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Applied and Environmental Microbiology, February 2005, p. 993-1003, Vol. 71, No. 2
0099-2240/05/$08.00+0 doi:10.1128/AEM.71.2.993-1003.2005
Copyright © 2005, American Society for Microbiology. All Rights Reserved.
Assessment of Genotypic Diversity of Antibiotic-Producing Pseudomonas Species in the Rhizosphere by Denaturing Gradient Gel Electrophoresis
M. Bergsma-Vlami,1
M. E. Prins,1
M. Staats,1 and
J. M. Raaijmakers1*
Laboratory of Phytopathology, Wageningen University, Wageningen, The Netherlands1
Received 6 July 2004/
Accepted 13 September 2004

ABSTRACT
The genotypic diversity of antibiotic-producing
Pseudomonas spp. provides an enormous resource for identifying strains that
are highly rhizosphere competent and superior for biological
control of plant diseases. In this study, a simple and rapid
method was developed to determine the presence and genotypic
diversity of 2,4-diacetylphloroglucinol (DAPG)-producing
Pseudomonas strains in rhizosphere samples. Denaturing gradient gel electrophoresis
(DGGE) of 350-bp fragments of
phlD, a key gene involved in DAPG
biosynthesis, allowed discrimination between genotypically different
phlD+ reference strains and indigenous isolates. DGGE analysis
of the
phlD fragments provided a level of discrimination between
phlD+ genotypes that was higher than the level obtained by currently
used techniques and enabled detection of specific
phlD+ genotypes
directly in rhizosphere samples with a detection limit of approximately
5
x 10
3 CFU/g of root. DGGE also allowed simultaneous detection
of multiple
phlD+ genotypes present in mixtures in rhizosphere
samples. DGGE analysis of 184 indigenous
phlD+ isolates obtained
from the rhizospheres of wheat, sugar beet, and potato plants
resulted in the identification of seven
phlD+ genotypes, five
of which were not described previously based on sequence and
phylogenetic analyses. Subsequent bioassays demonstrated that
eight genotypically different
phlD+ genotypes differed substantially
in the ability to colonize the rhizosphere of sugar beet seedlings.
Collectively, these results demonstrated that DGGE analysis
of the
phlD gene allows identification of new genotypic groups
of specific antibiotic-producing
Pseudomonas with different
abilities to colonize the rhizosphere of sugar beet seedlings.

INTRODUCTION
Antibiotic compounds produced by fluorescent
Pseudomonas strains
play key roles in the suppression of various soilborne plant
pathogens (
41,
47,
52). 2,4-Diacetylphloroglucinol (DAPG) produced
by
Pseudomonas fluorescens has activity against a range of plant
pathogens, including bacteria, fungi, and nematodes (reviewed
in reference
41). Recently, the broad-spectrum activity of DAPG
also has drawn attention in the medical area because of the
bacteriolytic activity of DAPG against multidrug-resistant
Staphylococcus aureus (
18). DAPG-producing
Pseudomonas spp. have been isolated
from the rhizospheres of different crops grown in soils from
diverse geographic regions (
19), and they are predominant constituents
of the rhizosphere of wheat plants grown in soils that naturally
suppress take-all disease (
4,
30,
39,
58). They also have been
isolated from soils that naturally suppress black root rot of
tobacco (
19,
43) or
Fusarium wilt disease (
23).
Multiple genes are involved in biosynthesis and regulation of DAPG production in P. fluorescens (reviewed in reference 12). One of these genes, the polyketide synthase gene phlD, is essential for synthesis of the DAPG precursor monoacetylphloroglucinol (1). It has been well documented that the phlD gene is conserved among DAPG-producing Pseudomonas strains found worldwide (19, 39) but displays a certain degree of polymorphism (23, 28, 42). Given that the genotypic diversity among DAPG-producing Pseudomonas strains provides an enormous resource for identifying strains that are highly rhizosphere competent and superior for biological control of plant diseases (40, 47), the sequence heterogeneity of the phlD gene is now routinely used to assess the diversity of this group of antagonistic bacteria (24, 28, 31, 42, 56). A range of other methods have been used to determine the genotypic diversity of DAPG-producing Pseudomonas strains; these methods include amplified ribosomal DNA restriction analysis (19, 37), random amplified polymorphic DNA (RAPD) analysis (28, 40), and BOX-PCR (31). A notable difficulty with all of these methods is the requirement for isolation and cultivation of phlD+ pseudomonads from soil and rhizosphere environments prior to genotypic characterization of the organisms. Isolation of phlD+ pseudomonads can be achieved by plating on semiselective media, followed by colony hybridization (39), a time-consuming method. Alternatively, direct characterization of phlD+ Pseudomonas isolates in rhizosphere samples can be performed by a rapid PCR assay (32). However, this method also requires cultivation of a rhizosphere sample in semiselective nutrient broth prior to characterization of the phlD+ genotype and may be biased toward detecting the most predominant genotype.
