Editor: Kornelia Smalla
Rhizosphere bacteria affected by transgenic potatoes with antibacterial activities compared with the effects of soil, wild-type potatoes, vegetation stage and pathogen exposure
Version of Record online: 31 OCT 2005
FEMS Microbiology Ecology
Volume 56, Issue 2, pages 219–235, May 2006
How to Cite
Rasche, F., Hödl, V., Poll, C., Kandeler, E., Gerzabek, M. H., Van Elsas, J. D. and Sessitsch, A. (2006), Rhizosphere bacteria affected by transgenic potatoes with antibacterial activities compared with the effects of soil, wild-type potatoes, vegetation stage and pathogen exposure. FEMS Microbiology Ecology, 56: 219–235. doi: 10.1111/j.1574-6941.2005.00027.x
- Issue online: 24 FEB 2006
- Version of Record online: 31 OCT 2005
- Received 26 November 2004; revised 7 April 2005; accepted 8 April 2005First published online 31 October 2005.
- genetically modified potato;
- antibacterial compounds;
- microbial diversity;
- microbial enzyme activity
- Top of page
- Materials and methods
A greenhouse experiment was performed to analyze a potential effect of genetically modified potatoes expressing antibacterial compounds (attacin/cecropin, T4 lysozyme) and their nearly isogenic, nontransformed parental wild types on rhizosphere bacterial communities. To compare plant transformation-related variations with commonly accepted impacts caused by altered environmental conditions, potatoes were cultivated under different environmental conditions, for example using contrasting soil types. Further, plants were challenged with the blackleg pathogen Erwinia carotovora ssp. atroseptica. Rhizosphere soil samples were obtained at the stem elongation and early flowering stages. The activities of various extracellular rhizosphere enzymes involved in the C-, P- and N-nutrient cycles were determined as the rates of fluorescence of enzymatically hydrolyzed substrates containing the highly fluorescent compounds 4-methylumbelliferone or 7-amino-4-methyl coumarin. The structural diversity of the bacterial communities was assessed by 16S rRNA-based terminal restriction fragment length polymorphism analysis, and 16S rRNA gene clone libraries were established for the flowering conventional and T4 lysozyme-expressing Desirée lines grown on the chernozem soil, each line treated with and without E. carotovora ssp. atroseptica. Both genetic transformation events induced a differentiation in the activity rates and structures of associated bacterial communities. In general, T4 lysozyme had a stronger effect than attacin/cecropin. In comparison with the other factors, the impact of the genetic modification was only transient and minor, or comparable to the dominant variations caused by soil type, plant genotype, vegetation stage and pathogen exposure.
- Top of page
- Materials and methods
The production of potatoes (Solanum tuberosum L.) is accompanied by severe diseases caused by bacterial phytopathogens leading to enormous losses in yield and quality worldwide (Oerke et al., 1994). One of the most important potato pathogens is the gram-negative enterobacterium Erwinia carotovora ssp. atroseptica (Eca) (Pérombelon, 2002). Eca induces blackleg and soft rot of potatoes by producing high levels of multiple exoenzymes, including pectinases, cellulases and proteases, which are able to break down plant cell walls and release nutrients for bacterial growth (Hélias et al., 2000). Currently, conventional breeding has not revealed appropriate resistant cultivars and management practices in field and storage have hardly been able to reduce the appearance of pathogens. Genetic engineering, e.g. the production of antimicrobial compounds (Mourgues et al., 1998), represents one approach to fighting off pathogens.
Cecropins, which exhibit lytic and antibacterial activity against several gram-negative and gram-positive bacteria in vitro, were first isolated from the giant silk moth, Hyalophora cecropia (Hultmark et al., 1980). It has been confirmed that cecropins, especially cecropin B, have a strong in vitro toxicity against a number of plant pathogenic bacteria (Nordeen et al., 1992). Transgenic plants expressing cecropin B have been demonstrated to fight off bacterial phytopathogens successfully (Huang et al., 1997; Sharma et al., 2000). In addition to cecropins, attacins produced by the giant silk moth show antibacterial activity (Hultmark et al., 1983). The capability of attacin to fight off the bacterial pathogen Erwinia amylovora causing fire blight was successfully demonstrated on transgenic apple and pear trees by Reynoird et al. (1999) and Norelli et al. (1994), respectively. Another promising strategy for potential bacterial pathogen control in crops is the insertion of the gene encoding antibacterial T4 lysozyme (de Vries et al., 1999), which shows lytic activity on the cell walls of gram-positive as well as of gram-negative bacteria. Tsugita et al. (1968) reported the murimidase activity of T4 lysozyme against the bacterial cell wall component murein, and Düring et al. (1999) described a nonenzymatic mechanism which may be involved in cell membrane disruption. T4 lysozyme is thought to protect the plant by fighting off pathogenic bacteria invading the plant (de Vries et al., 1999). Earlier studies had already confirmed that the production of T4 lysozyme in transgenic potatoes effectively enhanced the resistance against E. carotovora (Düring et al., 1993; Heuer & Smalla, 1999).
Currently, public debate on the release of genetically modified (GM) crops has led to questions regarding their ecological compatibility. Many studies have addressed biosafety aspects as well as risk assessment of undesired ecological side-effects of GM crops such as structural and functional alterations of plant-associated microbial populations (for reviews see Wolfenbarger & Phifer, 2000; Dale et al., 2002; Conner et al., 2003). GM crops have to be carefully investigated for possible harmful effects on the environment (e.g. rhizosphere), where the soil biota are integrally involved in biogeochemical cycles and where their activities contribute to the productivity of terrestrial ecosystems (Buckley & Schmidt, 2003; Nannipieri et al., 2003).
The structure and function of the rhizosphere microflora may be affected by the plant physiology often found in different plant genotypes (Grayston et al., 1998; Smalla et al., 2001; Söderberg et al., 2002), and may also fluctuate between vegetation stages of the same plant genotype (Wieland et al., 2001; Gyamfi et al., 2002). Furthermore, environmental factors such as soil type (Buyer et al., 1999) as well as stress response due to pathogens (Yang et al., 2001) have been found to cause microbial community shifts. These studies suggest that a comparison of GM crops with the isogenic, nontransgenic control regarding the potential impact on the functioning and community composition of rhizosphere microflora has to take into account different environmental conditions as well as variation between plant genotypes and vegetation stages.
