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Applied and Environmental Microbiology, October 2002, p. 5064-5081, Vol. 68, No. 10
0099-2240/02/$04.00+0 DOI: 10.1128/AEM.68.10.5064-5081.2002
Copyright © 2002, American Society for Microbiology. All Rights Reserved.
Oligonucleotide Microarray for 16S rRNA Gene-Based Detection of All Recognized Lineages of Sulfate-Reducing Prokaryotes in the Environment
Alexander Loy,1 Angelika Lehner,1 Natuschka Lee,1 Justyna Adamczyk,1 Harald Meier,2 Jens Ernst,3 Karl-Heinz Schleifer,1 and Michael Wagner1*
Lehrstuhl für Mikrobiologie, Technische Universität München, D-85350 Freising,1
Lehrstuhl für Rechnertechnik und Rechnerorganisation,2
Lehrstuhl für Effiziente Algorithmen, Technische Universität München, D-80290 Munich, Germany3
Received 13 March 2002/
Accepted 5 July 2002

ABSTRACT
For cultivation-independent detection of sulfate-reducing prokaryotes
(SRPs) an oligonucleotide microarray consisting of 132 16S rRNA
gene-targeted oligonucleotide probes (18-mers) having hierarchical
and parallel (identical) specificity for the detection of all
known lineages of sulfate-reducing prokaryotes (SRP-PhyloChip)
was designed and subsequently evaluated with 41 suitable pure
cultures of SRPs. The applicability of SRP-PhyloChip for diversity
screening of SRPs in environmental and clinical samples was
tested by using samples from periodontal tooth pockets and from
the chemocline of a hypersaline cyanobacterial mat from Solar
Lake (Sinai, Egypt). Consistent with previous studies, SRP-PhyloChip
indicated the occurrence of
Desulfomicrobium spp. in the tooth
pockets and the presence of
Desulfonema- and
Desulfomonile-like
SRPs (together with other SRPs) in the chemocline of the mat.
The SRP-PhyloChip results were confirmed by several DNA microarray-independent
techniques, including specific PCR amplification, cloning, and
sequencing of SRP 16S rRNA genes and the genes encoding the
dissimilatory (bi)sulfite reductase (
dsrAB).

INTRODUCTION
Anaerobic respiration with sulfate is a central component of
the global sulfur cycle and is exhibited exclusively by prokaryotes
(
53). Sulfate-reducing prokaryotes (SRPs) are thus of major
numerical and functional importance in many ecosystems, including
marine sediments (
14,
29,
30,
38,
54) and cyanobacterial microbial
mats (
46,
56,
70). Recently, SRPs were also identified as unculturable
symbionts of gutless marine oligochetes (
15) and as uncultured
components of microbial aggregates catalyzing anaerobic methane
oxidation (
4,
10,
48,
72). In addition, some SRPs have been
implicated in human disease (
32,
35,
39,
43,
60,
69). More than
130 species of SRPs have been described so far, and they comprise
a phylogenetically diverse assemblage of organisms consisting
of members of at least four bacterial phyla and one archaeal
phylum (
11,
12,
66). The polyphyletic affiliation of SRPs and
the fact that several SRPs are closely related to microorganisms
which cannot perform anaerobic sulfate reduction for energy
generation hamper cultivation-independent detection of these
organisms by established 16S rRNA-based methods because many
different PCR primer sets or probes would be required to target
all members of this microbial guild. Consequently, previous
environmental microbiology research on the composition of SRP
communities performed by using specific 16S rRNA gene-targeting
PCR systems or probes has focused on a few selected genera or
groups (
16,
24,
36,
41,
49,
50,
56,
59,
68,
71).
Nucleic acid microarrays, which have recently been introduced for bacterial identification in microbial ecology (5, 23, 37, 62, 73, 77), provide a powerful tool for parallel detection of 16S rRNA genes (23, 37, 62, 73) and thus might be particularly useful for environmental studies of phylogenetically diverse microbial groups. However, most microarrays developed so far for bacterial identification consist of a limited number of probes and are mainly used for method development and optimization. In this study, we developed and successfully used a microarray consisting of 132 16S rRNA-targeted oligonucleotide probes covering all recognized lineages of SRPs for high-resolution screening of clinical and environmental samples. For periodontal tooth pockets and a hypersaline microbial mat, microarray SRP diversity fingerprints were found to be consistent with results obtained by using well-established molecular methods for SRP community composition analysis.

MATERIALS AND METHODS
Pure cultures of SRPs.
Table
1 lists the 42 reference organisms that were obtained
as lyophilized cells or active cultures from the Deutsche Sammlung
von Mikroorganismen und Zellkulturen (Braunschweig, Germany)
and were used to evaluate our microarray (SRP-PhyloChip).
