, American Society for Microbiology. All Rights Reserved.
Analysis of Microbial Gene Transcripts in Environmental Samples
Rachel S. Poretsky,1
Nasreen Bano,1
Alison Buchan,2
Gary LeCleir,1
Jutta Kleikemper,3
Maria Pickering,1
Whitney M. Pate,1
Mary Ann Moran,1* and
James T. Hollibaugh1
Department of Marine Sciences, University of Georgia, Athens, Georgia 30602,1
Department of Molecular, Cellular, and Developmental Biology, P.O. Box 208103, Yale University, New Haven, Connecticut 06520,2
Institute of Terrestrial Ecology, Swiss Federal Institute of Technology Zurich, CH-8952 Schlieren, Switzerland3
Received 12 August 2004/
Accepted 21 January 2005

ABSTRACT
We analyzed gene expression in marine and freshwater bacterioplankton
communities by the direct retrieval and analysis of microbial
transcripts. Environmental mRNA, obtained from total RNA by
subtractive hybridization of rRNA, was reverse transcribed,
amplified with random primers, and cloned. Approximately 400
clones were analyzed, of which

80% were unambiguously mRNA derived.
mRNAs appeared to be from diverse taxonomic groups, including
both
Bacteria (mainly

- and

-
Proteobacteria) and
Archaea (mainly
Euryarchaeota). Many transcripts could be linked to environmentally
important processes such as sulfur oxidation (
soxA), assimilation
of C1 compounds (
fdh1B), and acquisition of nitrogen via polyamine
degradation (
aphA). Environmental transcriptomics is a means
of exploring functional gene expression within natural microbial
communities without bias toward known sequences, and provides
a new approach for obtaining community-specific variants of
key functional genes.

INTRODUCTION
The technology of environmental genomics is based on sequence
analysis of fragments of environmental DNA and retrieves genes
without any previous sequence information and with relatively
little apparent bias (
1,
18,
21). An analogous method for environmental
mRNA (i.e., environmental transcriptomics) could similarly retrieve
the transcriptome of a microbial assemblage without any prior
information on what genes the community might be expressing.
The prospect for using environmental transcriptomics to link
genetic potential with biogeochemical activity of microbes has
been hindered, however, by the difficulties of working with
mRNAs. Prokaryotic transcripts generally lack the poly(A) tails
that make isolation of most eukaryotic messages straightforward
(
12). Some mRNAs degrade quickly, with half-lives as short as
30 s based on studies of cultured bacteria (
2). Finally, mRNA
molecules are much less abundant than rRNA molecules in total
RNA extracts, so the mRNA signal is often overwhelmed by background.
We have developed a protocol to analyze partial environmental transcriptomes by collecting total RNA from the environment, enriching for mRNA by subtractive hybridization of rRNA, and using randomly primed reverse transcription (RT) to produce a cDNA template population. The templates are amplified by PCR and used to generate cDNA clone libraries. Here we report results from the analysis of approximately 400 environmental gene transcripts retrieved directly from bacterioplankton communities of Sapelo Island, GA, and Mono Lake, CA.

