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Applied and Environmental Microbiology, March 2002, p. 1325-1335, Vol. 68, No. 3
0099-2240/02/$04.00+0 DOI: 10.1128/AEM.68.3.1325-1335.2002
Copyright © 2002, American Society for Microbiology. All Rights Reserved.
Effects of T4 Lysozyme Release from Transgenic Potato Roots on Bacterial Rhizosphere Communities Are Negligible Relative to Natural Factors
Holger Heuer,1,
Reiner M. Kroppenstedt,2 Jana Lottmann,3 Gabriele Berg,3 and Kornelia Smalla1*
Federal Biological Research Centre for Agriculture and Forestry, Institute for Microbiology, Plant Virology and Biosafety,1
German Collection of Microorganisms and Cell Cultures, Braunschweig,2
Department of Biological Science, Microbiology, University of Rostock, Rostock, Germany3
Received 31 July 2001/
Accepted 30 November 2001

ABSTRACT
Rhizosphere bacterial communities of two transgenic potato lines
which produce T4 lysozyme for protection against bacterial infections
were analyzed in comparison to communities of wild-type plants
and transgenic controls not harboring the lysozyme gene. Rhizosphere
samples were taken from young, flowering, and senescent plants
at two field sites in three consecutive years. The communities
were characterized in a polyphasic approach. Cultivation-dependent
methods included heterotrophic plate counts, determination of
species composition and diversity based on fatty acid analysis
of isolates, and community level catabolic profiling. Cultivation-independent
analyses were based on denaturing gradient gel electrophoresis
(DGGE) of 16S rRNA gene fragments amplified from rhizosphere
DNA using primers specific for
Bacteria,
Actinomycetales, or

- or ß-
Proteobacteria. Several bands of the DGGE patterns
were further characterized by sequence analysis. All methods
revealed that environmental factors related to season, field
site, or year but not to the T4 lysozyme expression of the transgenic
plants influenced the rhizosphere communities. For one of the
T4 lysozyme-producing cultivars, no deviation in the rhizosphere
communities compared to the control lines was observed. For
the other, differences were detected at some of the samplings
between the rhizosphere community structure and those of one
or all other cultivars which were not attributable to T4 lysozyme
production but most likely to differences observed in the growth
characteristics of this cultivar.

INTRODUCTION
Rhizobacteria can significantly influence plant growth either
positively or negatively (
33). After the removal of crop plants,
plant-induced changes in the soil microbial community can affect
the follow-on crop (
2). One possible reason for negative feedback
is the enrichment of host-specific pathogens, which is familiar
to agronomists (
5). Positive feedback might be due to an increase
in plant growth-promoting microbial populations. The compositions
of compounds which are released from the roots and interact
with bacteria in the rhizosphere vary depending on the plant
species, cultivar, and physiological status of the plants (
45).
Genetically engineered plants might change the bacterial consortia
in the rhizosphere due to the release of transgene products
or an altered composition of root exudates (
35). The transgenic
potato plants investigated in this study were engineered to
overcome limitations of conventional resistance breeding by
heterologous expression of the T4 lysozyme gene, which is a
strategy applicable to various crop plants and against a variety
of economically important crop diseases (
11,
30). T4 lysozyme
affects gram-positive and gram-negative bacteria either by its
muramidase activity against the bacterial cell wall component
murein (
46) or by a nonenzymatic mechanism which may involve
disruption of membranes (
14). In contrast to many other transgenic
plants, this genetic modification targeted bacteria, and it
was shown that plant-associated bacteria were indeed affected,
in that the susceptibility of the transgenic potato plants to
infection by
Erwinia carotovora was significantly reduced (
12,
13). Furthermore, it was demonstrated that a detectable amount
of T4 lysozyme was released from the roots (
6), causing bactericidal
activity on the root surface (
1). Many plant-associated bacterial
species were susceptible in vitro (
6,
10,
25). As the effects
on different species varied significantly, the T4 lysozyme expression
has the potential to change the structure of the bacterial community
in the soil fraction which is influenced by the plant roots
(i.e., the rhizosphere) and subsequently to affect the quality
or function of the soil. Only a few studies of the effects of
transgenic crop plants on the composition of bacterial communities
in the rhizosphere under field conditions (
26,
42) or in the
greenhouse (
7) have been published so far. In all three studies,
only culturable bacteria were investigated.
The objective of this study was to characterize the structure and dynamics of bacterial consortia in the rhizospheres of potato plants under field conditions and to compare them to those of the transgenic plants. Two T4 lysozyme-producing lines, a transgenic control without the T4 lysozyme gene, and the parental line were investigated over 3 years at two distant field sites with different soil types. The bacterial communities were analyzed by three different approaches, which were intended to complement each other. In the first approach, the relative abundances of bacterial species in the rhizosphere were determined based on the cultivation and characterization of isolates by fatty acid analysis. Although this approach is restricted to axenically culturable bacteria, it allowed us to identify species and keep representative strains for further characterization. The second approach was the catabolic profiling of the communities as functional units using Biolog GN microplates (16; reviewed in reference 15). The third approach was based on the analysis of 16S rRNA gene fragments amplified from total rhizosphere DNA by denaturing gradient gel electrophoresis (DGGE) (32; reviewed in reference 31) or by cloning and sequencing. This made it possible to monitor changes in the bacterial rhizosphere consortia, including those bacteria not readily culturable or those in a nonculturable state.