Archaeoglobus veneficus SNP6
T (containing plasmid XY) was deposited in the
Deutsche Sammlung von Mikroorganismen und Zellkulturen by K.
O. Stetter, Lehrstuhl fur Mikrobiologie, Universität Regensburg,
Regensburg, Germany, as DSM 11195
T.
Solar Lake mat sample.
A core (1 by 1cm; depth, 4 cm) of a hypersaline cyanobacterial
mat from Solar Lake (Sinai, Egypt) was sectioned horizontally
at 200-µm intervals with a cryomicrotome (MIKROM HM500;
Microm, Walldorf, Germany). The mat sections were stored at
-80°C.
Peridontal tooth pocket samples.
Samples from five patients with adult periodontitis were taken by inserting a sterile medium-sized paper point into a single periodontal tooth pocket. After sampling the paper points were stored at -20°C.
DNA extraction.
Genomic DNA was isolated from reference organisms with a FastDNA kit (Bio 101, Vista, Calif.). DNA from periodontal tooth pocket material and DNA from a cryosection of Solar Lake mat from the chemocline (1,400 to 1,600 µm from the mat surface) were extracted by using a modification of the protocol of Griffiths et al. (22). In contrast to the original protocol, precipitation of nucleic acids in the aqueous phase was performed with 0.1 volume of sodium acetate (pH 5.2) and 0.6 volume of isopropanol for 2 h at room temperature.
PCR amplification of 16S rRNA and dsrAB genes.
For subsequent DNA microarray hybridization, almost complete 16S rRNA gene fragments were amplified from DNA of pure cultures of SRPs by using the 616V-630R primer pair (Table 2). 16S rRNA gene fragments of A. veneficus were amplified by using the newly designed Archaeoglobus genus-specific forward primer ARGLO36F and the universal reverse primer 1492R (Table 2). Amplification of bacterial 16S rRNA gene fragments from periodontal tooth pocket or Solar Lake mat genomic DNA was performed by using the 616V-630R and 616V-1492R primer pairs (Table 2).
To confirm DNA microarray results, specific amplification of
16S rRNA gene fragments of defined SRP groups was performed
with periodontal tooth pocket DNA and Solar Lake mat DNA by
using previously described and newly designed primers (Table
2). In addition, an approximately 1.9-kb
dsrAB fragment was
amplified from periodontal tooth pockets by using primers DSR1F
and DSR4R under the conditions described by Wagner et al. (
76).
Positive controls containing purified DNA from suitable reference organisms were included in all of the PCR amplification experiments along with negative controls (no DNA added). For 16S rRNA gene amplification, reaction mixtures (total volume, 50 µl) containing each primer at a concentration of 25 pM were prepared by using 10x Ex Taq reaction buffer and 2.5 U of Ex Taq polymerase (Takara Biomedicals, Otsu, Shiga, Japan). Additionally, 20 mM tetramethylammonium chloride (Sigma, Deisenhofen, Germany) was added to each amplification mixture to enhance the specificity of the PCR (31). Thermal cycling was carried out by using an initial denaturation step of 94°C for 1 min, followed by 30 cycles of denaturation at 94°C for 40 s, annealing at temperatures ranging from 52 to 60°C (depending on the primer pair [Table 2]) for 40 s, and elongation at 72°C for 1 min 30 s. Cycling was completed by a final elongation step of 72°C for 10 min.
Fluorescence labeling of PCR amplificates.
Prior to labeling, PCR amplificates were purified by using a QIAquick PCR purification kit (Qiagen, Hilden, Germany). Subsequently, the amount of DNA was determined spectrophotometrically by measuring the optical density at 260 nm. Purified PCR products were labeled with Cy5 by using a DecaLabel DNA labeling kit (MBI Fermentas, Vilnius, Lithuania). Reaction mixtures (total volume, 45 µl) containing 200 ng of purified PCR product and 10 µl of decanucleotides in reaction buffer were denatured at 95°C for 10 min and immediately placed on ice. After addition of 3 µl of deoxynucleotide Mix C (containing no dCTP), 1 µl of Cy5-dCTP (Amersham Biosciences, Freiburg, Germany), and 1 µl of the Klenow fragment (Exo-; 5 U µl-1), the labeling reaction mixtures were incubated at 37°C for 45 min. For more efficient labeling, the addition of Mix C, Cy5-dCTP, and the Klenow fragment and incubation at 37°C for 45 min were repeated. Labeling was completed by addition of 4 µl of dNTP-Mix and incubation at 37°C for 60 min. To remove unincorporated deoxynucleotides and decanucleotides, the labeling mixture was purified with a QIAquick nucleotide removal kit (Qiagen) by using double-distilled water for DNA elution. Finally, the eluted DNA was vacuum dried and stored in the dark at -20°C.
Microarray manufacture and processing.