Protocol for library generation.
Water samples were collected from the Sapelo Island Microbial
Observatory (SIMO; tidal salt marsh creek in the southeastern
United States;
http://simo.marsci.uga.edu/) and the Mono Lake
Microbial Observatory (MLMO; closed-basin, hypersaline soda
lake near Lake Tahoe, CA;
http://www.monolake.uga.edu/). SIMO
water samples (10 liters) were collected in October 2002 and
August 2003 and screened immediately after collection to remove
particles of >3.0 µm, including most eukaryotic cells.
Cells for RNA extraction were collected on a 0.2-µm-pore-size
polycarbonate membrane filter. MLMO samples (8 liters) were
collected in May 2003 at depths of 5 m (surface) and 23 m (chemocline).
Because the dominant phytoplankter (
Picocystis salinarum) is
of a size similar to the bacterioplankton, MLMO samples were
not screened. MLMO samples were stored on ice during transport
to the laboratory and then filtered onto a 0.2-µm-pore-size
membrane filter.
The process from sample collection to RNA extraction was done as rapidly as possible to limit degradation of mRNA. RNA was extracted using a RNAqueous-Midi kit (Ambion, Austin, TX) with several modifications (see the supplemental material for detailed protocol). For SIMO samples, the elapsed time between water collection and RNA extraction was less than 30 min. For MLMO samples, the elapsed time was
2 h. Subtractive hybridization was used to selectively remove rRNA (MICROBExpress Bacterial mRNA enrichment kit; Ambion). DNase-treated mRNA preparations were amplified by RT-PCR using two of six possible random primers (see Table S1 in the supplemental material): 10-mer primers OPA04, OPA13, and OPA17 from a commercial primer stock (Operon Technologies, Inc., Alameda, CA), primer SD14 designed to target the Shine-Dalgarno region of bacterial mRNAs (5), and primers SES3-1 and SESRT-3 designed with low G+C content (MLMO only). Clone libraries of some PCR products were screened to eliminate sequences derived from contaminating rRNA using probes constructed by amplifying rRNA genes from DNA harvested from the same sample (see the supplemental material for detailed protocol). Sequences of 347 SIMO clones (40 from October 2002 and 307 from August 2003) and 60 MLMO clones were analyzed using the BLASTX and BLASTN tools (http://www.ncbi.nlm.nih.gov/BLAST/). Additionally, 282 of the August 2003 SIMO clones were automatically annotated using the Annotation Engine service provided by The Institute for Genomic Research (Rockville, MD).

Environmental transcript libraries.
We calculate that 2.4
x 10
13 bacterial mRNAs were present in
the 10-liter SIMO water samples collected in August 2003, of
which 80,000 were unique (calculated assuming a late summer
population of 1.7
x 10
6 bacterial cells ml
1 [
http://gce-lter.marsci.uga.edu]
each with 1,380 total mRNA molecules per cell [
10] and 200 bacterial
species represented in the community [
http://simo.marsci.uga.edu/MainWeb/pages/database.htm/]
each with 400 unique mRNAs per cell [
10]). Thus the 342 SIMO
clones and 60 MLMO clones analyzed here were a small fraction
of the total transcript pool in each environment. Yet while
these small libraries do not provide a quantitative inventory
of bacterioplankton transcripts, they offer a novel glimpse
of microbial activity that is unconstrained by existing sequence
data and not restricted to previously characterized processes.
Further, the standard cloning and sequencing methods used for
these manually assembled libraries can be readily adapted to
high-throughput approaches, potentially allowing the sequencing
of thousands of amplicons from a single community.
Sublibraries were generated from a single sample using different primer combinations, with one primer chosen at random for the RT step and that primer used in combination with a second primer in the PCR step (see Table S2 in the supplemental material). When we compared transcript retrieval with different permutations of the random primers, the SD14 primer appeared to outcompete the others. Often, both ends of the amplicons were primed by SD14. No amplicons were generated for MLMO samples without SD14 in either the RT or PCR step, although several primer combinations without SD14 were used with success in the SIMO samples (see Table S2 in the supplemental material). The higher amplification efficiency with the SD14 primer is not surprising, as primers designed to bind to the Shine-Dalgarno region (the ribosomal binding site) have been used in differential display analyses of mRNA transcripts in both pure cultures and in soils (5). When used as a PCR primer, it ostensibly biases amplification to the 5' end of mRNA transcripts for bacteria that possess a typical Escherichia coli-like Shine-Dalgarno region (e.g., AGGAGG) (10). When used as an RT primer, we expected to see the SD14 primer sequence only for polycistronic operons because it would target the Shine-Dalgarno site at the beginning of the gene downstream from the one that was reverse transcribed. Because the SD14 primer sequence was often identified at both the beginning and end of sequences following RT-PCR, we concluded that SD14 does not necessarily target the Shine-Dalgarno site exclusively when used under low-specificity PCR conditions.
Although we still observed a few rRNA-generated cDNA sequences after repeated subtractive hybridizations, analysis of the clone libraries indicated that the protocol for removing rRNA worked effectively, as typically fewer than 20% of the clones were derived from 16S, 23S, and 28S rRNA combined (see Table S2 in the supplemental material). Results from colony hybridizations of the SIMO clone libraries indicated that perhaps a higher percentage of clones were rRNA generated, but this screening step reduced the number of rRNA clones sequenced. Even though they were not screened by hybridization, MLMO cDNA libraries contained few rRNA genes, indicating that the subtractive hybridization alone worked efficiently for these samples.