Cultivation-independent community analysis has become state-of-the-art in order to address the highly diverse and mostly uncultivable bacterial populations in terrestrial ecosystems. Commonly, the small subunit 16S rRNA gene is used as a phylogenetic marker. 16S rRNA-based terminal restriction fragment length polymorphism (T-RFLP) analysis, which was introduced by Liu et al. (1997) for the characterization of highly diverse soil bacterial communities, is one of the most powerful fingerprinting techniques available at present. Measurement of extracellular catabolic enzyme activities has proved to be highly useful for functional analysis of microbial communities (Miller et al., 1998; Kandeler et al., 1999). The prompt responsiveness of various enzymes to environmental disturbance makes them a potential indicator of soil biological activity (Lahav & Steinberger, 2001).
The objective of this study was to investigate the potential impact of transgenic potatoes with antibacterial activities on the structure and function of associated rhizosphere microbial populations. To compare observed fluctuations due to the plant transformation with generally accepted effects caused by various environmental conditions, transgenic and nearly isogenic, nontransgenic control plants were grown in two contrasting soils. A treatment with pathogen (E. carotovora ssp. atroseptica) exposure was included. Microbial communities colonizing the rhizospheres of two lytic peptide/protein-expressing potato lines as well as their nearly isogenic, nontransgenic wild types were assessed by 16S rRNA gene-based T-RFLP and enzyme analysis at two vegetation stages.
Materials and methods
- Top of page
- Materials and methods
In May 2003, a greenhouse experiment was performed with four different lines of Solanum tuberosum L.: cultivar Desirée DL12 (transgenic, containing the T4 lysozyme gene with the CaMV 35S promoter), cultivar Desirée DC (nontransgenic control), cultivar Merkur MT (transgenic, containing the attacin E gene [Att] and cecropin B gene [C4] with the mas2C4-mas1Att nopaline synthase promoter) and cultivar Merkur MC (nontransgenic control). For T4 lysozyme plants, expression of the transgene was verified by real-time PCR using RNA isolated from roots (data not shown). For the other plants, gene expression had been verified in previous experiments by Northern blot analysis (Kopper, 1999; Keppel, 2000). Plants were grown in two contrasting soils (luvisol, soil L and chernozem, soil C) to simulate different environmental conditions. Soils were taken from the top layer (0–25 cm) of two agricultural fields in Austria. The luvisol had developed on crystalline bedrock and was derived from Meires (north of Lower Austria), whereas the chernozem had developed on marine sediments and was taken from Seibersdorf (southeast of Lower Austria). The two soils differed in soil texture (soil L: sand 65%, silt 25%, clay 10%; soil C: sand 43%, silt 37%, clay 21%), organic carbon (soil L: 0.9%; (soil C: 2.7%), pH value (soil L: 3.8; soil C: 7.0) and available plant nutrients such as NO3N (soil L: 16.5 mg kg–1; soil C: 81.9 mg kg–1), P2O5 (soil L: 8.9 mg 100 mg–1; soil C: 22.7 mg 100 mg–1), K2O (soil L: 12.7 mg 100 mg–1; soil C: 33.8 mg 100 mg–1) and Mg (soil L: 6.0 mg 100 mg–1; soil C: 12.0 mg 100 mg–1).
Prior to tuber planting, stones and root material were removed from each soil, before homogenization of the soil by passage through a 10 mm sieve. Planting pots (13 × 13 × 13 cm) were filled with soil and one tuber planted per pot. For each of the different treatments, six replicate plants (in total 96 plants) were arranged in a randomized block design. During the experiment, eight plants (one DL 12, five MC, two MT) did not grow due to tuber rottenness after planting. These were excluded from further analysis.
For inoculation with the blackleg pathogen E. carotovora ssp. atroseptica, strain IPO161::gusA110 carrying the gusA gene in control of the ptac promoter and the lacIq repressor gene (Wilson et al., 1995) was used. A marked strain was applied in order to be able to monitor pathogen colonization. After the plants had reached the height of approximately 15–20 cm (vegetation stage 3 ‘stem elongation’ according to the vegetation stages defined by Hack et al. 1993), they were infected with strain IPO161::gusA110 by applying a modified toothpick protocol as published by Lees et al. (2000). Cell material of a fresh Eca colony was taken from 10% TSA (Merck, Darmstadt, Germany) solid medium with an autoclaved wooden toothpick, which was then inserted into the plant stem (2–3 cm above soil surface). The infection site was subsequently wrapped in cotton wool, which was moistened to keep the infection site wet. After the infection procedure, the plants were sprayed with a fine mist of water and subsequently covered with a plastic bag to keep the whole plant in a moist atmosphere. Plastic bags were not removed until plants were sampled. The noninfected control plants were treated in the same way but with sterile medium. Generally, transgenic lines clearly showed less disease symptoms than their nontransgenic counterparts; however, production of antibacterial substances did not result in resistance against the pathogen. Pathogen levels and blackleg symptoms depended on the presence of the transgene, the kind of antibacterial substance and the vegetation stage. Eca colonization ranged from 7.67 × 102±2.31 × 102 SE (standard error) CFU per gram fresh plant material at stem elongation (Hack et al., 1993) to 2.92 × 103±3.21 × 102 SE CFU at the early flowering per gram fresh plant material (Hack et al., 1993). At stem elongation stage, 71% of Eca-infected potato plants showed the initiation of blackleg symptoms, whereas at the early flowering stage, blackleg symptoms had proceeded for 86% of Eca-challenged plants.
Rhizosphere soil samples were obtained from three replicate plants per treatment, 10 days (‘stem elongation’, stage 3; Hack et al., 1993) and 30 days (‘early flowering’, stage 6; Hack et al., 1993) after infection. Plants were taken from planting pots and shaken carefully to remove the nonadhering soil. A brush was used to remove gently the adhering rhizosphere soil from plant roots, which was passed through a 1 mm sieve and stored at −20°C until analysis.