Oligonucleotides for microarray printing were obtained from MWG Biotech (Ebersberg, Germany). The sequence, specificity, and microarray position of each oligonucleotide probe are shown in Table 3. In addition, difference alignments for all probes generated with the latest ARB small-subunit rRNA database (http://www.arb-home.de) can be viewed at the probeBase website (http://www.probebase.net). The 5' end of each oligonucleotide probe was tailed with 15 dTTP molecules (T-spacer) to increase the on-chip accessibility of spotted probes to target DNA (61, 63). In addition, the 5'-terminal nucleotide of each oligonucleotide was aminated to allow covalent coupling of the oligonucleotides to aldehyde group-coated CSS-100 glass slides (CEL Associates, Houston, Tex.). The concentration of oligonucleotide probes before printing was adjusted to 50 pmol µl-1 in 50% dimethyl sulfoxide to prevent evaporation during the printing procedure. SRP-PhyloChips were printed by using a GMS 417 contact arrayer (Affymetrix, Santa Clara, Calif.). Spotted DNA microarrays were dried overnight at room temperature to allow efficient cross-linking. Slides were washed twice at room temperature in 0.2% sodium dodecyl sulfate (SDS) and then twice with double-distilled water with vigorous agitation to remove unbound oligonucleotides and the SDS. After air drying, the slides were incubated for 5 min in a fresh sodium borohydride solution (1.0 g of NaBH4 in 300 ml of phosphate-buffered saline and 100 ml of absolute ethanol) to reduce all remaining reactive aldehyde groups on the glass. The reaction was stopped by adding ice-cold absolute ethanol. The reduced slides were washed three times (with 0.2% SDS and double-distilled water), air dried, and stored in the dark at room temperature.
Reverse hybridization on microarrays.
Vacuum-dried Cy5-labeled PCR products (400 ng) and 0.5 pmol
of the Cy5-labeled control oligonucleotide CONT-COMP (Table
3) were resuspended in 20 µl of hybridization buffer (5
x SSC, 1% blocking reagent [Roche, Mannheim, Germany], 0.1%
n-lauryl
sarcosine, 0.02% SDS, 5% formamide [1
x SSC is 0.15 M NaCl plus
0.015 M sodium citrate]), denatured for 10 min at 95°C,
and immediately placed on ice. Then the solution was pipetted
onto an SRP-PhyloChip, covered with a coverslip, and inserted
into a tight custom-made hybridization chamber (
http://cmgm.stanford.edu/pbrown/mguide/HybChamber.pdf)
containing 50 µl of hybridization buffer for subsequent
equilibration. Hybridization was performed overnight at 42°C
in a water bath. After hybridization, the slides were washed
immediately under stringent conditions for 5 min at 55°C
in 50 ml of washing buffer (containing 3 M tetramethylammonium
chloride, 50 mM Tris-HCl, 2 mM EDTA, and 0.1% SDS). To record
probe-target melting curves, the temperature of the washing
step was varied from 42 to 80°C. After the stringent washing,
the slides were washed twice with ice-cold double-distilled
water, air dried, and stored in the dark at room temperature.
Scanning of microarrays.
Fluorescence images of the SRP PhyloChips were recorded by scanning the slides with a GMS 418 array scanner (Affymetrix). The fluorescence signals were quantified by using the ImaGene 4.0 software (BioDiscovery, Inc., Los Angeles, Calif.). A grid of individual circles defining the location of each spot on the array was superimposed on the image to designate each fluorescent spot to be quantified. The mean signal intensity was determined for each spot. In addition, the mean signal intensity of the local background area surrounding the spots was determined.
Selective enrichment of nucleic acids by a capture probe approach.
Five microliters of aldehyde group-coated glass beads (diameter, 1 µm; Xenopore, Hawthorne, N.J.) was incubated overnight with 5 µl of the appropriate capture probe (100 pmol µl-1; tailed with 15 dTTP molecules; aminated with 5'-terminal nucleotide) at room temperature. Subsequently, the beads were washed once with 400 µl of 0.2% SDS and pelleted by centrifugation (1 min at 14,000 rpm; Hettich Zentrifuge type 1000, Tuttlingen, Germany), and the supernatant was decanted. After this step, the beads were washed twice with 400 µl of double-distilled water, dried, and stored at room temperature prior to hybridization. A vacuum-dried bacterial 16S rRNA gene PCR product (obtained from DNA from the Solar Lake mat with the 616V-1492R primer pair) was resuspended in 200 µl of hybridization buffer (see above), denatured for 10 min at 95°C, and immediately cooled on ice. The hybridization solution and capture probe beads were mixed in a screw-cap tube and incubated overnight at 42°C on a shaker. Subsequently, the beads were washed twice with 1.5 ml of washing buffer (see above) at 55°C for 2.5 min. After the stringent washes, the beads were washed with 1.5 ml of ice-cold double-distilled water and then with ice-cold 70% ethanol. Beads with captured nucleic acids were vacuum dried and resuspended in 50 µl of EB buffer (part of the QIAquick PCR purification kit; Qiagen) for storage at -20°C. Reamplification of bacterial 16S rRNA gene fragments from the captured nucleic acids was performed by using 5 µl of the resuspended beads for PCR performed by using the 616V-1492R primer pair and the protocols described above.