The aim of this work was to develop a simple and rapid method to study the presence and genotypic diversity of phlD+ Pseudomonas strains directly in rhizosphere samples without prior isolation or enrichment on nutrient media. New phlD-specific primers were developed, and their specificity was tested with a range of different phlD+ genotypes, alone and in mixtures. Polymorphisms within the amplified 350-bp phlD fragments were assessed by denaturing gradient gel electrophoresis (DGGE) analysis, sequencing, and phylogenetic analysis. The specificity and resolving capacity of the PCR-DGGE system were compared to the specificity and resolving capacity of currently used techniques, including phlD restriction fragment length polymorphism (RFLP) (31), RAPD analysis (19), and the rapid PCR assay (32). Finally, the biological significance of the newly developed PCR-DGGE classification was tested in root colonization assays with sugar beet seedlings treated with eight genotypically different phlD+ genotypes of Pseudomonas.

MATERIALS AND METHODS
Pseudomonas strains and culture conditions.
All
Pseudomonas strains used in this study were cultured on
King's medium B (KMB) agar (
20) at 25°C for 48 h. To determine
the specificity and resolving capacity of the PCR-DGGE method
developed in this study, we tested multiple
phlD+ reference
strains (Table
1), as well as 184 indigenous
phlD+ Pseudomonas isolates obtained from the rhizospheres of three plant species
(wheat, sugar beet, and potato) by colony hybridization with
a
phlD-specific probe.
PCR-DGGE analysis.
PCR amplification was carried out in a 25-µl reaction
mixture which contained 3 µl of a 40-fold-diluted heat-lysed
cell suspension (
39), 1
x GeneAmp PCR buffer (Perkin-Elmer Corp.,
Norwalk, Conn.), each deoxynucleoside triphosphate (Promega)
at a concentration of 500 µM, 40 pmol of the reverse primer,
40 pmol of the forward primer (Amersham Pharmacia Biotech),
1.5 mM MgCl
2, and 1.0 U of AmpliTaq DNA polymerase (Perkin-Elmer).
The PCR program consisted of an initial denaturation at 94°C
for 3 min, followed by 30 cycles of 94°C for 30 s, 67°C
for 30 s, and 72°C for 60 s. The reactions were performed
by using a Peltier Thermal Cycler-200 (Biozym, Landgraaf, The
Netherlands). Fifteen microliters of the PCR product was used
for analysis by DGGE with the Dcode universal mutation detection
system (Bio-Rad Laboratories, Hercules, Calif.). The DGGE analysis
protocol was based on the initial protocol of Muyzer et al.
(
35) and was performed by using an 8% (wt/vol) acrylamide gel
with a linear denaturing gradient (100% denaturant contained
7 M urea plus 40% [vol/vol] deionized formamide). In almost
all cases a gradient from 32% denaturant at the top to 41% denaturant
at the bottom gave optimal separation of the amplified products,
and this gradient was routinely used. Gels were run for 10 min
at 200 V and subsequently for 16 h at 85 V (60°C), stained
with ethidium bromide (0.5 µg/ml in 1
x Tris-acetate-EDTA
[TAE] [pH 8.3]) for 30 min, and visualized on an UV transilluminator.
DNA sequence analysis.
phlD fragments from multiple representative strains were amplified by using the Expand High Fidelity Taq polymerase (Roche, Almere, The Netherlands) and were subsequently sequenced by BaseClear (Leiden, The Netherlands). Alignment of phlD sequences obtained in this study and phlD sequences present in the databases was performed with Clustal W (53). Distance matrices were computed with MEGA, and phylogenetic trees were constructed by using the neighbor-joining method (44); the topology was checked by bootstrap analysis (1,000 data sets).
RFLP and RAPD analyses.