MATERIALS AND METHODS
Plants and field design.
Tubers of genetically modified and unmodified potato plants
(
Solanum tuberosum L.) were provided by K. Düring (MPB
Cologne, Cologne, Germany). The T4 lysozyme-producing plant
lines DL4 and DL5 were derived from
Solanum tuberosum cv. Désirée
and harbor the T-DNA from the binary vector pSR8-30 (
9) containing
the
nptII marker gene and the T4 lysozyme gene in a small polylinker
site (
11). The transgenic plants constitutively expressed the
bacteriophage T4 lysozyme under control of the cauliflower mosaic
virus 35S promoter (
13). The lysozyme gene was fused to the
barley

-amylase signal peptide gene. This leading sequence caused
the secretion of the lysozyme into the intercellular spaces
(
13,
24). The transgenic control plant line DC1 was transformed
with the same construct as DL4 and DL5 but without the T4 lysozyme
gene. Plants derived from the parental cell line, DES, were
taken as the nontransgenic control. Tubers of DES, DC1, DL4,
and DL5 were planted at Groß Lüsewitz near Rostock
(field L) and Quedlinburg (field Q) in complete randomized block
design in three consecutive years. Fields and tillage were provided
by the Bundesanstalt für Züchtungsforschung (Quedlinburg,
Germany). The fields and sampling times are described in Table
1. The soil was sandy loam with 1.1% organic matter in field
L and silt loam with 2.2% organic matter in field Q; both soils
had pH 5.9 (
26).
Sampling.
A rhizosphere sample consisted of 5 g (wet weight) of roots
with adhering soil from three to five plants from one plot.
All plots were sampled at least three times a year, from young
plants (principal growth stage 1, according to Hack et al. [
19]),
flowering plants (principal growth stage 6), and senescent plants
shortly before harvest of the tubers (principal growth stage
9). The samples were extracted three times for 1 min at 260
rpm in a stomacher blender with sterile solutions of (i) 0.3
g of Chelex-100 (Bio-Rad, Hercules, Calif.) in 20 ml of phosphate-buffered
saline (
40), (ii) 15 ml of SDP (0.02% sodium deoxycholate, 0.5%
polyethylene glycol), and (iii) 15 ml of distilled water, according
to a protocol slightly modified from that of Herron and Wellington
(
20). The three extracts were combined, 1 ml was used for serial
dilution and plating, 2 ml were centrifuged (20 min; 14,000
x g; 4°C), and the pellets were stored at -20°C for
later extraction of DNA. From the rest, most of the soil particles
were removed by a low-speed centrifugation step (2 min; 500
x g; 20°C), and then microorganisms were harvested from
the supernatant (20 min; 5,000
x g; 20°C) and resuspended
in 5 ml of sterile saline (0.85% NaCl). An aliquot of 0.5 ml
was diluted in 17 ml of sterile saline and mixed, and 0.15 ml
was transferred to each well of a Biolog GN microplate for community
level catabolic profiling.
Community level catabolic profiling in Biolog GN microplates.
Community level catabolic profiles were determined for eight replicate rhizosphere samples per plant line from 10 samplings of fields Q and L. The mixtures of microorganisms extracted from the rhizosphere samples were incubated in Biolog GN microplates in the dark at room temperature (20 to 25°C). The optical density (OD) was measured with a computer-linked microplate reader (Vmax; Molecular Devices Corp., Menlo Park, Calif.) at 595 nm at several time points after the first appearance of color. The data analysis was done as described by Glimm et al. (17). Shortly, the raw OD values in each microplate were corrected for the background color (OD0). The time point at which the highest number of wells over all microplates exceeded an OD0 of 0.1 (significant catabolic activity) was chosen for analysis. The OD0 was divided by the average well color of the plate to reduce the bias due to differing initial cell densities of the samples. The 95 variables were transformed to principal components (PCs) using the covariance of the variables. The first five PCs were used to test for significant differences between T4 lysozyme-producing plants and control plants (multivariate analysis of variance [MANOVA], P < 0.1).
Plating and characterization of bacterial isolates.
Aerobe heterotrophic plate counts were determined on R2A medium (Difco Laboratories, Detroit, Mich.), supplemented with 100 mg of cycloheximide (Sigma, Steinheim, Germany) liter-1, after 4 days' incubation at 20 to 23°C. The species compositions of the cultured rhizobacteria from the four plant lines were determined for all three samplings of field Q in the first year and for the last samplings of Q and L in the second year. For each sample, an equal number of colonies were randomly selected and purified on Trypticase soy broth (Becton Dickinson, Cockeysville, Md.) supplemented with 15 g of Bacto Agar (Difco Laboratories) liter-1 to obtain axenic cultures. A total of 2,010 strains were characterized by fatty acid analysis according to the standard procedure of the Microbial Identification System (MIS; MIDI Inc., Newark, N.J.).