Cloning, sequencing, and phylogeny inference.
Prior to cloning, the PCR amplification products were purified by low-melting-point agarose (1.5%) gel electrophoresis (NuSieve 3:1; FMC Bioproducts, Biozym Diagnostics GmbH, Oldendorf, Germany) and stained in a SYBR Green I solution (10 µl of 1,0000x SYBR Green I stain in 100 µl of TAE buffer [40 mM Tris, 10 mM sodium acetate, 1 mM EDTA; pH 8.0]; Biozym Diagnostics GmbH) for 45 min. Bands of the expected size were excised from the agarose gel with a glass capillary and melted with 50 µl of double-distilled water for 10 min at 80°C. Four microliters of each solution was ligated as recommended by the manufacturer into the cloning vector pCR2.1 supplied with a TOPO TA cloning kit (Invitrogen Corp., San Diego, Calif.). Nucleotide sequences were determined by the dideoxynucleotide method (57) as described by Purkhold et al. (51). The new 16S rRNA sequences were added to an alignment of about 16,000 small-subunit rRNA sequences by using the alignment tool of the ARB program package (O. Strunk and W. Ludwig, http://www.arb-home.de). Alignments were refined by visual inspection. Phylogenetic analyses were performed by using distance matrix, maximum-parsimony, and maximum-likelihood methods and the appropriate tools of the ARB program package and the fastDNAml program (34). The compositions of the data sets varied with respect to the reference sequences and the alignment positions included. Variability in the individual alignment positions was determined by using the appropriate tool of the ARB package and was used as a criterion to remove or include variable positions for phylogenetic analyses. Phylogenetic consensus trees were drawn by following the recommendations of Ludwig et al. (40). The new dsrAB sequences were translated into amino acids and added to an alignment of 62 DsrAB sequences of SRPs (18, 28). Phylogenetic analyses were performed by using the procedures described by Klein et al. (28).
Nucleotide sequence accession numbers.
The sequences determined in this study are available in the GenBank database under accession numbers AY083010 to AY083027 (16S rRNA gene clones) and AY083028 to AY083029 (dsrAB gene clones). The dsrAB gene sequence of Desulfomicrobium orale DSM 12838T has been deposited under accession number AY083030.

RESULTS
SRP phylogeny.
As the basis for development of the SRP-PhyloChip, a thorough
reevaluation of the phylogeny of SRPs was performed. All 16S
rRNA sequences of SRPs which are available in public databases
(as of October 2001) were collected, aligned, and analyzed phylogenetically
by using maximum-parsimony, maximum-likelihood, and neighbor-joining
methods. Figures
1 and
2 illustrate the phylogeny of the delta-proteobacterial
SRPs. Figure
3 shows the phylogeny of SRPs affiliated with the
Firmicutes,
Nitrospira,
Thermodesulfobacteria, and
Euryarchaeota phyla (phylum names according to the taxonomic outline in the
second edition of
Bergey's Manual of Systematic Bacteriology,
2nd ed. [
21]).
Probe design.
Initially, the specificities of previously described probes
and primers for SRPs (
2,
8,
9,
13,
20,
25,
41,
52,
55,
59,
68)
were reevaluated with the current 16S rRNA data set containing
more than 16,000 entries. Based on this analysis, 26 probes
were considered to be suitable for inclusion on the SRP-PhyloChip
(Table
3). These probes were, if necessary, adjusted to a length
of 18 nucleotides (not including the T-spacer). Twenty-four
of these probes exclusively target SRPs. Probes SRB385 (
2) and
SRB385Db (
52) were included on the chip because they have been
widely used in previous SRP research (
3,
16,
36,
49,
58,
71),
although both of these probes target a considerable number of
phylogenetically diverse non-SRPs. In addition, we significantly
extended the SRP probe set by designing 102 probes targeting
monophyletic groups of SRPs (Fig.
1 to
3 and Table
3). These
probes were designed to have a minimum G+C content of 50%, a
length of 18 nucleotides (not including the T-spacer), and as
many centrally located mismatches with the target sites on 16S
rRNA genes of nontarget organisms as possible. Several of these
probes target the same SRPs, complementing several unique regions
of the 16S rRNA gene, while others exhibit hierarchical specificity.
For example, the genus
Desulfotalea is specifically detected
by five probes and is also targeted by three probes with broader
specificities (Fig.