To determine the resolving capacity of the classifications assessed by PCR-DGGE analysis, multiple phlD+ strains were also subjected to phlD RFLP and RAPD analyses, two techniques that are currently used to determine the genotypic diversity of DAPG-producing Pseudomonas spp. For the phlD RFLP analysis, 629-bp fragments of the phlD gene were amplified with primers B2BF and BPR4, and this was followed by restriction with HaeIII, MspI, or TaqI (32). Restriction fragments were separated on a 2% agarose gel in 1x TAE for 2 to 3 h at 120 V. RAPD analysis with the 10-mer primers M12, M13 and D7 was performed according to protocols described previously (19, 40). The amplification products were separated on a 2% agarose gel in 1x TAE at 120 V for 3 h. phlD RFLP patterns and RAPD markers were visualized with a UV transilluminator and were photographed by using a digital camera. All PCR-RAPD amplifications were repeated at least two times, and only the consistent RAPD markers were included in the evaluation. The sizes of the restriction fragments obtained in the phlD RFLP analysis and the RAPD markers were determined with the Phoretix 1D software (version 3.0; Phoretix International, Newcastle, England). Band positions were converted to Rf values (0 and 1), and profile similarities were calculated by determining the pairwise coefficients of similarity (Nei-Li distances) for the total number of lane patterns. Cluster analysis with neighbor joining (44) and the corresponding bootstrap analysis (1,000 data sets) were performed with the Treecon software (version 1.3b) for Windows (54).
Plant cultivation and DNA extraction from the rhizosphere.
Wheat plants (Triticum aestivum L. cv. Bussard) were grown in a soil consisting of agricultural CB soil (4) mixed at a 1:1 ratio (wt/wt) with quartz sand. Sixteen wheat seeds were sown in square polyvinyl chloride pots containing 250 g (dry weight) of soil. A spontaneous rifampin-resistant derivative of phlD+ Pseudomonas isolate PWB532, representing DGGE group E, was introduced into soil at densities of 0, 10, 102, 103, 104, and 106 cells/g with an initial water content of 20% (vol/wt). One additional control treatment consisted of soil that was autoclaved twice (with 24 h between the two autoclave runs) to eliminate putative indigenous phlD+ isolates. Each treatment consisted of three replicates. After 10 to 12 days of cultivation in a growth chamber at 20°C with a 16-h photoperiod, the wheat plants were harvested, and rhizosphere samples were prepared for (i) enumeration of the introduced strain on selective agar plates and (ii) direct DNA extraction, followed by PCR-DGGE analysis. For enumeration of the introduced strain, 0.5 g of roots with associated rhizosphere soil was suspended in 5.0 ml of sterile distilled water and shaken vigorously for 1 min on a Vortex mixer; samples were subsequently sonicated in an ultrasonic cleaner for 1 min and dilution plated onto KMB agar supplemented with delvocid (100 mg/liter), chloramphenicol (13 mg/liter), ampicillin (40 mg/liter), and rifampin (100 mg/liter) (48). The plates were incubated for 3 days at 25°C, and colonies were enumerated. For direct DNA extraction from the rhizosphere, 0.5 g of roots with associated rhizosphere soil was suspended in 1.0 ml of saline phosphate buffer, shaken vigorously for 1 min on a Vortex mixer, and sonicated in an ultrasonic cleaner for 1 min. The roots were discarded, and the suspension was centrifuged for 1 min at 10,000 rpm (19,000 x g). An additional 0.5 g of rhizosphere soil that had been subjected to the same treatment was added, and the sample was subsequently processed by bead beating (three times for 90 s each). Cells were lysed by using the protocol of a FastDNA SPIN kit for soil (Bio 101). The DNA pellet was dissolved in 50 µl of Tris-EDTA (10 mM Tris, 0.1 mM EDTA; pH 8). PCR amplification of extracted DNA was performed in 50-µl reaction mixtures containing approximately 10 to 50 ng of DNA. In most cases, this amount of DNA was acquired after 100-fold dilution of the DNA obtained with the FastDNA SPIN kit. To enhance the specificity of the PCR, a ramping PCR was carried out as follows: the annealing temperature was initially 60°C, and it was increased to 72°C in steps of 0.1°C. The PCR program consisted of an initial denaturation at 94°C for 3 min, followed by 30 cycles of 94°C for 30 s, 60°C for 30 s, with an increase at a rate of 0.1°C/s up to 72°C, and 72°C for 1 min. PCR amplification was carried out as described above. The primer concentration used was 20 pmol per reaction mixture instead of 40 pmol per reaction mixture.