Rhizosphere soil enzyme activity analysis
Activities of extracellular rhizosphere enzymes involved in the C-, P- and N-nutrient cycles were determined as the rates of fluorescence of enzymatic hydrolyzed substrates containing the highly fluorescent compounds 4-methylumbelliferone (4-MUF; 4-MUF-α-d-glucoside (α-d-glucosidase), 4-MUF-β-d-glucoside (β-d-glucosidase), 4-MUF-cellobioside (β-d-cellobiohydrolase), 4-MUF-xyloside (β-d-xylosidase), 4-MUF-N-acetyl-glucosaminide (N-acetyl-β-d-glucosaminidase), 4-MUF-phosphate (phosphatase)) and 7-amino-4-methyl coumarin (7-AMC; l-leucine-7-AMC [leucine aminopeptidase]) (all substrates were provided by Sigma-Aldrich, St. Louis, MO).
Measurement of enzyme activities was performed with slight modifications according to the protocol previously published by Marx et al. (2001). All substrates were dissolved in 300 μL dimethylsulfoxide (DMSO), filled to a final volume of 10 mL with autoclaved H2O (10 mM stock solution), and stored at 4°C until further processing. For analysis, a 1 mM working solution of each substrate was prepared with autoclaved buffer. Buffers were prepared for the stabilization of substrate fluorescence as well as for optimization of enzyme reaction (0.1 M MES-buffer (2-[N-Morpholino]ethanesulfonic acid, pH 6.1) for MUF-substrates, and 0.05 M Trizma® buffer (Sigma-Aldrich) for the AMC-substrate (pH 7.8). Buffers were autoclaved before use. Standards were used for both dyes, 4-MUF and 7-AMC. For preparation of standard stock solutions, 0.1762 g 4-methylumbelliferone (10 mM), and 0.0876 g 7-amino-4-methyl coumarin (5 mM), respectively, were suspended in 100 mL methanol and autoclaved H2O (1 : 1). The stock solutions were diluted with the corresponding buffer to a final concentration of 10 μM.
For enzyme activity analysis, 0.5 g of frozen 1 mm sieved rhizosphere soil was weighed into an autoclaved beaker. Each sample was suspended in 50 mL autoclaved H2O and sonicated with an ultrasonic disintegrator for 2 min at an output energy of 50 J s−1 to break up macroaggregates. Homogenized soil suspension 50 μL was dispensed into the microtiter plate (PP microplate, black 96-well, Greiner, Frickenhausen, Germany), 50 μL buffer (0.1 M MES, 0.05 Trizma®), and 100 μL of 1 mM substrate solution were added. Three analytical replicates for each substrate were prepared. The total volume of each microplate well was 200 μL. For each sample a standard plate for both dyes, 4-MUF and 7-AMC, was prepared and treated in the same way as the plates with soil and substrate. Each individual well of the standard plates was filled with 50 μL soil suspension and 150 μL of standard/buffer-mixture in the following concentrations: 0 μM (0 μL dye solution [10 μM]+150 μL buffer), 0.5, 1.0, 2.5, 4.0, and 6.0 μM. Microtiter plates were incubated at 30°C, and monitored over a period of 3 h. Simultaneous detection of substrate hydrolysis was carried out after 30, 60, 120, and 180 min with a microplate reader (FLX 800, Microplate Fluorescence Reader, Bio-Tek Instruments, Inc., Winooski, VT). Increase in substrate hydrolysis in the samples over time was calculated as a linear regression according to the dye-specific standards, and presented as nmol g–1 h–1.
Rhizosphere soil DNA was isolated using the UltraClean Soil DNA Kit (MoBioLab., Inc., Solana Beach, CA, USA) according to the manufacturer's instructions. 16S rRNA genes of rhizosphere bacteria were amplified by PCR using the primers 8F (5′-AGAGTTTGATCCTGGCTCAG-3′) (Weisburg et al., 1991) and 1520R (5′-AAGGAGGTGATCCAGCCGCA-3′) (Edwards et al., 1989). For T-RFLP analysis, 8F primer was labeled with 6-carboxyfluorescein at the 5′ end. PCR-reaction cocktails of 50 μL contained 1 μL of undiluted DNA extract as template, 1 × PCR reaction buffer (Invitrogen, Carlsbad, CA), 2.5 mM MgCl2, 0.15 μM of each primer, 0.2 mM of each deoxynucleoside triphosphate, and 2 U Taq DNA polymerase (Invitrogen). PCR amplifications were performed under the following conditions: initial denaturation for 5 min at 95°C, 30 cycles consisting of denaturation for 30 s at 95°C, primer annealing for 1 min at 55°C, and polymerization for 2 min at 72°C. Amplification was completed by a final extension for 10 min at 72°C. PCR products (5 μL) were checked by electrophoresis in 1% (w/v) agarose gels.
Digestion of 10 μL PCR products was performed with 5 U AluI (Invitrogen) for 4 h. Prior to the T-RFLP analysis, digests were purified with Sephadex ™ G-50 (Amersham, Buckinghamshire, UK). Labeled terminal-restriction fragments (T-RFs) were then detected by capillary electrophoresis using an ABI 3100 automatic DNA sequencer in the GeneScan mode. Five microliters of AluI-digested PCR products were mixed with 15 μL formamide (Applied Biosystems, Warrington, UK) and 0.3 μL internal size standard (500 ROXTM Size Standard, Applied Biosystems). Prior to analysis, samples were denatured at 92°C for 2 min and immediately chilled on ice. For data collection the GeneScan® analysis software packet (Version 3.7, Applied Biosystems) was used. The relative lengths of the T-RFs were determined by comparing them with the internal 500 ROXTM size standard. Genotyper 3.7 NT software (Applied Biosystems) was used to compile the electropherograms of each sample into numeric data. Both fragment length and peak height were used as parameters for profile comparison. All T-RFs with heights of ≥30 fluorescence units which were detected by the Genotyper software were included in the further analysis. Normalization of T-RFLP profiles was performed according to Dunbar et al. (2000). Finally, the values of peak heights of ≥30 fluorescence units of 114 normalized T-RFs with different fragment lengths were used for analysis of community patterns.