Identification and classification of bacterial strains and analysis of species composition.
The MIS database TSBA (revision 3.9) was searched to identify the strains by their fatty acid profiles. To assign unnamed strains to known bacterial groups, their fatty acid profiles were compared to a database of 1,856 identified strains (MIS similarity index [SIM] > 0.2) which were isolated from the potato phyllosphere and rhizosphere. The strains were grouped into gram-positive bacteria, Cytophaga-Flavobacterium-Bacteroides (CFB) group bacteria, and gram-negative bacteria according to combinations of signature fatty acids (mainly with regard to hydroxylation or branching). The procedure FASTCLUS of the statistical package SAS (SAS Institute Inc., Cary, N.C.) was used to determine the most similar strain identified and to calculate the Euclidian distance, using the datasets of strains for which SIM was >0.2 as fixed cluster seeds. PC analysis (SAS procedure PRINCOMP, using the covariance matrix) was performed to compare the relative species abundances in the rhizospheres of the four plant lines. Shannon's diversity index H (41), which is a measure of both species richness and the degree of equitability of the relative species abundances, was calculated from the number of species, s, which were isolated from a plant line as determined by fatty acid analysis, and their proportion, p, of the total number of isolates: H = -
pi (log pi), where i = 1, . . . , s. To correct for differing numbers of isolates from the different plant lines at the five samplings, H was calculated repeatedly from random subsets of 47 strains until the average H did not change by further iterations (40 times).
Molecular analysis of the rhizosphere communities.
Total DNA was extracted by the method of Smalla et al., which included an enzymatic and a bead beating step for cell lysis, phenol-chloroform extractions, and a purification by glass milk (43). Amplification of the bacterial 16S ribosomal DNA (rDNA) fragment between positions 968 and 1401 (Escherichia coli numbering [3]) by PCR and separation of the products by DGGE were done as previously described (20a). A denaturing gradient of 3.2 to 4.6 M urea plus 16.0 to 23.2% (vol/vol) formamide was used for DGGE, which was performed in 1x Tris-acetate-EDTA buffer at 60°C and a constant voltage of 180 V for 4 h. A mixture of the 16S rDNA fragments from the following 11 bacterial species was applied to each DGGE gel as a marker: Clostridium pasteurianum DSM 525(a), E. carotovora DSM 30168(b), Agrobacterium tumefaciens DSM 30205(c), Pseudomonas fluorescens R2f(d), Pantoea agglomerans (e), Nocardia asteroides N3(f), Rhizobium leguminosarum DSM 30132(g), Actinomadura viridis DSM 43462(h), Kineosporia aurantiaca JCM 3230(i), Nocardiopsis atra ATCC 31511(j), and Actinoplanes philippinensis JCM 3001(k). Acid silver staining was used for detection of DNA in DGGE gels (39). Selective amplification of 16S rDNA from Actinomycetales in a first PCR followed by amplification of the nested fragment for DGGE analysis was done as previously described (23). The same approach was analogously applied to analyze the
- and ß-proteobacterial populations in the rhizosphere, using F203
(CCGCATACGCCCTACGGGGGAAAGATTTAT) and F948ß (CGCACAAGCGGTGGATGA) as taxon-specific primers (18). Two strategies were applied to characterize bands of the DGGE fingerprints by sequence analysis. The first approach was to excise bands from DGGE gels stained with SYBRgreen (BMA, Vallensbaek Strand, Denmark). The recovered DNA was reamplified and cloned with the pGEM-T kit (Promega, Mannheim, Germany). Cloned fragments were checked by DGGE to assess whether the desired band was cloned and were sequenced. The second approach was to amplify and clone large fragments of the 16S rDNA from total rhizosphere DNA for sequencing of ca. 1,400 bp between E. coli positions 28 and 1491. Sequences were analyzed using Chimera Check of the Ribosomal Database Project II (29) and the ARB software package (Department of Microbiology, Technical University of Munich, Munich, Germany [http://www.arb-home.de]).
Nucleotide sequence accession numbers.
Sequence accession numbers in GenBank are AY048885 to AY048918.