1 and Table
3). Altogether, all 134 recognized
SRPs for which 16S rRNA sequences have been published are covered
by the probe set which we developed. The probes were spotted
onto glass slides by using a pattern roughly reflecting the
phylogeny of the SRPs (Table
3). In addition, universal, bacterial,
and archaeal probes, as well as a nonsense probe (NONSENSE,
with a sequence having at least four mismatches with every known
16S rRNA sequence), were immobilized on the microarray for hybridization
control purposes (Table
3). Furthermore, another nonsense probe
(CONT) (Table
3) was spotted at the beginning and end of each
probe row of the microarray. During hybridization, a fluorescently
labeled oligonucleotide fully complementary to this probe was
added for control of hybridization efficiency and for straightforward
localization of the probe spot rows in the microarray readout.
Evaluation of the SRP-PhyloChip with pure cultures.
In the first step, the SRP-PhyloChip was hybridized with fluorescently labeled 16S rRNA gene amplificates of Desulfovibrio halophilus, Desulfomicrobium aspheronum, and Desulfohalobium retbaense under increasingly stringent conditions. For each data point, a separate microarray with nine replicate spots of each probe was hybridized, washed, and analyzed. Figure 4 shows representative melting curves of probe-target duplexes for two of the SRP-specific probes and for bacterial probe EUB338 with the labeled 16S rRNA gene amplificates of the three reference organisms. Positive hybridization signals were recorded with probe EUB338 for the three SRPs when wash temperatures between 42 and 60°C were used. However, the EUB338 hybridization signal intensities varied significantly for the three reference organisms, indicating that there were variations in the efficiency of the fluorescence labeling of the PCR amplificates (Fig. 4C). Clear discrimination between perfectly matched and mismatched duplexes was achieved for most but not all of the probes investigated (Fig. 4A and B and 5). When a wash temperature of 42°C was used, the fluorescence intensity of probe-target hybrids with mismatches was almost always lower than the fluorescence intensity of completely matched hybrids (Fig. 5A). Unexpectedly, the difference in signal intensity between completely matched and mismatched duplexes was not significantly increased by gradually increasing the wash temperature to 80°C (Fig. 5). Based on the recorded melting curves, a wash temperature of 55°C was selected for all further experiments.
In the next step, an SRP-PhyloChip with duplicate spots for
each probe was evaluated by using 41 SRP reference organisms.
For each SRP-specific probe, this set of reference organisms
contained an SRP which has a 16S rRNA gene with a perfectly
matched target site. For each reference organism, fluorescently
labeled, PCR-amplified 16S rRNA gene fragments were hybridized
separately with the microarray by using 55°C as the wash
temperature. The array readout was quantitatively analyzed by
digital image analysis to determine a signal-to-noise ratio
for each probe according to the following formula:
where
T is the signal-to-noise ratio of the probe,
IP is the mean pixel intensity of both specific probe spots,
IN is the mean pixel intensity of both NONSENSE probe spots
(note that
IN -
INLB must always have a lower value than
IP),
INLB is the mean pixel intensity of the local background area
around both NONSENSE probe spots, and
IPLB is the mean pixel
intensity of the local background area around both specific
probe spots.
Spots for which the signal-to-noise ratio was equal to or greater than 2.0 were considered positive in the pure-culture evaluation experiments and all subsequent analyses. Furthermore, the signal-to-noise ratio of each probe was divided by the signal-to-noise ratio of the bacterial EUB338 probe recorded on the same microarray in order to compare the duplex yields of the different SRP-specific probes. To do this, the following formula was used:
where
R is the normalized signal-to-noise ratio
of the probe,
IEUB is the mean pixel intensity of all EUB338
probe spots, and
IEUBLB is the mean pixel intensity of the local
background area around all EUB338 probe spots.
The normalized signal-to-noise ratios of the probes ranged from 0.3 for probe DFACE1028 with Desulfotomaculum acetoxidans to 16.9 for probe DSBAC355 with Desulfobacula toluolica, demonstrating that different probes exhibit very different signal intensities after hybridization with their perfectly matched target sequences.
The individual hybridization results for each of the 132 probes with each of the reference organisms can be downloaded from our website (http://www.microbial-ecology.de/srpphylochip/). Six of the probes evaluated (listed separately in Table 3) did not show a positive hybridization signal with any of the reference organisms, including the perfect-match target SRP, and thus were excluded from the microarray in subsequent experiments. In addition, four probes (listed separately in Table 3) were found to be not suitable for SRP diversity surveys due to their nonspecific binding to many nontarget organisms under stringent hybridization conditions (see supplementary web material). Under the conditions used, 75 (59%) of the probes found to be suitable for the SRP-PhyloChip hybridized exclusively to their target organisms. The other probes hybridized to rRNA gene amplificates with perfectly matched target sites, as well as to some rRNA genes with target sites having between one and six mismatches. In summary, of the 5,248 individual probe-target hybridization reactions performed (by hybridizing the 41 reference organisms with the final SRP-PhyloChip), 5,050 (96%) gave the expected results by either showing a detectable signal with the appropriate perfect-match target or showing no signal with target sequences containing mismatches.