Cloning and sequence analysis
Clone libraries of amplified 16S rRNA genes were generated from the lines DC and DL from soil C, each line treated with and without Eca, at early flowering. PCR products of the three treatment replicates were pooled and purified using the QIAquick Gel Extraction Kit (Qiagen, Venlo, NL) according to the manufacturer's instructions. Purified amplicons were ligated into the TpCR 4-TOPO vector (Invitrogen). Escherichia coli strain DH5α-TlR (Invitrogen) was then transformed with the ligation products according to the manufacturer's instructions. Fifty colonies were randomly selected and transferred to a new medium for another 24 h incubation. Colonies were suspended in a reaction tube containing 50 μL TE buffer (pH 8.0), boiled for 10 min, chilled on ice to induce cell lysis, centrifuged for 10 min at 13 000 r.p.m., and the supernatant used for PCR. Clones were PCR-amplified by using the primers M13f and M13r. Amplicons were purified with Sephadex™ G-50 (Amersham) and used as templates for sequencing analysis. Partial sequencing of 16S rDNA was performed by applying the BigDye V3.1 Terminator-Kit (Applied Biosystems) and the reverse primer 518r (5′-ATTACCGCGGCTGCTGG-3′) (Liu et al., 1997), resulting in sequences of approximately 500 bp length. Clones were finally checked for chimaeric artifacts by using CHECK_CHIMERA of the Ribosomal Database Project and chimaeric sequences were discarded. Sequences were subjected to BLAST analysis with the National Center for Biotechnology Information (NCBI) database. To identify the 16S rRNA gene clones with the T-RFs in the corresponding T-RFLP fingerprint, clones were subjected to T-RFLP analysis as described above.
Nucleotide sequence accession numbers
The nucleotide sequences determined in this study have been deposited in the NCBI database under accession numbers AY834286 to AY834389.
Analysis of variance combined with post hoc Tukey-B tests (SPSS for Windows, version 11.7, SPSS Inc., Chicago, IL) was used to determine significant treatment effects on the enzyme activity and T-RFLP data sets. Enzyme activity values and the values of peak height of terminal restriction fragments were examined for significant differences in relation to soil type, plant genotype, vegetation stage and pathogen exposure. The T-RFLP data set was further subjected to discriminant analysis (i) to investigate differences between treatments, (ii) to identify important discriminating variables in both data sets and (iii) to test the treatment groupings for significant differences.
- Top of page
- Materials and methods
Comparison of the two soils (luvisol [soil L] and chernozem [soil C]) revealed highly significant differences between the activities of all selected enzyme activities (P<0.001) (Table 1). Enzymes involved in the C- and N-cycles (α-d-glucosidase, β-d-glucosidase, β-d-cellobiohydrolase, β-d-xylosidase, N-acetyl-β-d-glucosaminidase, leucine aminopeptidase) revealed higher activities in soil C than in soil L (Fig. 1). Phosphatase activity was higher in soil L than in soil C (Fig. 1).
|Soil type‡||Potato line‡||Vegetation stage‡||Pathogen exposure|
No significant differences were found between either type of genetic modification and their two corresponding wild-type lines grown on soil L (P<0.05). Nevertheless, enzyme activities tended to be higher in the rhizosphere of DL than in its nontransgenic counterpart DC (Fig. 1). In contrast, the activities were, except for β-d-cellobiohydrolase, lower in the rhizosphere of MT than in that of MC. The plant genotype had a more pronounced effect than the genetic modification (Fig. 1). Rhizosphere soil of line MC had generally higher enzyme activities than rhizosphere soil of line DC (Fig. 1). However, except for the activity of leucine aminopeptidase, these differences were not significant (P<0.05) (Table 1). In soil C, comparison of the transgenic (DL) and isogenic, wild-type plants (DC) revealed no consistent trend. Leucine aminopeptidase was significantly more active in the rhizosphere of DC than in that of DL (P<0.05). Similarly, higher activities of β-d-glucosidase, β-d-xylosidase, and α-d-glucosidase were found in the rhizosphere of DC. In contrast, N-acetyl-β-d-glucosaminidase, β-d-cellobiohydrolase, as well as phosphatase, were more active in the rhizospheres of line DL (Fig. 1). A comparison of MC with MT revealed lower, albeit not significantly, activities of all seven enzymes in association with MC (P<0.05) (Fig. 1). Leucine aminopeptidase was significantly more active in the rhizosphere of line DC than in the rhizosphere of line MC (P<0.05). A comparable, but not significant, tendency was found for α-d-glucosidase, β-d-cellobiohydrolase, β-d-xylosidase, and N-acetyl-β-d-glucosaminidase (P<0.05), whereas the activities of β-d-glucosidase and phosphatase were reduced in the rhizosphere of line DC (Fig. 1).
Vegetation stages influenced the enzyme activities in the rhizospheres of DC and DL cultivated on soil L. In particular, activities had a tendency to increase from stem elongation to early flowering. The largest differences were found for N-acetyl-β-d-glucosaminidase in the rhizosphere of line DC (P<0.05) and line DL (P=0.084), and for leucine aminopeptidase in the rhizosphere of line DC (P=0.098). In contrast, in association with DC and DL, β-d-cellobiohydrolase and leucine aminopeptidase showed decreased activities at the later vegetation stage. In the rhizosphere of MC, the activity of β-d-glucosidase, β-d-xylosidase, N-acetyl-β-d-glucosaminidase, and leucine aminopeptidase generally increased with time, whereas the activity of β-d-cellobiohydrolase (P=0.065), α-d-glucosidase and phosphatase decreased over the measurement period. In the rhizosphere of MT, all enzymes involved in the C- and N-cycles were less active at the early flowering stage, whereas with phosphatase a very slight increase over time was seen (Fig. 1). In soil C, all enzymes in the rhizospheres of line DC had a tendency to be more active at the early flowering stage than in the stem elongation stage; however, these differences were not significant (P<0.05). The opposite result was found for its transgenic derivative DL. Here, the greatest differences were measured for β-d-glucosidase (P<0.05), β-d-xylosidase (P<0.05) and βD-cellobiohydrolase (P=0.076). No consistent trend for an increase or a reduction in enzyme activities was detected in the rhizospheres associated with line MC. α-d-glucosidase, β-d-cellobiohydrolase, N-acetyl-β-d-glucosaminidase, and phosphatase tended to be less active, whereas the opposite was measured for β-d-glucosidase, and β-d-xylosidase. Only a minor change was determined for leucine aminopeptidase. In the rhizosphere of MT, a clear increase of all seven enzyme activities was measured, where the greatest differences were obtained for N-acetyl-β-d-glucosaminidase (P<0.01), β-d-xylosidase (P<0.01), leucine aminopeptidase (P<0.05), and α-d-glucosidase (P=0.08) (Fig. 1).