In addition to wheat, experiments were performed with sugar beet (Beta vulgaris cv. Auris). Twenty-eight sugar beet seeds were sown in small square pots containing 250 g (dry weight) of soil and cultivated in a climate room with a controlled environment at 20°C and a 16-h photoperiod. Genotypically different phlD+ isolates were introduced separately into soil at a density of approximately 104 CFU/g of soil. The phlD+ isolates were spontaneous rifampin-resistant derivatives of isolates PWB233 (DGGE group A), PSC2218 (DGGE group B), PPB2310 (DGGE group C), PSB211 (DGGE group D), PWB532 (DGGE group E), PPB3512 (DGGE group F), PSC415 (DGGE group Z), and Q8R1-96 (DGGE group G). For short-term colonization experiments, the sugar beet plants were harvested after 10 to 12 days of cultivation. For long-term colonization studies, sugar beet plants were grown in the same pots for six successive cycles consisting of 10 to 12 days each. Twice a week, the plants were treated with one-third-strength Hoaglund's solution (macroelements only). After 10 to 12 days of growth, plants were harvested, and their root systems with rhizosphere soil were collected. Excess root material was mixed with the cultivated soil and represented approximately 0.125% (wt/wt) of the soil dry weight. The cultivated soil was subsequently returned to the same pot, and sugar beet seeds were replanted. This process of plant growth and harvesting was repeated for six successive cycles. Four replicates were included per treatment. For both short-term and long-term colonization experiments, rhizosphere samples were plated onto selective media and subjected to direct DNA extraction as described above for the experiments with wheat.
Statistical analysis.
Population densities of the introduced phlD+ fluorescent Pseudomonas strains were log10 transformed prior to statistical analysis. For the colonization assays with sugar beet seedlings, differences in population densities between the introduced strains were analyzed for each successive growth cycle by analysis of variance, followed by Tukey's Studentized range test (SAS Institute Inc., Cary, N.C.).
Nucleotide sequence accession numbers.
phlD sequences obtained in this study have been deposited in the GenBank database under the accession numbers shown in Table 1.

RESULTS AND DISCUSSION
Primer design and specificity.
For detection of DAPG-producing
Pseudomonas spp., a number of
primers directed against sequences in the
phlD gene have been
developed previously (
32,
39). The sizes of the amplification
products of these primers range from approximately 600 to 750
bp, which is relatively large for further analysis by DGGE.
Therefore, two new sets of oligonucleotide primers were developed
for conserved sequences in the
phlD gene of multiple reference
strains (Fig.
1). In both primer sets, the forward primer is
identical (DGGE292for), whereas there is a four-nucleotide difference
between the two different reverse primers (DGGE618rev and 6DGGE618rev).
Additionally, a 40-bp GC clamp is attached at the 5' end of
the forward primer (Table
2). The first primer set resulted
in amplification of fragments of the predicted size (approximately
350 bp) from DNA of four genotypically different
phlD+ reference
strains (PILH1, F113, Q8R1-96, and Q2-87) and from DNA of each
of 184
phlD+ isolates obtained previously from the rhizospheres
of three different plant species. No amplification product was
obtained from DNA of
phlD mutant R1SS101 or from DNA of
phlD+ reference strains CHA0 and Pf-5. At this stage, several attempts
were made to further optimize the first primer set, including
adjustment of the primer concentrations, the annealing temperature
(the temperatures tested ranged from 48 to 70°C), and the
Mg
2+ concentration. However, none of these attempts were successful.
The second primer set resulted in amplification of the predicted
350-bp fragment from DNA of all six
phlD+ reference strains,
including strains CHA0 and Pf-5, and from DNA of each of the
184
phlD+ isolates (Fig.
2). For successful amplification with
the second primer set, a two-step PCR approach was required.
In the first PCR step, no GC clamp was present at the 5' end
of the forward primer. After the first step, the PCR products
were diluted 100- to 1,000-fold, after which the second PCR
step was performed with the forward primer containing the GC
clamp. The PCR programs for the one-step and two-step PCR amplifications
were the same as the program described above.
DGGE analysis.