RESULTS
Phenotypes of the potato lines.
The plant lines DES, DC1, and DL5 showed normal growth in the
field, whereas DL4 appeared to have a reduced stem length and
smaller leaves when the plants were young (principal growth
stages 1 to 5), and the progress of senescence during growth
stage 9 was enhanced.
Community level catabolic profiling.
The mixtures of microorganisms extracted from the rhizospheres of the different plant lines were compared as functional units in their relative respiration rates of the 95 sole carbon sources which are supplied in Biolog GN microplates. To test sensitively for differences, the multivariate data sets were normalized and reduced in dimensionality to five PCs typically explaining more than 70% of the total variance and were compared by MANOVA. Significant differences (P < 0.1) in the community level catabolic potential were detected between rhizobacteria from DL4 and DC1 in six samplings, and in four of these samplings also between rhizobacteria from DL4 and DES (Table 2). The other T4 lysozyme-producing plant line, DL5, was never significantly different from the control lines. The deviation of DL4 did not correlate well with a particular plant growth stage, but it was most pronounced for senescent plants. A specific set of carbon sources correlated with the phenomenon could not be identified due to the variability of the Biolog pattern between samplings. The sets of utilized carbon sources were highly similar among all microplates of a sampling event irrespective of the plant line from which the inoculated sample originated. Three Biolog wells, where significant (univariate) differences in catabolic rates among samples from DL4 and both control lines were detected, were sampled for DGGE analysis after the experiment. For all plant lines, the DGGE fingerprints showed the same set of ribotypes being enriched by growth on the sole carbon source (data not shown). Only small differences in their relative abundances were observed. This indicated the sensitivity of the catabolic profiling and the detection of minor shifts in the community structure.
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TABLE 2. Pairwise statistical comparisons of community-level catabolic profiles (CLCP) of rhizosphere samples from T4 lysozyme-producing plants (DL4 and DL5) and control plants (DES and DC1) and aerobe bacterial plate counts
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Aerobe heterotrophic plate counts.
The numbers of aerobic bacteria that could be recovered from
the rhizospheres of the four plant lines were determined in
four samplings for field Q and six samplings for field L (Table
2). Only in the two samplings of senescent plants in field Q
were significant differences (
P < 0.1) between numbers of
CFU of the potato lines apparent: samples from DL4 showed higher
plate counts than all other plant lines in the first year but
slightly less than DES and DL5 in the second year. This deviation
of the DL4 samples coincided with reduced diversity indices
(
H) (Table
3). The average rhizosphere population sizes over
the 10 samplings did not significantly differ between T4 lysozyme-producing
and control plants (
P > 0.1; paired Student's
t tests).
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TABLE 3. Percentages of species and diversity of cultured rhizobacteria from plant lines DC1, DES, DL4, and DL5 in five samplings
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Species compositions of axenically cultured rhizobacteria.
The species compositions of the cultured rhizobacteria from
the four plant lines were determined for young, flowering, and
senescent plants in field Q in the first year and for senescent
plants in fields Q and L in the second year (Table
3). A diverse
spectrum of species from the