Pathogen exposure of Eca did not result in a change (increase or reduction) of any rhizosphere enzyme activities analyzed (P<0.05) (Table 1).
After normalization of T-RFLP profiles, a total of 114 terminal restriction fragments (T-RFs) with different fragment lengths were identified. In individual profiles, between 25 and 59 T-RFs were identified, with peak heights of at least 30 fluorescence units. The rhizosphere communities showed highly different community structures in relation to the two soils, luvisol and chernozem. In particular, 58 T-RFs significantly distinguished the microbial structure in the two soils, whereas 47 T-RFs were significantly affected by the potato lines (P<0.05) (Table 2). Comparison of the microbial community structures affected by pathogen exposure revealed 13 significantly different T-RFs, and the impact of vegetation stage was significant for seven T-RFs (P<0.05) (Table 2).
|T-RF size‡ (bp)||Significance level†||T-RF size‡ (bp)||Significance level†|
|Soil type§||Potato line§||Vegetation stage§||Pathogen exposure§||Soil type§||Potato line§||Vegetation stage§||Pathogen exposure§|
Comparison of community profiles was based on discriminant analysis of the T-RFLP data, which revealed distinct differences in the microbial community structure of the potato lines either infected or not infected with Eca. In all four cases (Fig. 2a–d), the first two discriminating functions were able to explain at least 90.5% of the total variance. The quality of the discriminating functions was confirmed by their high canonical correlations with the treatments, at least r=0.981. The capability of the discriminating functions to significantly discriminate the treatments was exemplified by a Wilks' lambda of at least P=0.040. The rhizospheres of the potato plants in soil L at stem elongation stage were clearly affected by the pathogen exposure, whereas the differences between the transgenic lines and their isogenic wild-types were only small (Fig. 2a). Only five T-RFs (38, 48, 153, 220 and 221 bp) were responsible for this treatment separation (P<0.05). The differences between the noninfected and infected plants were smaller after plants reached the early flowering stage (Fig. 2b). In particular, a difference was determined for both Desirée lines, DC and DL. Although the differences at early flowering were less pronounced than at the stem elongation stage, 25 T-RFs (36, 38–41, 47, 48, 54–59, 66, 70–74, 143, 155, 170, 175, 176 and 221 bp) were detected that could significantly discriminate the rhizospheres (P<0.05). In contrast to soil L, the differences in the microbial community structure in soil C became greater over time. At the stem elongation stage only small differences were found between the potato lines, either with or without infection, except for lines DC and MT (Fig. 2c). Analysis of variance revealed 25 significant, treatment-discriminating T-RFs (38–41, 43, 52, 56, 57, 60, 61, 66, 68, 70, 71, 73, 196, 197, 217, 228, 229, 231, 233, 237, 241 and 248 bp) (P<0.05). At early flowering, a more distinct effect of Eca infection was determined for lines DC, DL and MC, whereas the difference in the community composition of the transgenic line MT was less pronounced (Fig. 2d). When comparing conventional vs. transgenic lines, the differences between DC and DL were greater than the differences between MC and MT. Differences at the early flowering stage in soil C were due to 28 significant T-RFs (39–41, 46–48, 52–55, 58, 62, 67, 69–71, 74, 75, 157, 168, 196, 206, 226, 228, 231, 233, 247 and 248 bp) (P<0.05).
Analysis of clone libraries
In order to identify dominant rhizosphere-associated bacteria, 16S rRNA gene clone libraries were established and partial insert sequences determined. These clone libraries consisted of sequences derived from the lines DC and DL cultivated on the chernozem, each line treated with and without Eca, and sampled at early flowering. In total, 200 sequences were determined; however, for 96 sequences the presence of chimaeric sequences could not be excluded unambiguously. Most of the clearly nonchimaeric sequences showed at least 95% similarities to known sequences in the NCBI database, whereas 20% of the clones were only distantly (86–94%) related to known 16S rRNA genes (Tables 3 and 4). The majority of sequences fell into the divisions Holophaga/Acidobacterium (32–42%), high-G+C gram-positives (5–32%), Alphaproteobacteria (4–27%), Betaproteobacteria (3–18%) and Gammaproteobacteria (3–11%). The remaining clones with low numbers belonged to the divisions of Firmicutes, Deltaproteobacteria, green nonsulfur bacteria, Nitrospirae, Cytophaga/Flexibacter/Bacteroides (CFB), cyanobacteria and Planctomycetes. To identify clones corresponding to dominant T-RFs in the community profiles, clones were subjected to T-RFLP analysis. This was necessary as the actual T-RF lengths may differ from the theoretical, sequence-determined T-RF lengths. The drift ranged from 0 to 4 bases (Tables 3 and 4). In general, the results obtained by sequence analysis and by T-RFLP analysis were in good agreement. Bacteria belonging to the Holophaga/Acidobacterium division, the high-G+C gram-positives and Alphaproteobacteria were strongly represented in T-RFLP patterns by various fragments indicating a high abundance (Fig. 3). The 16S rRNA gene clone libraries indicated differences between wild-type lines and their transgenic counterparts as well as between Eca infection vs. noninfection, although to a certain extent highly similar sequences were found in different treatments. Nevertheless, the number of clones analyzed was far too small to allow any statistical analysis.