DGGE and temperature gradient gel electrophoresis are widely
used to study the microbial diversity in environmental samples
and to monitor changes in specific microbial groups or communities
(
7,
10,
11,
22,
35,
45,
55). DGGE allows analysis of a large
number of samples, which is essential for studying spatial and
temporal variations in microbial populations (
14,
33,
34,
35,
36,
51). To date, most primers used in DGGE analysis target
rRNA genes of different microbial genera. In this context, group-specific
primers have been developed for a number of bacterial genera,
including
Pseudomonas and
Bacillus (
10,
11), as well as for
Burkholderia (
45),
Actinomycetes (
15), and ammonium oxidizers
and methanotrophs (
2,
22). Recently, primers targeting specific
biosynthetic genes have been developed, and, when combined with
DGGE fingerprinting, these primers have led to a better level
of discrimination within specific bacterial groups. For example,
primers directed against the
fliC gene allowed specific detection
of the bacterial wilt pathogen
Ralstonia solanacearum in soil
and subsequent discrimination between strains obtained from
various places (
46). Rapid assessment of the diversity of methanogens
was performed by DGGE analysis of the
nifH gene (
25,
57). In
the same line of research, terminal RFLP analysis of PCR-amplified
nifH fragments was shown to be a rapid technique for profiling
diazotrophic microbial communities (
50). Additionally, the community
structures of ammonia-oxidizing bacteria (
17) and bacteria from
the marine environment (
3) were explored by DGGE analysis of
the
amoA and
rpoB genes, respectively.
In the present study, DGGE analysis was performed with the phlD fragments amplified with the first and second primer sets described above. A linear 32 to 41% denaturant gradient allowed detection of the amplified fragments and gave optimal discrimination between genotypically different phlD+ reference strains and isolates, except for strains CHA0 and Pf-5 (Fig. 2A and C). For CHA0 and Pf-5, a 40 to 51% denaturant gradient was required to detect the PCR products amplified with the second primer set (Fig. 2B). Attempts to design a DGGE gradient (32 to 51% denaturant) for all phlD+ strains, including strains CHA0 and Pf-5, resulted in a loss of discrimination between phlD+ genotypes other than those of strains CHA0 and Pf-5. The difference in the behavior of strains CHA0 and Pf-5 compared to other phlD+ strains in both PCR and DGGE is supported by phlD sequence data (see below) and has been described previously for PCR with other phlD primers (32). For strains other than CHA0 and Pf-5, the migration positions of PCR fragments obtained with the first and second primer sets were different, but the DGGE groups of the phlD+ genotypes were the same for both primer sets (data not shown). DGGE analysis of PGNR1, PINR2, and PINL1, three other strains that are also very closely related to CHA0 and Pf-5 (19), showed that their amplified phlD fragments migrated to the same positions as the phlD fragments of strains CHA0 and Pf-5 (Fig. 2B).
DGGE analysis of the 184 phlD+ isolates obtained from the rhizospheres of wheat, sugar beet, and potato resulted in seven DGGE groups, designated DGGE groups A, B, C, D, E, F, and Z (Fig. 2C and Table 3). Several of the 184 phlD+ isolates were assigned to the same DGGE group as reference strains PILH1 (DGGE group A) and Q2-87 (DGGE group B). None of the 184 phlD+ isolates were assigned to DGGE groups containing the reference strains Q8R1-96 (DGGE group G), F113 (DGGE group I), and CHA0 (DGGE group M). Therefore, the isolates assigned to DGGE groups C, D, E, F, and Z may represent phlD+ genotypes not described previously. DGGE group E was the dominant phlD+ genotype found among the collection of 184 indigenous phlD+ isolates, representing approximately 52% of the diversity (Table 3).
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TABLE 3. Genotypic classification of 184 indigenous phlD+ Pseudomonas isolates originating from the rhizospheres of multiple plant species by DGGE and RAPD analyses
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Comparison of PCR-DGGE, RAPD, and phlD RFLP analyses.
To determine the resolving capacity of the classifications obtained
by PCR-DGGE analysis of the
phlD gene, RAPD analysis with three
10-mer primers and
phlD RFLP analysis were performed. The results
of RAPD analysis of the 184 indigenous
phlD+ isolates correlated
well with the results obtained by PCR-DGGE, but there was a
higher degree of discrimination than there was in the PCR-DGGE
analysis (Table
3). RAPD analyses resulted in 12 different RAPD
groups, whereas PCR-DGGE resulted in seven different groups.
Isolates belonging to DGGE group E were assigned to five different
RAPD groups (RAPD groups E1 thru E5), and isolates belonging
to DGGE group A were assigned to two RAPD groups (RAPD groups
A1 and A2). A subset of five
phlD+ reference strains and 12
indigenous
phlD+ isolates, representing the 12 different RAPD
groups, were analyzed by RFLP analysis of a 629-bp
phlD fragment
with three restriction enzymes, a technique routinely used to
determine the genotypic diversity of DAPG-producing
Pseudomonas spp. (
32). Based on the RFLP analysis, the two isolates (isolates
A1 and A2) belonging to DGGE group A were identical to D27B1,
a reference strain representing DGGE genotype A (Table
4). Representative
isolates belonging to DGGE groups D, F, and Z could be distinguished
on the basis of the RFLP analysis. In contrast, however, the
RFLP profiles of reference strain Q8r1-96 (DGGE group G) were
identical to those of all five isolates belonging to DGGE group
E (RAPD groups E1 thru E5). Similarly, the RFLP profiles of
isolates belonging to DGGE groups B and C were identical. These
results indicated that PCR-DGGE provides a higher level of discrimination
between
phlD+ genotypes than the currently used
phlD RFLP analysis.