Subsequently, the SRP-PhyloChip was hybridized in independent experiments with different amounts (1, 5, 10, 25, 50, 100, 200, and 400 ng) of PCR-amplified, labeled 16S rRNA gene fragments of Desulfovibrio halophilus. The same hybridization pattern was observed when 50 to 400 ng of labeled nucleic acids was used. When less than 50 ng of added nucleic acid was used, the signal-to-noise ratios of the hybridization signals were less than 2.0.
SRP-PhyloChip analyses of complex samples.
To evaluate the applicability of the SRP-PhyloChip for medical and environmental studies, two different samples, both containing diverse microbial communities, were analyzed. In the first experiment, tooth pocket samples from five patients suffering from adult periodontitis were investigated. While for three of the patients none of the SRP-specific probes showed a positive signal (data not shown), probe hybridization patterns indicative of the presence of members of the genus Desulfomicrobium were obtained for the other two patients (Fig. 6A). This result was confirmed independently by PCR analysis of the DNA obtained from the tooth pockets of the five patients by using primers specific for the 16S rRNA gene of members of the genus Desulfomicrobium (Table 2). Consistent with the microarray results, specific PCR amplificates were obtained for two of the five patients. Amplificates from both of these patients were cloned and sequenced. Comparative analysis of six clones demonstrated that the amplified sequences were almost identical to each other and to the corresponding 16S rRNA gene fragment of Desulfomicrobium orale (99.6 to 99.9% sequence similarity) (Fig. 6B). Furthermore, the compositions of the SRP communities in the tooth pockets of the patients were analyzed by using the genes encoding the dissimilatory (bi)sulfite reductase as a marker (28, 76). Approximately 1.9-kb dsrAB fragments could be PCR amplified from two of the five patients, and these fragments were cloned and sequenced. All 19 clones analyzed (6 clones from patient 1 and 13 clones from patient 4) had sequences almost identical to each other and to the dsrAB sequence of Desulfomicrobium orale (99.2 to 99.7% amino acid identity), which was also determined in this study.
In the second experiment, the SRP-PhyloChip was used to investigate
the SRP community in the chemocline of a hypersaline cyanobacterial
mat from Solar Lake. The SRP-PhyloChip hybridization patterns
of fluorescently labeled 16S rRNA gene PCR amplificates obtained
from the chemocline were more complex than those obtained from
the tooth pockets (Fig.
7A). The probe hybridization patterns
indicated that bacteria related to the genera
Desulfonema and
Desulfomonile were present. Furthermore, probe DSB220 showed
signals above the threshold value which could have resulted
from SRPs related to the genus
Desulfofaba. However, the signal
of probe DSB674, which also targets this genus, was below the
threshold value. To confirm these results, 16S rRNA gene PCRs
specific for most members of the "
Desulfobacterales" (including
the genera
Desulfonema and
Desulfofaba) and the "
Syntrophobacterales"
(primers DSBAC355F and 1492R [Table
2]), as well as for some
Desulfonema species (primers DSN61F and DSN+1201R [Table
2]),
were performed. Cloning and sequencing of the PCR amplificates
confirmed that
Desulfonema- and
Desulfomonile-related organisms
were present in the mat chemocline (Fig.
7B). In contrast to
the microarray results, no sequences affiliated with the genus
Desulfofaba were retrieved. In addition, we used glass beads
coated with probe DSN658 to enrich
Desulfonema-related 16S rRNA
gene sequences from bacterial 16S rRNA gene amplificates from
the mat chemocline. After enrichment, reamplification, and cloning,
1 of 12 cloned sequences did indeed possess the target site
of probe DSN658 and was identical to
Desulfonema-related sequences
obtained by the specific PCR assay described above (Fig.
7B).
The remaining 11 cloned sequences did not possess the probe
DSN658 target site and were unrelated to recognized SRPs (data
not shown).
Software-assisted interpretation of microarray readouts.
Interpretation of experiments performed with the SRP-PhyloChip
requires translation of more or less complex probe hybridization
patterns into a list of SRPs which might be present in the sample
analyzed. In principle, this task can be performed manually
by using Table
3 and Fig.
1 to
3 as guides, but this procedure
is tedious and sometimes not straightforward when it is performed
with complex hybridization patterns. Consequently, we developed
a software tool termed ChipChecker, which, after the microarray
readout file (output from the ImaGene software) is imported,
automatically creates a list of SRPs that potential occur in
a sample. To do this, the software determines for each hybridization
experiment which probes were positive (signal-to-noise ratio
greater than the threshold; default signal-to-noise ratio,

2.0)
and compares this result automatically with a list which specifies
for each recognized SRP all fully complementary probes. Only
those SRPs for which all perfect-match probes show a positive
signal are listed. The ChipChecker software can easily be adapted
for interpretation of other DNA microarrays and is available
together with additional information for free download (
http://www.bode.cs.tum.edu/
meierh/download_chipchecker.html).