, ß and

subdivision
of the
Proteobacteria, the CFB group, actinobacteria, and low-G+C
gram-positive bacteria was isolated from the rhizospheres of
all four plant lines, as determined by identification of strains
based on their fatty acid profiles. A total of 156 species could
be distinguished, of which 28 species represented 75% of the
2,010 strains analyzed. Most frequently isolated were
Variovorax paradoxus (6.6%),
P. fluorescens (6.4%),
Flavobacterium johnsoniae (6.3%), and
Pseudomonas chlororaphis (5.6%). Differences in
species or genus composition of rhizosphere samples from T4
lysozyme-producing plants and control lines were apparent for
single samplings but were not consistent (Table
3). For instance,
Chryseobacterium was more frequently detected in samples from
the senescent control plants from field L in the second year
but was rarely found in samples from field Q in both years.
Flavobacterium,
Agrobacterium,
Comamonas, and
Enterobacter were
more often cultured from T4 lysozyme-producing plants in some
samplings but more often from control plants in other samplings.
The higher abundance of
Pseudomonas syringae and
Acinetobacter baumannii in the rhizospheres of young T4 lysozyme plants and
of
Burkholderia cepacia in the rhizospheres of senescent control
plants in the first year could not be confirmed in other samplings.
All these deviations in species or genus abundance were the
effect of natural variation rather than of T4 lysozyme production.
The taxonomic distribution of all strains retrieved from the five samplings is summarized in Table 4. This shows a slightly reduced occurrence of
-Proteobacteria, mainly represented by the genus Agrobacterium, for the samples from T4 lysozyme plants. For all other taxa, the differences within the groups of T4 lysozyme plants and control plants exceeded the difference between those groups. Compared to the other plant lines, the exceptionally high abundance of the genus Pseudomonas in the rhizosphere of DL4 was noticeable. Gram-positive bacteria, which on average might be more affected by the muramidase activity of T4 lysozyme than other bacteria, were more frequently recovered from the wild-type DES (27% of all strains from DES) than from the T4 lysozyme-producing lines DL4 and DL5 (23%). Nevertheless, the transgenic control line DC1 showed the same percentage of gram-positive strains as DL4 and DL5. The higher percentage of gram-positive bacteria in the rhizosphere of DES could be attributed exclusively to the sampling of young plants. The percentages of gram-positive bacteria decreased during the season (first year; field Q), from an average of 45% for young plants and 35% for flowering plants to 12% for senescent plants. The low proportion of gram-positive bacteria in the rhizospheres of senescent plants was also observed in the second year in fields Q and L (13 and 8%, respectively).
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TABLE 4. Taxonomic distribution of strains from the rhizospheres of T4 lysozyme-producing plants (DL4 and DL5) and control plants (DC1 and DES) in five samplings
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The distributions of the more abundant species (>5% of all
isolates) were compared among the different plant lines and
samplings by PC analysis in order to consider concerted effects
on two or more species (Fig.
1). Each datum point represented
the distribution of species which were isolated from the rhizosphere
of a plant line at one sampling event. The species patterns
clustered in the first and second PCs according to the plant
growth stage and year of sampling, whereas the production of
T4 lysozyme was not a major factor. The patterns from young
plants were discriminated from the patterns of older plants
mainly in the second PC, which was highly correlated with the
prevalence of
Bacillus megaterium (Pearson correlation,
r2 =
0.75). The species patterns from flowering and senescent plants
were mainly separated by the first PC due to the higher percentages
of
V. paradoxus (
r2 = 0.76) and
Streptoverticillium (
r2 = 0.75)
in the rhizospheres of flowering plants. The samples from DL4
had smaller values of the first PC than the other plant lines
for all samplings of field site Q. The samples of the second
year from both field sites were highly similar irrespective
of the plant line they originated from. For all samplings, the
average distance in the PC plots between control plants and
T4 lysozyme plants was small compared to the average within-group
distance. Thus, the differences in species composition could
not be attributed to the T4 lysozyme factor but rather to other
plant properties, where DL4 and DL5 especially differed.
Genetic fingerprints of the bacterial rhizosphere communities by DGGE.
Molecular analysis of the bacterial rhizosphere communities
was done by PCR amplification of 16S rRNA genes with bacterium-specific
primers from total DNA of each sample and separation in DGGE
based on sequence variability. The rhizosphere communities of
the four plant lines were compared by DGGE profiling for all
22 samplings which were taken in three consecutive years at
the two field sites and at various growth stages of the plants.
For each sampling, community fingerprints were done in DGGE
gels comparing the replicate samples of a T4 lysozyme-producing
plant line to a control plant line. The DGGE fingerprints of
rhizosphere communities from young plants, which were growing
in separate plots of field L in the first year, are shown in
Fig.
2. Despite some variable bands, all fingerprints from the
different plots were highly similar. Bands specific for the
T4 lysozyme plants or the control plants were not observed,
which indicated that neither the plant line nor the production
of T4 lysozyme significantly affected the abundant bacterial
species in the rhizosphere. This result was observed for nearly
all samplings. The only exception was sampling Q3 (field Q;
first year; senescent plants), where a particular band was dominant
in the DGGE fingerprints of seven of the eight replicate rhizosphere
samples of plant line DL4. In the fingerprints from rhizosphere
samples of the other plant lines, this band was much weaker,
with the exception of a single sample from plant line DES. The
sequence of the DNA from this band could be attributed to the
species
E. carotovora. The plants did not show symptoms of an
infection with this species, but senescence was more pronounced
than for the other plants. The other T4 lysozyme-producing plant
line DL5 corresponded in the DGGE fingerprints with the control
lines DES and DC1 in sampling Q3 as well as in all other samplings.
Effects of environmental factors other than T4 lysozyme analyzed by DGGE.
In order to draw conclusions about the biosafety of the transgenic
plants, we had to analyze whether DGGE analysis is sensitive
enough to detect relevant changes in the bacterial community
structure. A relevant perturbation should cause deeper changes
in the community structure than changes due to common environmental
factors related to the season, field site, or year. To analyze
this natural variability, samples representative of all samples
of a particular sampling with regard to their DGGE fingerprints
were selected for within-gel comparison between different samplings.
In Fig.
3, a DGGE gel is shown which demonstrates seasonal changes
of the bacterial community structure in the rhizospheres of
DES and DL5 (field L; third year). Once again, it became obvious
that the fingerprints from samples of the transgenic and the
wild-type plants did not differ significantly. However, seasonal
shifts in the community structure became apparent. Band hw6
was most intense for flowering plants. It represented a ribotype
with a high sequence identity (99.5%) to that of
Serratia ficaria JCM1241. Many band intensities changed when the plants reached
the growth stage of flowering and remained stable until the
harvest of the potatoes, e.g., bands hw7 and hw8. Band hw7 represented
an