Apparent taxonomic representation.
The putative taxonomic origin of the transcripts was used to
assess diversity in relation to the known microbial composition
of the two systems. Putative taxonomic origin was assigned based
on the taxon of the most similar sequence by BLAST analysis
(see Table S3 in the supplemental material). The accuracy of
this assignment is negatively affected by lateral gene transfer
and positively correlated with the taxonomic coverage of the
database for any given gene. Given these caveats, the SIMO libraries
appeared to be almost entirely bacterial derived, although similarities
to known genes were sometimes low (see Table S3 in the supplemental
material). Using only those sequences with E values of

e
10,
gene expression at the SIMO site was inferred for

-, ß-,

-,

-, and
-Proteobacteria,
Bacteroidetes,
Chlorobi,
Cyanobacteria,
Firmicutes,
Actinobacteria,
Spirochaetes,
Planctomycetes,
Euryarchaeota,
and
Crenarchaeota. Apparent archaeal sequences represented a
significant portion of the August 2003 SIMO library (Fig.
1A).
Almost all of the putative archaeal transcripts were most similar
to genes from
Sulfolobus tokodaii or
Methanococcus voltae, but
identification may be skewed toward organisms for which a genome
sequence is available.
A small-subunit rRNA database of SIMO bacterioplankton that
was generated during a different year, but for the same season
(summer) and the same size fraction (0.2 to 3.0 µm) (
http://simo.marsci.uga.edu/),
provided a comparison with the putative taxonomic assignment
of the transcripts in the August 2003 mRNA library. The SIMO
16S rRNA libraries were dominated by sequences from
- and

-
Proteobacteria (18 and 16%) (Fig.
1B). These two taxonomic groups were similarly
represented in the mRNA library (16 and 19%, respectively).
Cyanobacteria played a larger role in the 16S rRNA library (Fig.
1B) than in the mRNA library while
Chlorobi,
-Proteobacteria,
and
Spirochaetes appeared to contribute to the mRNA pool but
were not well represented in the 16S rRNA library. Overall,
relatively similar distributions among apparent taxonomic groups
existed between the two libraries. The transcripts in the August
2003 SIMO library were also compared to the genome of
Silicibacter pomeroyi, a marine
-Proteobacteria isolated from coastal water
near the SIMO site (
http://www.marsci.uga.edu/s_pomeroyi/) (
6,
15). Using BLASTX, almost 10% of the clones in the SIMO transcript
library matched predicted proteins in the
S. pomeroyi genome
with identities higher than other entries in GenBank, with E
values between e
70 and e
97 in most cases.
At MLMO, 33% of the 60 transcripts appeared to be eukaryotic in origin; not surprising given that the spring phytoplankton bloom was under way during sample collection and eukaryotes were too small to be removed by size-selective screening. Prokaryotic MLMO transcripts matched genes from Firmicutes, Cyanobacteria, Bacteroidetes, Spirochaetes, Actinobacteria, Planctomycetes, and
-, ß-,
-, and
-Proteobacteria. Putative taxonomic affiliations of MLMO transcripts were consistent with a 16S rRNA gene library constructed in July 2000, as evidenced by the presence of
-Proteobacteria-like sequences in surface and chemocline samples in both mRNA and 16S rRNA libraries, as well as a cyanobacterial-like mRNA and 16S rRNA sequences in the chemocline (9). Although there is uncertainty in the taxonomic assignment of mRNA sequences as discussed above, environmental transcripts appeared to be retrieved from a diversity of microorganisms at both the SIMO and MLMO sites.

Transcript annotation.
Most of the sequences obtained were not full-length transcripts
(