|Theoretical T-RF size (bp)||Actual T-RF size (bp)||Corresponding clone||Closest NCBI match (accession number)/% homology|
|66||64||cloRDC-48||Uncult. bact. clone BB-1-G5 (AY214743)/96|
|73||72||cloRDC-4||Uncult. bact. clone EB1028 (AY395347)/93|
|157||153||cloRDC-28||Uncult. bact. clone S52.42PG (AF431515)/97|
|199||202||cloRDC-9||Uncult. bact. clone BB-1-B5 (AY214783)/98|
|212||213||cloRDC-14||Uncult. bact. clone GR20 (AY150900)/97|
|227||230||cloRDC-13||Uncult. bact. clone Ellin6099 (AY234751)/96|
|248||248||cloRDC-42||Uncult. bact. clone W1H7 (AY632474)/95|
|249||248||cloRDC-1||Uncult. bact clone D114 (AY632474)/97|
|249||248||cloRDC-27||Uncult. bact. clone C1G1 (AY632456)/94|
|249||248||cloRDC-29||Uncult. bact. clone W1H7 (AY632474)/94|
|253||255||cloRDC-3||Uncult. bact. clone 39p18 (AY281355)/96|
|High-G+C gram positives|
|164||166||cloRDC-25||Uncult. bact. clone LBS3 (AJ232831)/98|
|197||196||cloRDC-7||Streptomyces sp. strain So54 (AJ308576)/99|
|203||206||cloRDC-2||Unknown soil bact. clone MC 66 (X68458)/97|
|203||206||cloRDC-6||Uncult. Conexibacter sp. clone ACTINO10 (AY494658)/95|
|204||206||cloRDC-43||Uncult. bact. clone z13 (AY235436)/98|
|204||206||cloRDC-17/37||Uncult. bact. clone z20 (AY235437)/94-96|
|204||206||cloRDC-36||Uncult. bact. clone SMS9.65WL (AY043905)/94|
|227||230||cloRDC-8||Uncult. bact. clone TBS1 (AJ005994)/97|
|234||234||cloRDC-18||Hongia sp. strain 337E05 (AB124350)/98|
|208||206||cloRDC-22||Porphyrobacter sp. strain MBIC3936 (AB022015)/97|
|208||206||cloRDC-16||Filumicrobium fusimore strain DSM 5304 (Y14313)/96|
|218/219||216||cloRDC-19/46/47||Uncult. bact. clone 597-1 (AY326608)/99|
|236||238||cloRDC-12||Uncult. bact. clone A21b (AF234707)/97|
|240||241||cloRDC-15||Xanthomonas sp. strain AK (AB016762)/97|
|Green non-sulphur bacteria|
|242||244||cloRDC-41||Uncult. Chloroflexus sp. clone glen99_19 (AY150877)/98|
|245||244||cloRDC-20||Uncult. bact. clone DSP16 (AJ290185)/95|
|154||153||cloRDC+2||Uncult. bact. clone S52.42PG (AF431515)/95|
|200||198||cloRDC+45||Uncult. bact. clone WYO1bC (AY150918)/97|
|200||198||cloRDC+10/9||Uncult. bact. clone C1C8 (AY632458)/95-97|
|249||248||cloRDC+13||Uncult. bact. clone glen99_7 (AY150876)/97|
|249||248||cloRDC+5/17||Uncult. bact. clone W1F9 (AY632472)/94|
|High-G+C gram positives|
|245||244||cloRDC+40||Pseudonocardia dioxanivorans strain CB1190 (AY340622)/100|
|141||140||cloRDC+8||Pseudomonas sp. strain G-179 (AF109171)/99|
|143||140||cloRDC+32||Uncult. bact. clone BB-1-H2 (AY214737)/99|
|206||206||cloRDC+11||Rhizobium sp. strain SX211 (AF345554)/99|
|208||206||cloRDC+12||Sphingomonas sp. strain HS380 (AY116887)/99|
|208||208||cloRDC+44||Sphingomonas sp. strain CD (AF191022)/98|
|272||273||cloRDC+37||Uncult. bact. clone BB-1-H2 (AY214737)/94|
|234||233||cloRDC+39||Schlegelella thermodepolymerans strain K14 (AY152824)/95|
|251||–||cloRDC+3||Uncult. bact. clone Ac40 (AF388318)/99|
|240||238||cloRDC+33||Uncult. Xanthomonas sp. clone Cl-106-TB4-II (AY599709)/94|
|221||222||cloRDC+29||Uncult. bact. clone ISCB-16 (AY596128)/93|
|Green non-sulphur bacteria|
|263||264||cloRDC+21||Uncult. Chloroflexus clone NMW3.41WL (AY043952)/86|
|162||161||cloRDC+47||Uncult. bact. clone Mul1P2-8 (AJ518176)/97|
|73||71||cloRDC+42||Bacillus niacini strain IFO15566 (AB021194)/98|
|110||–||cloRDC+23||Nodularia spumigena strain UTEX-B2092 (AF268022)/96|
|Theoretical T-RF size (bp)||Actual T-RF size (bp)||Corresponding clone||Closest NCBI match (accession number)/% homology|
|200||197||cloRDL-4||Uncult. bact. clone WYO1bC (AY150918)/97|
|200||197||cloRDL-30||Uncult. bact. clone LBD5 (AF392742)/97|
|200||197||closRDL-32||Uncult. bact. clone C1C8 (AY632458)/97|
|230||—||cloRDL-21||Uncult. bact. clone W1C8 (AF010071)/94|
|237||236||cloRDL-42||Uncult. bact. clone Ac62 (AF388354)/92|
|238||236||cloRDL-46/17||Uncult. bact. clone BB-2-H5 (AY214798)/95-98|
|246||248||cloRDL-14||Uncult. bact. clone glen99_24 (AY150886)/89|
|249||248||cloRDL-40||Uncult. bact. clone Ac69 (AF388349)/98|
|249||248||cloRDL-29||Uncult. bact. clone GR20 (AY150900)/94|
|High-G+C gram positives|
|72 bp||72||cloRDL-39||Agromyces fucosus strain VKM Ac-1352 T (AY158025)/99|
|239 bp||236||cloRDL-45||Cellulomonas cellasea strain DSM 20118 T (X83804)/99|
|241 bp||245||cloRDL-22||Uncult. bact. clone 1267-1 (AY326533)/95|
|208||206||cloRDL-10||Uncult. bact. clone N27.63SM (AF431139)/100|
|208||206||cloRDL-16||Sphingomonas sp. strain SAFR-028 (AY167833)/98|
|210||206||cloRDL-28||Bradyrhizobium sp. strain Shinsu-th2 (AB121773)/99|
|232||232||cloRDL-43||Uncult. bact. clone W1A8 (AY632488)/98|
|233||232||cloRDL-31/33||Uncult. bact. clone Ellin6067 (AY234719)/99|
|233||232||cloRDL-1||Uncult. bact. clone O10R (AY395217)/97|
|233||232||cloRDL-19||Uncult. bact. clone Spb153 (AJ422165)/97|
|75||78||cloRDL-44||Uncult. bact. clone LTUG07956 (AY144258)/97|
|234||236||cloRDL-24||Uncult. bact. clone BB-1-H3 (AY214736)/99|
|234||236||cloRDL-37||Uncult. bact. clone WCB153 (AY217478)/99|
|217||217||cloRDL-25||Uncult. bact. clone LBE10 (AF392699)/90|
|75||78||cloRDL-47||Sporosarcina sp. strain GIC9 (AY439261)/97|
|Green non-sulphur bacteria|
|243||245||cloRDL-3||Uncult. Chloroflexus sp. clone glen99_19 (AY150877)/98|
|59||59||cloRDL-9||Uncult. bact. clone 40 (AF271331)/96|
|153||153||cloRDL+7||Uncult. bact. clone D131 (AY274137)/94|
|155||154||cloRDL+4||Uncult. bact. clone SIMO-2043 (AY711409)/96|
|155||154||cloRDL+2||Uncult. bact. clone EB1071 (AY395390)/95|