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TABLE 4. Genotypic classification of 12 indigenous phlD+ Pseudomonas isolates originating from the rhizospheres of multiple plant species and five phlD+ reference Pseudomonas strains by DGGE and phlD RFLP analysesa
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Sequence and phylogenetic analyses.
In general, sequence analyses of the 350-bp
phlD fragments amplified
from DNA of 12 isolates representing the different DGGE genotypes
(genotypes A, B, C, D, E, F, and Z) showed a good correlation
between the G+C contents of the amplified fragments and the
migration patterns in the denaturing gel (Fig.
3). The G+C contents
ranged from 47.95% for DGGE genotype A (located in the upper
part of the 32 to 41% denaturant gradient) to 51.72% for DGGE
genotype I (located at the bottom). The results further showed
that not only the G+C content but also the position of the so-called
melting domains (
34) within the amplified fragment determines
the electrophoretic mobility. The relatively high G+C content
(59.6%) of the
phlD fragments of reference strains CHA0 and
Pf-5 supported the requirement for a gradient with a higher
percentage of denaturant (40 to 51% denaturant), as described
previously.
Phylogenetic analyses of the
phlD sequences obtained in this
study and present in the database (Table
1) revealed a total
of six distinct clusters based on bootstrap values higher than
75% (Fig.
4). Cluster I contained the reference strains Q8R1-96
(DGGE genotype G), Q65c80, and CM1A2, as well as isolates E1
through E5, which were five representatives of DGGE genotype
E. Representative isolates of DGGE genotype B were clustered
together (cluster II) with
phlD+ reference strains F113 (DGGE
genotype I) and MI-96. Cluster III contained only representative
isolates of DGGE genotypes C, D, F, and Z. Isolates A1 and A2,
representing DGGE genotype A, were classified in the same cluster
(cluster IV) together with reference strains PILH1 and PITR2,
both of which were also classified by DGGE analysis as genotype
A. Reference strain Q2-87 (DGGE genotype B) formed a unique
cluster (cluster V) that included the recently described strain
HR3-A13 (PfY) (
29). However, Q2-87 was not grouped close to
PWB134, a strain also classified in DGGE genotype B. These results
are in accordance with results obtained by the RFLP analysis
of strain Q2-87 and isolate PWB134. Cluster VI was the most
distant cluster obtained in the phylogenetic analyses and contained
reference strains CHA0 and Pf-5 (both DGGE genotype M) and the
recently described strain PR3-A52 (PfZ) (
29). Phylogenetic analyses
of the
phlD gene sequences by neighbor joining or maximum likelihood
yielded similar results and tree topologies.
PCR-DGGE of rhizosphere samples.
A notable difficulty of
phlD RFLP and RAPD analyses is the requirement
for isolation and cultivation of
phlD+ Pseudomonas isolates
from soil and rhizosphere environments prior to genotypic characterization
of the organisms. A PCR-DGGE analysis was performed with DNA
extracted from rhizosphere samples obtained from roots of wheat
plants grown for 10 to 12 days in soil treated with a spontaneous
rifampin-resistant derivative of isolate PWB532 (DGGE group
E). Isolate PWB532 was introduced into the soil at initial densities
ranging from 10 to 10
6 CFU/g. Rhizosphere samples were subjected
to direct DNA extraction, followed by PCR-DGGE, and they were
also dilution plated onto KMB supplemented with rifampin for
comparison purposes. Based on dilution plating, the rhizosphere
population densities of introduced isolate PWB532 ranged from
5
x 10
2 to 5
x 10
6 CFU/g of root after 10 to 12 days of cultivation.
PCR with DNA directly extracted from the wheat rhizosphere resulted
in amplification of the 350-bp
phlD fragment when the density
of PWB532 was equal to or higher than 5
x 10
3 CFU/g (fresh weight)
of root. Subsequent DGGE analysis of the 350-bp fragments amplified
from DNA extracted from the rhizosphere of wheat colonized by
isolate PWB532 showed a single band corresponding to DGGE group
E (Fig.