200 to 500 bp), although some amplicons were large (>1,000
bp). In all cases, there was no amplification in controls that
lacked the RT step. The mRNA sequences appeared to be transcribed
from a range of housekeeping genes, components of transport
systems, and genes for energy metabolism (Table
1). Like the
taxonomic assignments, the identities of transcripts were inferred
from the closest matches by BLASTX (see Table S3 in the supplemental
material). These assignments are only as good as the existing
database, and genes that are rare in genomes because they code
for unusual or specialized traits are particularly susceptible
to poor database coverage. For example, a MLMO transcript with
a strong BLAST hit to an arsenite transporter (
arsA) from
Arabidopsis thaliana (Table
1) predicts a function expected in Mono Lake
given the high concentration of arsenite (200 µM) (
14)
but predicts an organism quite distant from any lake plankton.
View this table:
[in this window]
[in a new window]
|
TABLE 1. Selected mRNA sequences with inferred functions of ecological or geochemical relevance in cDNA libraries constructed from SIMO (top) and MLMO (bottom) samplesa
|
In all libraries, several instances of multiple mRNAs transcribed
from homologous genes were seen. Some of the repeated mRNAs,
such as those having sequence similarity to
soxA (sulfur oxidation;
eight sequences) and
surE (stationary-phase survival protein;
four sequences) were found in different sublibraries (i.e.,
libraries constructed from the same RNA sample but using different
primer pairs). In all but one case, the homologous sequences
were found in eight or fewer clones, with the exception being
transcripts putatively encoding acetylpolyamine amidohydrolase
(
aphA) that accounted for 35 of 307 clones in the August 2003
sample.
Annotation of the clones from the SIMO libraries revealed that the majority (
80%) were found only once in the library. In contrast, nearly half (42%) of the 60 MLMO sequences were homologous to another sequence in the library. Four clones from the SIMO August 2003 sample and three clones from MLMO had no significant matches using an EXPECT threshold of 10 in homology searches (BLASTN and BLASTX) and thus either are transcripts of novel genes or are not transcripts.
The Institute for Genomic Research Annotation Engine organized the August 2003 SIMO sequences into role categories based on assigned functions of the highest matching gene sequences, including central intermediary metabolism (18.5% of the clones), cellular processes (5.5%), and protein synthesis (5.0%) (Table 2). Transcripts that appeared to code for transport/binding proteins (3.8%) were potentially involved in amino acid, carbohydrate, and organic acid and alcohol transport and metabolism (Table 2). The largest fraction of transcripts was categorized as hypothetical (35.3%), and 12% were "unclassified" (typically of known function but not readily placed in a role category during autoannotation). As discussed above, inferred functional assignments of transcripts are subject to effects of database coverage and lateral gene transfer.
View this table:
[in this window]
[in a new window]
|
TABLE 2. SIMO transcript identities and assigned role categories (August 2003 sample) as determined by the TIGR Annotation Engine
|
There are significant methodological obstacles in retrieving
an environmental transcriptome that may result in the unequal
capture of transcripts, including choice of primer, preferential
targeting of transcripts, and bias toward the longest-lived
mRNAs. In assessing the issue of targeting bias, we found evidence
for selective amplification of some targets by a given primer
pair, such as
soxA transcript amplification only when both OPA13
and OPA17 primers were used and
aphA transcript amplification
only if primer SD14 was used. In assessing the issue of mRNA
lifetime, we examined three gene categories predicted to have
longer half-lives based on studies of
E. coli transcripts: cell
envelope genes, energy metabolism genes, and transport/binding
genes (
3). The 307-member August 2003 SIMO environmental transcript
library was not dominated by any of these functional categories,
although evidence from organisms such as
Bacillus subtilis indicates
that there are both long and short half-life transcripts in
almost all gene classes (
7). For the MLMO transcript library,
for which the time from collection to processing was

2 h, potential
biases related to mRNA half-life could not be evaluated.

Applications of environmental transcriptomics.
A promising application of environmental transcriptomics is
the retrieval of community-specific functional gene sequences
with relevance for quantitative ecological studies. Functional
gene discovery in natural environments is typically based on
primer sets designed from a limited database that is heavily
biased toward cultured organisms (
17). Environmental transcript
libraries can alleviate this problem by supplying site-specific
functional gene sequences from active cells without the constraints
of prior sequence information. For example, the eight putative
soxA sequences in the SIMO library were similar to one another
but distinct from those found in cultured bacteria (Fig.
2).
Quantitative PCR analysis of DNA from an August 2004 SIMO bacterioplankton
community, using a primer set designed to target only the SIMO
clade
soxA genes, indicated that they were present at concentrations
of