DISCUSSION
Microarray design and hybridization strategy.
In this study an encompassing DNA microarray for analysis of
SRP diversity in complex samples was developed and evaluated.
A total of 132 previously described and newly designed probes
for the detection of 16S rRNA genes of SRPs were immobilized
on the microarray. Consistent with design formats used in previous
microarray applications for identification of other bacterial
groups (
23,
37), a hierarchical set of oligonucleotides complementary
to the 16S rRNA genes of the target microorganisms at multiple
levels of specificity was developed. However, the number of
16S rRNA-targeted oligonucleotide probes used in this study
is significantly higher than the numbers of probes used in previous
applications of chips for bacterial identification (
23,
37,
62). This difference had important implications for the strategy
which we selected for optimizing the hybridization conditions
to ensure maximum specificity of the probes. Initially, temperature-dependent
dissociation of several probe-target duplexes with perfect matches
or mismatches was measured by using labeled 16S rRNA gene amplificates
of three SRP reference organisms (Fig.
4 and
5). Comparable
dissociation temperatures between 58 and 62°C, at which
50% of the starting duplexes remained intact, were observed
for the different duplexes. This congruence probably reflects
the fact that all probes of the SRP-PhyloChip are the same length
(18 nucleotides) and the fact that the wash buffer contained
3 M tetramethylammonium chloride to equalize A · T and
G · C base pair stability (
42). Because our setup did
not allow us to determine nonequilibrium online melting curves
(
37), it was not feasible (due to the high number of probes
used) to record melting curves for each probe with perfectly
matched and suitably mismatched target nucleic acids. Based
on the recorded melting curves of selected probes, a wash temperature
of 55°C was chosen for all further experiments as the best
compromise between signal intensity and stringency. A further
increase in stringency significantly reduced the signal intensity
of some probes after hybridization with the perfectly matched
target molecules (Fig.
5A) and thus decreased the sensitivity
of the microarray.
Evaluation of the SRP-PhyloChip with more than 40 SRP reference strains was used to determine a threshold value above which a probe hybridization signal was considered positive. In addition, for each probe the signal intensity after hybridization with a perfectly matched target was compared to the signal intensity of the EUB338 probe on the same microarray (normalized signal-to-noise ratio). Consistent with data from quantitative fluorescence in situ hybridization experiments performed with different 16S rRNA-targeted oligonucleotide probes for Escherichia coli (19), (i) some of the probes used in the first version of the SRP-PhyloChip did not hybridize to their perfect-match targets and (ii) the signal intensities measured for the other probes on the SRP-PhyloChip varied significantly, by factors of up to 56. Dramatic differences in duplex yield arising from different regions of the target were also observed in other microarray applications (45, 64) and probably reflect either accessibility differences for the different probe target sites due to secondary structures of the target DNA or different steric hindrances of the different nucleic acid hybrids formed on the microarrays after hybridization.
The evaluation of the microarray with SRP pure cultures demonstrated (i) that false-negative hybridization never occurred (within the detection limit of the microarray method) but (ii) that some of the probes still hybridized to nontarget organisms under the hybridization and washing conditions used, leading to false-positive results (see supplementary web material). As expected, the nucleotide composition of the mismatch, the mismatch position (67, 73), and possibly other variables, such as the influence of an adjacent nucleotide stacking interaction (17), were the major factors determining the duplex yields of probes with mismatched target nucleic acids. Most of the mismatched duplexes with signal intensities above the threshold value (used to differentiate between positive and negative hybridization results) had a signal intensity (and normalized signal-to-noise ratio) lower than that of the corresponding perfect-match duplex (Fig. 5). However, this difference cannot be exploited for interpretation of microarray hybridization results for environmental samples because a low hybridization signal of a probe can be caused not only by mismatched duplex formation but also by low abundance of the perfect-match target nucleic acid.
Misinterpretation of microarray hybridization patterns caused by the nonperfect specificity of some of the probes could be avoided at least partially by using the multiple-probe concept. While hybridization patterns consistent with the hierarchical or parallel specificity of the probes increase the reliability of detection, inconsistent probe hybridization patterns must be interpreted with caution. In complex samples, inconsistent hybridization patterns can be caused either by nonspecific binding of one or several probes or by previously unrecognized prokaryotes with unusual combinations of perfect-match probe target sites in their 16S rRNA gene sequences.
Microarray-based SRP diversity surveys of complex samples.