5A). No other DGGE genotypes were detected. Additionally,
no 350-bp amplification products were detected in the control
treatments, which included rhizosphere samples from natural
CB soil and from CB soil autoclaved twice prior to wheat cultivation
(data not shown). The ramping PCR protocol used for DNA extracted
from rhizosphere samples was crucial as it considerably increased
the sensitivity of the PCR amplification. Similar results were
obtained in short-term experiments with sugar beet plants grown
in soils treated with isolates PSC415 (DGGE group Z), Q8R1-96
(DGGE group G), and PPB3512 (DGGE group F) (Fig.
5B). Collectively,
these results indicate that PCR-DGGE can be used to detect specific
phlD+ genotypes directly in rhizosphere samples with a detection
limit of approximately 5
x 10
3 CFU/g of root when ethidium bromide
staining of the gel after electrophoresis is used. For ethidium
bromide-stained gels, a detection limit of 10
5 CFU/g of soil
was reported previously for
R. solanacearum (
46). When the results
were combined with Southern hybridization, however, cell densities
of
R. solanacearum of approximately 10
3 CFU/g of soil could
be detected (
46). The results of the latter study suggest that
the detection limit for indigenous
phlD+ isolates may be increased
further when the technique is combined with Southern hybridization
or when silver staining is used instead of ethidium bromide
staining.
A potential problem for PCR-DGGE analysis of DNA extracted from
environmental samples may be that in mixed populations of
phlD+ isolates, certain
phlD genes are preferentially amplified, leading
to incorrect assessment of all the genotypes present. In the
present study, a mixture of six genotypically different
phlD+ isolates (representatives of DGGE genotypes B, C, E, F, G, and
Z) was introduced into wheat rhizosphere samples to a final
density of approximately 5
x 10
5 CFU/g of root for each isolate
prior to DNA extraction. PCR-DGGE analysis showed that all six
genotypes were detectable in both replicates included. In both
mixed samples, one additional band was detected in the DGGE
gel; this band may have been a heteroduplex between the different
phlD sequence variants, as described previously by Kowalchuk
et al. (
22), or it may have represented another indigenous
phlD+ isolate present in the wheat rhizosphere sample. The latter
possibility was not pursued further. Collectively, these results
indicated that PCR-DGGE analysis of the
phlD gene allows simultaneous
detection of multiple genotypes present in a rhizosphere sample.
In the same experiment, the PCR-DGGE methodology was compared with the currently used rapid PCR-based protocol for rhizosphere samples (32). For the latter rapid PCR-based protocol, different dilutions of the rhizosphere samples required incubation in nutrient broth for 48 h prior to PCR and genotypic characterization. PCR and subsequent genotypic characterization showed that the rapid PCR-based protocol resulted in detection of only DGGE group G (strain Q8r1-96), whereas PCR-DGGE analysis resulted in detection of all six genotypes. In conclusion, these results indicated that cultivation of a rhizosphere sample in nutrient broth prior to genotypic characterization introduces a bias toward detecting either the most dominant genotype or the genotypes with higher growth rates or competitive abilities in the nutrient broth relative to the other genotypes present. This bias is circumvented by direct PCR-DGGE analysis of the phlD gene.
Biological significance of PCR-DGGE classification of phlD+ genotypes.
In order to investigate the biological significance of the additional classifications of phlD+ genotypes obtained by the PCR-DGGE methodology described in this study, the population dynamics of eight isolates representing different DGGE groups were monitored during six successive growth cycles of sugar beet seedlings in soil obtained from an agricultural field (Fig. 6). Each of the eight isolates was introduced only once (growth cycle 0) at an initial density of approximately 5 x 104 CFU/g of soil. After the first sugar beet growth cycle, the densities of strains Q8r1-96 (DGGE genotype G) and PWB233 (DGGE genotype A) were the highest densities; the population densities of strain Q8r1-96 (DGGE genotype G) increased further during growth cycles 2 to 4 to values of approximately 3 x 107 CFU/g of root, whereas the population densities of PWB233 (DGGE genotype A) leveled off at values of approximately 5 x 106 CFU/g of root. After the first growth cycle, strains PWB532 (DGGE genotype E), PPB2310 (DGGE genotype C), and PSC415 (DGGE genotype Z) did not exhibit densities as high as those of strains Q8r1-96 (DGGE genotype G) and PWB233 (DGGE genotype A), but they reached densities similar to those of PWB233 (DGGE genotype A) in growth cycles 2 to 4. After six growth cycles of sugar beet seedlings, the population densities of the genotype A, E, and G strains were significantly similar (P < 0.05). Strains PSB211 (DGGE genotype D), PSC2218 (DGGE genotype B), and PPB3512 (DGGE genotype F) colonized the rhizosphere of sugar beet seedlings to a significantly lesser extent than the strains representing the other five DGGE genotypes. The population densities of the three strains (DGGE groups D, B, and F) did not increase above 105 CFU/g of root but instead declined in the last sugar beet growth cycle to values of 104 CFU/g of root (DGGE group D), 8 x 103 CFU/g of root (DGGE group B), and 4 x 103 CFU/g of root (DGGE group F) (Fig. 6).