4.6
x 10
6 liter
1, or in 1 of every 370 cells (assuming
1.7
x 10
6 cells ml
1 and one gene copy per cell). Further,
soxA transcripts were retrieved from four samples collected
within an 11-h period in August 2004 using RT-quantitative PCR
(averaging 2.6
x 10
3 transcripts liter
1), suggesting
that SIMO clade
soxA genes are consistently transcribed within
the bacterioplankton community. The putative chitinase transcript
in the MLMO library (Table
1), which has low identity to known
chitinase sequences (<27%), is also of significance because
chitinase genes cannot be amplified from the Mono Lake ecosystem
using existing
chi primer sets (
11). Nevertheless, the abundance
of arthropod exoskeletons in the lake along with previous demonstrations
of chitinase activity (
11) suggest that chitin degradation is
a major microbial process in this system. Environmental transcriptomics
thus provides gene sequences of biogeochemical interest (Table
1) without constraints imposed by existing sequence data and
with preference for those genes being actively expressed.
Environmental transcriptomics also has considerable potential
for generating novel hypotheses about microbial processes. In
the SIMO library, putative acetylpolyamine amidohydrolase (
aphA)
transcripts accounted for 11% of the sequences in the August
2003 SIMO library, represented by at least seven distinct sequences
in four sublibraries. The possible ecological relevance of these
sequences is not immediately apparent because prokaryotic
aphA genes are poorly characterized. However, they are suspected
to encode proteins involved in the degradation of polyamines
(
19), a class of nitrogen-rich compounds including putrescine
and spermidine that form complexes with DNA and RNA and act
as important signaling compounds for cell growth (
20). Evidence
in support of a hypothesis that the
aphA transcripts reflect
a role for polyamines as a nitrogen source for coastal bacterioplankton
includes the facts that polyamines are produced by marine algae,
plants, invertebrates, and microorganisms (
8,
13,
16,
20), they
reach concentrations of 30 nM in coastal seawater during algal
blooms (
16), and they are readily assimilated by coastal and
open ocean bacterioplankton communities (
8). Further, the genome
sequence of marine bacterium
S. pomeroyi contains an
aphA homolog
located in an apparent operon with a polyamine transporter (
potABCD)
(
15) and candidate genes for a putrescine degradation pathway
(putrescine transaminase and aminobutyraldehyde dehydrogenase).
The
aphA transcripts may be a response to unusual conditions
caused by sample processing (e.g., a spike in polyamine concentrations
due to eukaryotic cell breakage during filtration), but nonetheless
indicate an ability of bacteria to respond rapidly to the availability
of these nitrogen-rich compounds in seawater. While polyamine
assimilation by marine bacteria has been considered in the past
(
8), the SIMO transcript library forms the foundation of a hypothesis
that these compounds are a more important source of dissolved
organic nitrogen for coastal bacterioplankton than is currently
suspected.
Our environmental transcriptomics protocol was used successfully to survey two very different types of aquatic communities for microbial gene expression, without the constraints of targeting specific organisms, phylogenetic groups, or metabolic pathways. While the libraries analyzed here were small, this approach can be readily adapted for high-throughput processing and automated annotation and can be coupled to environmental genomics methods to assess genetic potential and patterns of activity in natural microbial assemblages.

Nucleotide sequence accession numbers.
Newly determined sequences were deposited in GenBank under the
accession numbers
AY793704 to
AY794012.

ACKNOWLEDGMENTS
We thank J. R. Henriksen for help with sequence analysis, E.
C. Hierling and J. Shalack for assistance with sample collection
and analysis, and three anonymous reviewers for constructive
comments. This work was supported by National Science Foundation
(NSF) grants MCB-0084164 to the Sapelo Island Microbial Observatory
and MCB-9977886 to the Mono Lake Microbal Observatory, as well
as by the Gordon and Betty Moore Foundation. R.S.P. was funded
by an NSF graduate research fellowship, and M.P. and W.M.P.
were funded by NSF REU fellowships. The Annotation Engine service
was provided by The Institute for Genomic Research as a result
of funding from the Department of Energy and the NSF.

FOOTNOTES
* Corresponding author. Mailing address: Department of Marine Sciences, University of Georgia, Athens, GA 30602. Phone: (706) 542-6481. Fax: (706) 542-5888. E-mail:
mmoran{at}uga.edu.

Supplemental material for this article may be found at http://aem.asm.org/. 

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Applied and Environmental Microbiology, July 2005, p. 4121-4126, Vol. 71, No. 7
0099-2240/05/$08.00+0 doi:10.1128/AEM.71.7.4121-4126.2005
Copyright © 2005, American Society for Microbiology. All Rights Reserved.
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