In this study, periodontal tooth pocket material and a cyanobacterial microbial mat were used to demonstrate the suitability of using the microarray developed for SRP diversity analysis of medical and environmental samples. For the tooth pocket material of two patients suffering from adult periodontitis the SRP-PhyloChip hybridization pattern indicated the presence of members of the genus Desulfomicrobium. Colonization of the tooth pockets analyzed by these SRPs, which is consistent with a previous report of isolation of Desulfomicrobium orale from periodontal tooth pockets (33), was independently confirmed by retrieval of 16S rRNA and dsrAB gene sequences of Desulfomicrobium orale, demonstrating the reliability of the microarray results.
The microarray hybridization patterns obtained by reverse hybridization of 16S rRNA gene fragments amplified from the chemocline of a Solar Lake microbial mat suggested that several phylogenetically different SRPs, including bacteria related to the genera Desulfonema, Desulfomonile, and Desulfofaba, were present. By using specific PCR assays, 16S rRNA gene sequences related to sequences of members of the genera Desulfonema and Desulfomonile were obtained from the mat material analyzed, while the presence of Desulfofaba-like organisms could not be confirmed. The failure to detect Desulfofaba-like bacteria with the PCR assay might mean that a relatively limited number of 16S rRNA gene clones was sequenced or that the microarray hybridization pattern indicative of Desulfofaba was caused by the presence of bacteria that have not been recognized yet. The detection of Desulfonema-like bacteria in the chemocline of the Solar Lake mat is consistent with findings of previous studies (46, 47, 70) and further supports the importance of these SRPs in hypersaline mat ecosystems.
In conclusion, we developed an encompassing 16S rRNA gene-targeting oligonucleotide microarray suitable for SRP diversity analyses of complex environmental and clinical samples. The microarray was used to screen samples in order to rapidly obtain indications of the presence of distinct lineages of SRPs. Subsequently, this information was used to select appropriate PCR-based techniques for confirmation of the microarray results and for retrieval of sequence information for phylogenetic analysis. In contrast to previously available tools for cultivation-independent SRP identification (13, 18, 41, 56, 75, 76), the SRP-PhyloChip allowed us to obtain a phylogenetically informative, high-resolution fingerprint of the SRP diversity in a given sample within 48 h (including all experimental work from DNA extraction to hybridization pattern interpretation). However, keeping in mind that (i) most environmental microbial communities contain a high percentage of bacteria not yet sequenced on the 16S rRNA level and (ii) not all probes on the microarray are absolutely specific under the conditions used, the SRP-PhyloChip experiments should always be supplemented with microarray-independent techniques to confirm the phylogenetic affiliations of the SRPs detected. Furthermore, it should be noted that the microarray approach described here did not allow us to obtain quantitative data on the compositions of SRP communities because of the recognized biases introduced by using PCR for 16S rRNA gene amplification (74). In addition, the duplex yield of a probe on the microarray is dependent not only on the actual abundance of its perfect-match target nucleic acid in the PCR amplificate mixture but also on a variety of other factors, including the labeling efficiency of the specific target nucleic acid, the secondary structure of the target region, and the inherent variations associated with microarray fabrication. Despite these limitations, the microarray which we developed has great potential for rapid screening of SRP diversity in complex samples. The SRP diversity microarray fingerprint technique should allow workers to identify the probes which have relevance for further characterization of a sample by PCR or quantitative hybridization experiments. This option should be particularly valuable if large numbers of samples are to be analyzed to study temporal or spatial variations in SRP diversity.

ACKNOWLEDGMENTS
Yehuda Cohen is acknowledged for kindly providing cyanobacterial
mat material from Solar Lake. The excellent technical assistance
of Claudia Schulz, Helga Gaenge, Susanne Thiemann, and Sibylle
Schadhauser is acknowledged. We also thank Bernhard Loy for
providing the tooth pocket samples and Josef Reischenbeck for
fabrication of hybridization chambers.
This research was supported by grants from bmb+f (01 LC 0021 subproject 2, in the framework of the BIOLOG program) (to M.W.), DFG (trilateral cyanobacterial mat project RU458/18-4) (to M.W.), and Bayerischen Forschungsstiftung (Development of Oligonucleotide DNA Chips, in cooperation with MWG Biotech; project 368/99) (to M.W. and K.-H.S.).

FOOTNOTES
* Corresponding author. Mailing address: Lehrstuhl für Mikrobiologie, Technische Universität München, Am Hochanger 4, D-85350 Freising, Germany. Phone: 49 8161 71 5444. Fax: 49 8161 71 5475. E-mail:
wagner{at}microbial-ecology.de.


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Applied and Environmental Microbiology, October 2002, p. 5064-5081, Vol. 68, No. 10
0099-2240/02/$04.00+0 DOI: 10.1128/AEM.68.10.5064-5081.2002
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