These results showed that there were considerable differences
in the abilities of different
phlD+ genotypes to colonize the
rhizosphere of sugar beet seedlings, confirming and extending
results obtained in previous studies (
24,
40). Strain Q8r1-96,
representing DGGE genotype G, was shown to be superior for colonization
of the sugar beet rhizosphere, especially in the first four
growth cycles. Similar observations were described previously
for wheat (
40) and pea (
24). These results indicate that the
ability of strain Q8r1-96 to rapidly establish and maintain
high population densities in the rhizosphere is not linked to
a specific plant species but may be due to specific characteristics
that enable this strain to be competitive in different rhizosphere
environments. In this context, Mavrodi et al. (
27) recently
identified possible new traits by subtractive hybridization
that may contribute to the superior rhizosphere competence of
strain Q8R1-96. These traits include bacteriocin production,
a trait that may be advantageous in intraspecific competition
with other indigenous pseudomonads. Although strain Q8r1-96
(DGGE genotype G) could not be distinguished from strain PWB532
(DGGE genotype E) on the basis of
phlD RFLP analysis, these
organisms differed considerably in the ability to colonize the
rhizosphere of sugar beet seedlings. Similarly, strains PPB2310
(DGGE genotype C) and PSC2218 (DGGE genotype B), which could
not be distinguished by
phlD RFLP analysis, differed significantly
in the ability to colonize the sugar beet rhizosphere. These
results highlight the conclusion that the additional classification
of this widely distributed group of antibiotic-producing
Pseudomonas spp. by PCR-DGGE analysis of the
phlD gene also provides biologically
relevant discrimination. Given the level of polymorphism in
specific genes involved in the regulation (
gacA) (
6) or biosynthesis
of other antibiotic compounds, including pyrrolnitrin (
5,
21)
and phenazine antibiotics (
26,
39), this technique could easily
be used to provide an additional level of discrimination between
isolates and strains producing other metabolites involved in
rhizosphere competence and biological control of plant pathogens.
Conclusion.
Establishing the presence of individual populations of antagonistic microorganisms in soil and rhizosphere environments is an important first step toward fully understanding the functional roles of the organisms in these natural environments. Additionally, the diversity within such indigenous populations of antagonistic microorganisms with a common biocontrol trait holds promise for further improvement of biological control, especially when this diversity reflects important interactions at the host-antagonist level. The technique described in this paper allows direct detection and assessment of the genotypic diversity of a specific group of bacteria that produce DAPG, a broad-spectrum antibiotic that has been implicated in biological control of multiple plant diseases and in the natural suppressiveness of soils. More specifically, our results indicated that the PCR-DGGE methodology can be used to detect specific phlD+ genotypes directly in rhizosphere samples with a detection limit of approximately 5 x 103 CFU/g of root and that it allows simultaneous detection of multiple genotypes present in a rhizosphere sample. Subsequent bioassays clearly showed that there is differential ability of the genotypic groups with respect to colonization of the sugar beet rhizosphere, confirming the biological significance of this methodology.

ACKNOWLEDGMENTS
This research is supported by the Technology Foundation STW
(project WBI.4843), the applied science division of NWO, and
the technology program of the Ministry of Economic Affairs.
The contribution of Jos Raaijmakers was financially supported
by the Royal Netherlands Academy of Arts and Science.
We thank Pierre de Wit for critically reading this manuscript and for his valuable suggestions.

FOOTNOTES
* Corresponding author. Mailing address: Laboratory of Phytopathology, Wageningen University, Binnenhaven 5, 6709 PD Wageningen, The Netherlands. Phone: 31 317 483427. Fax: 31 317 483412. E-mail:
jos.raaijmakers{at}wur.nl.


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Applied and Environmental Microbiology, February 2005, p. 993-1003, Vol. 71, No. 2
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