-proteobacterium with 95.7% sequence identity of the DGGE
fragment to the type strain of
Devosia riboflavina. Identical
sequences were found in three samplings (L3, L10, and L11).
Band hw8 originated from the 16S rRNA gene of a streptomycete
(99.0% sequence identity to
Streptomyces olivoreticuli). Also,
for hw8 it was confirmed that the band represented identical
sequences in fingerprints of samplings L10 and L11. In general,
fingerprints of rhizosphere samples from senescent plants were
more variable than those of samples from young or flowering
plants with respect to strong bands in the upper part of the
DGGE gels, some of which could be attributed to enterobacterial
genera (
Enterobacter,
Serratia, and
Kluyvera), as determined
by sequencing of the DNA from the respective bands (B3, hw6,
and hw3).
In Fig.
4, representative fingerprints of samples from the two
field sites and from different years are shown for comparable
growth stages of the plants. A significant natural variability
could be detected. Many bands appeared only temporarily (e.g.,
hw6). The bacterial rhizosphere communities were more influenced
by environmental factors related to the field site and the year
of sampling than by those related to seasonal changes. Despite
this variability, some bands were present in all fingerprints
(e.g., hw8), and many others were present in samples from different
years or different field sites (e.g., hw7). This showed that
part of the community was maintained under very different environmental
conditions with regard to the soil type, climate, and state
of the plant roots.
DGGE analysis of
- and ß-Proteobacteria and Actinomycetales.
Specific primers were used to selectively amplify 16S rRNA genes
of the taxa

-
Proteobacteria, ß-
Proteobacteria, and
Actinomycetales from total rhizosphere DNA in a first PCR. The
diluted PCR products were used as targets for DGGE analyses
in order to compare rhizosphere communities of T4 lysozyme-producing
and control plants on the taxon level. It was apparent that
an effect of T4 lysozyme on the bacterial rhizosphere populations
belonging to the three taxa was not detectable (Fig.
5). The
sensitivity was increased by the taxon-specific approach, because
many bands of these profiles were not visible or hardly visible
in the total bacterial profiles (Fig.
5 and
6, lanes C), especially
bands of ß-proteobacteria. In contrast, some of the

-proteobacteria (e.g., the population represented by band hw7)
and many of the
Actinomycetales (e.g., the population represented
by band hw8) were among the most abundant community members,
as the taxon-specific fingerprints partially agree with the
total bacterial profiles (Fig.
6). The specificity of the approach
was confirmed by recovery of DNA from bands of the taxon-specific
fingerprints (Fig.
6) and sequence analyses. The sequences of
the DNA recovered from the bands hw11 and hw12 of the

-proteobacterial
profile were affiliated with the

-proteobacteria, hw13 and hw15
of the ß-proteobacterial profile were affiliated with
the ß-proteobacteria, and hw17 of the actinomycete
profile was affiliated with the genus
Streptomyces (Fig.
7).
The taxon-specific DGGE fingerprints of DES and DL5 were also
virtually identical for other samplings, while seasonal shifts
were easily detectable (data not shown).
Sequence analysis of amplified 16S rRNA genes.
Two strategies were applied to characterize bands of the DGGE
fingerprints by sequence analysis. The first approach was to
excise bands from DGGE gels and reamplify and clone the recovered
DNA for sequencing. Altogether, 21 sequences were obtained which
were not suspected to be chimeric (DGGE bands B1 to B7 (
20a)
and hw3 to hw17c [Fig.
7]). The second approach was to amplify
and clone 1.5-kb fragments of the 16S rDNA from total rhizosphere
DNA. A library of 80 clones from three samplings (Q2, Q3, and
L3) was analyzed in DGGE for correspondence with bands of the
rhizosphere community fingerprints. Nine clones were selected
for sequence analysis (rhizosphere clones C1 to C19 [Fig.
7]).
The rhizobacteria from which the sequences originated were phylogenetically
affiliated with the