|198||197||cloRDL+12||Uncult. bact. clone DA023 (Y07586)/94|
|200||197||cloRDL+50||Uncult. bact. clone BB-1-B5 (AY214783)/97|
|222||223||cloRDL+23||Uncult. bact. clone Cart-N4 (AY118153)/93|
|249||249||cloRDL+19||Uncult. bact. clone SL2-1-A9 (AY214662)/99|
|249||249||cloRDL+34||Uncult. bact. clone W1F9 (AY632472)/97|
|250||249||cloRDL+28||Uncult. bact. clone SL2-1-A6 (AY214664)/96|
|259||249||cloRDL+43||Uncult. bact. clone 32d1 (AY281353)/97|
|High-G+C gram positives|
|72||72||cloRDL+37||Uncult. bact. clone Ellin5069 (AY234486)/99|
|72||72||cloRDL+48||Arthrobacter sp. strain pfB3 (AY336532)/99|
|151||153||cloRDL+11||Uncult. bact. clone uvel24 (AY186870)/98|
|197||197||cloRDL+29||Streptomyces sp. strain So54 (AJ308576)/99|
|153||153||cloRDL+46||Uncult. bact. clone ccspost211 (AY133099)/96|
|234||233||cloRDL+31||Uncult. bact. clone t032 (AF422603)/98|
|234||233||cloRDL+5||Uncult. bact. clone BCM3S-5B (AY102911)/97|
|236||236||cloRDL+44||Uncult. bact. clone WCB200 (AY217470)/96|
|240||–||cloRDL+24||Uncult. bact. clone BAC-II-3A-P27 (AY214907)/97|
|Green non-sulphur bacteria|
|243||245||cloRDL+27||Uncult. bact. clone CCD4 (AY221037)/97|
|243||245||cloRDL+32||Uncult. Chloroflexus sp. clone glen99_19 (AY150877)/96|
|223||223||cloRDL+20||Uncult. bact. clone PeM12 (AJ576382)/95|
|204||207||cloRDL+49||Uncult. bact. clone CD21F11 (AY145665)/96|
|199||197||cloRDL+15||Uncult. Nitrospira sp. clone HAuD-UB28 (AB113588)/94|
- Top of page
- Materials and methods
The plant rhizosphere is a dynamic environment in which many parameters may influence the activity and population structure of the microbial communities living on and in the vicinity of roots. The objective of this study was to investigate the potential harmful effect of genetically modified potatoes producing antibacterial substances on functional and structural characteristics of microbial communities associated with potato roots and to compare these modification-related variations with natural factors such as soil type, plant genotype, vegetation stage and bacterial pathogen stress. For this purpose, we measured the activity of extracellular catabolic enzymes responsible for important soil functions and evaluated structural community fingerprints based on 16S rRNA gene differences. Our results demonstrated that rhizosphere microbial communities were clearly affected by the specific characteristics of each individual factor. However, the extent of impact differed greatly.
It has been suggested that the genetic modification of plants could induce a transformation-specific exudation pattern which may be different from that of the nearly isogenic wild-type lines (Donegan et al., 1999; Dunfield & Germida, 2001; Gyamfi et al., 2002; Sessitsch et al., 2003). In the case of plants producing attacin/cecropin or T4-lysozyme, a change of the exudation pattern could have been due either to a qualitatively and/or a quantitatively altered excretion of organic compounds, or to the release of the produced antibacterial substances. However, detailed analysis of the root exudates of the different plant genotypes used in the present study would be required for confirmation. A direct effect of potentially released antibacterial compounds on rhizosphere microbial communities is difficult to prove. In the attacin/ceropin-producing transgenic potato line, due to the genetic construct used, the peptides are supposed to remain within the plant cell. Thus, a release of the antimicrobial compounds from the roots into the rhizosphere would follow the discharge of dead root cells into the soil matrix. However, this speculation about a subsequent microbial cell killing effect in the rhizosphere has to be treated with care as it is known that freely occurring peptides such as cecropin are very susceptible to rapid enzymatic degradation (Maria Berenyi, unpublished data). In contrast to the cecropin/attacin modification, it can be assumed that due to the fusion of the α-amylase leader peptide, T4 lysozyme is transported to the intercellular space (apoplast). This essential difference probably advances the release of the T4 lysozyme from the root into the soil matrix by diffusion (de Vries et al., 1999). This difference may at least partly explain the greater impact on the rhizosphere microflora due to the insertion of the T4 lysozyme genes than due to the insertion of cecropin and attacin genes. Furthermore, T4 lysozyme potatoes showed a higher resistance level towards the pathogen than cecropin/attacin potatoes did. Ahrenholtz et al. (2000) and de Vries et al. (1999) detected bactericidal effects on rhizosphere microbial populations after the release of T4 lysozyme into the soil matrix surrounding the roots. In contrast, Lottmann et al. (2000) could not find a negative effect of T4 lysozyme-producing potatoes on the associated microbial community, suggesting that the microbial community was able to tolerate or adapt to the presence of T4 lysozyme. In this study, the shifts in the microbial community structure and the change of microbial activities due to the genetic modification were minor compared with the effects of the other factors analyzed. This confirms the findings of Heuer et al. (2002), who compared a potential T4 lysozyme effect on genetic characteristics of rhizosphere bacterial communities with seasonal and field effects. In that study the authors concluded that the impact due to genetic modification was negligible compared to the natural variation.
The two soils had the most pronounced contrasting effect on the activity and community structure rhizosphere microflora. This was not surprising, as the two soils used in this study differed greatly in physical and chemical properties. Earlier studies showed that the soil type and texture may significantly affect the activity and community structure of the soil microflora (Bossio et al., 1998; Kandeler et al., 2000; Sessitsch et al., 2001; Girvan et al., 2003; Blackwood & Paul, 2003). The availability and amount of organic carbon in soils is a key factor influencing the activity and structure of the microbial communities (Buyer et al., 1999; Degens et al., 2000). In this study, increased activities of enzymes involved in the carbon cycle were found in the chernozem soil, which had an organic carbon content three times higher than the luvisol soil. This observation is in accordance with an earlier study by Gerzabek et al. (2002), in which the activities of the same or related enzymes correlated with the organic matter content of soils of a long-term field experiment. Similarly, different soil organic carbon contents were found to alter microbial community structures (Sessitsch et al., 2001; Girvan et al., 2003). The pH value is a central determinant of soil microbial activity and population structure (Gerzabek et al., 2002). The higher pH value in the chernozem soil might explain the higher enzyme activities found in this study. The influence of pH on soil microbial activities was also observed by Ellis et al. (2001) and Knight et al. (1997), who investigated metabolic properties of microbial communities in heavy metal-contaminated soils. Kowalchuk et al. (2000) found pH-dependent variations in the community structure of chemolitho-autotrophic ammonia-oxidizing bacteria. In forest soils, pH was identified as a key parameter driving the composition of the microbial community (Buyer et al., 1999; Hackl et al., 2004).
Apart from the obvious soil effect, the plant genotype contributed to the differentiation in the enzyme activity rates and community fingerprints of the rhizosphere microflora. These differences may have been due to plant-specific root exudation patterns that lead to specific responses of the associated microbial communities (Grayston et al., 1998; Kandeler et al., 2002; Paterson, 2003; Jones et al., 2004). The assumption that different root exudation patterns were responsible for the varying functional and structural characteristics of bacteria in the rhizosphere of the potato lines analyzed in this study was further supported by Söderberg et al. (2002) and Marschner et al. (2001).
The developmental stage of the potato plants affected the functional and structural characteristics of the associated rhizosphere microbial community. The consequence of this age-dependent alteration might lead to the variations seen in the rhizosphere microbial communities. Jones et al. (2004) stated that the different stages of a plant growth cycle are accompanied by a change in the amount and chemical composition of root exudates. Evidence for this was found in the different enzyme activity rates and altered community fingerprint profiles of the two sampling dates at stem elongation and early flowering stage, respectively. These findings were in accordance with previous reports by Schmalenberger & Tebbe (2002) and Gyamfi et al. (2002).
An interesting observation was the effect of pathogen exposure on the microbial community composition in the rhizosphere. As the pathogen was found in stems, competition effects due to the presence of the pathogen in the rhizosphere are unlikely. We assume that the infection with the blackleg pathogen E. carotovora ssp. atroseptica caused alterations in plant physiology leading to qualitative and quantitative changes of root exudation patterns. These changes were probably responsible for the slightly altered microbial communities. Neumann & Römheld (2001) reported that biotic stress (e.g. due to pathogen attack) may change the rate of root exudation as a result of loss of membrane integrity or a breakdown in normal cell metabolism. Filion et al. (2004) examined soil microbial communities related to root rot diseased and healthy Picea mariana seedlings applying diversity and phylogenetic analyses. Their results supported the hypothesis that microbial communities could be affected by the appearance of a certain disease. Yang et al. (2001) detected significant changes in bacterial communities associated with healthy and Phytophthora-infected avocado roots by 16S rRNA fingerprinting. Similarly, McSpadden Gardener & Weller (2001) found altered microbial community structures in the rhizosphere of diseased wheat plants, which were infected with Gaeumannomyces graminis var. tritici, in comparison with healthy plants.
- Top of page
- Materials and methods
In summary, our experimental setup, the greenhouse experiment combined with enzyme activity measurements and T-RFLP analysis, was well suited to demonstrate that soil type, plant variety, genetic modification, vegetation stage and pathogen exposure are important parameters affecting the activity and structure of rhizosphere microbial communities. Our results indicated effects of the genetic modification on the activity and structure of bacterial rhizosphere populations. However, these differences were in part only transient and minor or comparable to the variations caused by the other factors analyzed in this study. Our results have shown that the function and structure of the investigated microbial communities are strongly influenced by interactions between the analyzed factors. The extent of the impact caused by the plant variety was strongly dependent on the soil type, which simulated two different growth habitats. Furthermore, the effect of the plant variety on the microbial community depended on the plant developmental stage. Similarly, the impact of the pathogen E. carotovora ssp. atroseptica varied with the variety and age of the plant. The importance of such interactions has been noticed formerly by other groups (Dunfield & Germida, 2001; Marschner et al., 2001; Wieland et al., 2001). We would point out that complex ecosystematic networks have to be considered and that the impact of the individual parameters tested in this study may be different under different conditions. Generally, a better understanding of the complex interactions between soil, plants and microorganisms is still required. This can serve as a baseline to evaluate the actual ecological impact of GM crops.
- Top of page
- Materials and methods
This study was financially supported by the European Union project ‘potatocontrol’ (QLK3-2000-01598). We are grateful to Dr Leo van Overbeek (PRI, Wageningen, The Netherlands) for providing Erwinia carotovora ssp. atroseptica strain IPO161, and Jan van de Haar (HZPC Research, Metslawier, The Netherlands) for offering potato tubers. We thank Dr Levente Bodrossy for his valuable comments on the manuscript.
- Top of page
- Materials and methods
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