-
Proteobacteria, the families
Enterobacteriaceae and
Pseudomonadaceae, the
Stenotrophomonas group of the

-
Proteobacteria,
the

-
Proteobacteria, verrucomicrobia, CFB group bacteria, and
the
Actinomycetales. Sequences of ß-proteobacteria
(
Variovorax and
Burkholderia) were found only if this group
was specifically amplified from total rhizosphere DNA, providing
more evidence for its lower abundance in the potato rhizosphere
relative to other taxa. In contrast, the percentage of cultured
ß-proteobacterial strains from the potato rhizosphere
was more than 10% (mainly
Variovorax and
Comamonas). From rhizosphere
DNA of sampling L3, a 1.5-kb 16S rDNA fragment was cloned and
sequenced in which the sequence of the DGGE fragment was identical
with that of band hw7. This band was highly abundant in samples
from most of the samplings. The nearly complete 16S rDNA had
only 92.1% sequence identity with the most similar database
sequence, which belongs to the

-proteobacterium
D. riboflavina.
Thus, this sequence probably originated from an abundant but
still-uncultured rhizobacterium.

DISCUSSION
This extensive field study of the impact of T4 lysozyme-producing
potato plants on bacterial communities in agricultural soil
contributed to the biosafety issue of whether genetically engineered
crop plants have the potential to unintentionally change the
agroecosystem by selecting bacterial communities different from
those selected by conventionally bred varieties. In contrast
to many other transgenic plants, the genetic modification targeted
bacteria (
12,
13), the transgene product had the potential to
affect many rhizobacterial species (
6,
10), and the roots released
it in an active form (
1). Moreover, the rhizosphere is known
to be a location of strong interaction between plants and microorganisms,
and potential effects of the T4 lysozyme on the bacterial community
structure were allowed to accumulate by using the same plots
for up to 3 years. Despite all that, differences between the
rhizosphere communities of the T4 lysozyme-expressing line DL5
and control plants were not detectable. One possible explanation
for this result is that the rhizosphere communities were stable
enough to resist T4 lysozyme effects. Evidence for that was
provided by the highly similar community profiles, especially
the DGGE fingerprints, of all samples taken from the different
plants in a field at a certain time. Another explanation might
be that an existing effect was not detected due to insufficient
resolution and sensitivity of the methods or too few replicate
samples, considering the natural variability. We tried to minimize
the probability of the latter error by using a high number of
replicate samples (
n = 8 plots), by setting the significance
level of statistical tests to 0.1 instead of 0.05, by taking
composite samples from several plants from one plot to reduce
variability, and by applying a range of complementary methods
with differing levels of resolution and sensitivity. Biosafety
as a relative term is reasonably associated with an acceptable
risk which is not significantly different from accepted background
levels. A relevant effect of the transgenic plants should cause
deeper changes in the community structure than the commonly
accepted changes due to environmental factors related to the
season, field site, or year. In this study, the environmental
factors, but not the T4 lysozyme expression of the transgenic
plants, influenced the rhizosphere communities, as shown by
the DGGE profiles, the compositions of bacterial isolates, and
Biolog profiles of the different samplings. Thus, the risk associated
with transgene effects on the bacterial community seems to be
below accepted background levels. Furthermore, the resolutions
and sensitivities of the applied methods were good enough to
detect relevant community changes. In parallel studies by Lottmann
et al., the distribution of potentially plant-beneficial bacteria,
which were isolated from the transgenic and control roots and
characterized phenotypically and genotypically, was not affected
by T4 lysozyme expression (
25,
26). Lukow et al. found seasonal
and spatial changes in soil bacterial communities by terminal
restriction fragment length polymorphism analysis in three soil
plots planted with transgenic GUS (ß-glucuronidase
gene), transgenic GUS/Barnase/Barstar potato lines, or nontransgenic
potato plants (
28). The seasonal shifts were more prominent
than the spatial differences. It remained unclear whether transgene
effects contributed to the spatial effects because replicated
plots were lacking. In a field experiment, Lottmann et al. monitored
the survival of two bacterial strains, a T4 lysozyme-tolerant
Pseudomonas putida strain and a T4 lysozyme sensitive
Serratia grimesii strain, in the rhizospheres of DL5, DES, and DC1, where
both strains were established after seed tuber inoculation (
27).
During flowering of the plants and coincidentally with the highest
measured level of T4 lysozyme expression of DL5, significantly
more colony counts of the T4 lysozyme-tolerant
P. putida were
recovered from transgenic T4 lysozyme plants than from the transgenic
control and the parental line. In a previous study, phyllosphere
bacterial communities of T4 lysozyme potato plants and control
lines were compared in the greenhouse and a field sampling (
22).
Differences in the percentages of culturable species were detectable
for the T4 lysozyme plants, namely, a higher percentage of isolates
classified as
Erwinia sp. and lower abundances of gram-positive
isolates and of
Agrobacterium, but the observed effects were
minor relative to the natural phyllosphere community differences
between field samplings.
The real community structure cannot be completely reflected by a single method but is best recovered by the applied polyphasic approach. By cultivation of bacteria on solid media and characterization of isolated pure cultures by the standard MIS procedure, species or populations that did not grow on the applied media were not detectable. Other unrecovered populations possibly entered a nonculturable state (47) or depended on biotic interactions. As DGGE profiles were derived independently of cultivation, they more accurately displayed abundant species. The high percentage of cultured ß-proteobacterial strains from the potato rhizosphere was not confirmed by molecular detection (Fig. 5). Differential lysis efficiencies and preferential amplification of species may bias the relative intensities of bands within a genetic fingerprint (21), but this does not affect comparison between fingerprints.
In contrast to DL5, the T4 lysozyme-expressing line DL4 often differed from the control lines and also from DL5 in its rhizosphere community structure. Rhizosphere samples of senescent DL4 plants in field Q were characterized in the first year by higher plate counts, reduced diversity of cultured bacteria, higher percentages of isolated strains classified as Pseudomonas or Flavobacterium, and differences in community level catabolic profiles and specific bands in DGGE fingerprints. In several other samplings, differences of DL4 from control plants were detected mainly in community level catabolic profiles, which were not reflected in DGGE profiling. Obviously, the catabolic profiling sensitively detected differences in the relative abundance of a community fraction which grew well in the Biolog plates but was not among the most abundant community members. By analyses of Biolog wells inoculated with cell suspensions from the potato rhizosphere, Smalla et al. observed that, compared with the inoculum, there was a decrease in the number of 16S rRNA gene fragments obtained from various wells, as well as a concomitant loss of populations that had been numerically dominant in the inoculum, and they suggested that fast-growing bacteria adapted to high substrate concentrations may have been primarily responsible for the patterns of substrate use (44). The deviation of DL4 was most likely connected to a general weakness of these plants evidenced by a significantly reduced root biomass (26), shorter stems and smaller leaves in the young plants, and a faster progress of senescence in the old plants. This could be the consequence of multiple and irregular integration of the T-DNA into the plant genome, affecting the functions of flanking genetic regions (38).
In contrast to experiments in which DGGE fingerprints have been used to analyze bacterial rhizosphere communities of plants grown in microcosms (8, 34), seasonal shifts of bacterial rhizosphere communities were found for field-grown plants (references 18, 27, and 44a and this study). Compared to natural community shifts, the T4 lysozyme was only a minor factorif anyin changing the bacterial community structure of the agroecosystem. However, the expression of T4 lysozyme significantly reduced the susceptibility of transgenic potato plants to infection by Erwinia carotovora subsp. atroseptica (12, 13), the causative agent of blackleg disease and soft rot of tubers (37). This effect could be achieved despite rather low expression levels (<18 ppm of total soluble protein [12]). The probable reason is that the T4 lysozyme is fused to a signal peptide, leading to secretion into the apoplast (13), where the initially small population of the plant pathogen has to multiply before it is able to attack the plant (4, 36). Thus, this genetic modification may be a suitable strategy for enhancing resistance of crops to bacterial disease, as counteractive effects on potentially beneficial populations are avoided.

ACKNOWLEDGMENTS
We are grateful to Henrike Westphal for excellent technical
assistance, to Johann de Vries and all others who helped to
sample the roots, and to D. Felgentreu for his help with the
gas chromatographic analysis of fatty acids.
This work was supported by BMBF grants 0310582A and 0311295.

FOOTNOTES
* Corresponding author. Mailing address: BBA, Institut PS, Messeweg 11-12, D-38104 Braunschweig, Germany. Phone: 495312993814. Fax: 495312993013. E-mail:
k.smalla{at}bba.de.

Present address: GBF, Microbial Ecology, D-38124 Braunschweig, Germany. 

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Applied and Environmental Microbiology, March 2002, p. 1325-1335, Vol. 68, No. 3
0099-2240/02/$04.00+0 DOI: 10.1128/AEM.68.3.1325-1335.2002
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