COMPARISON OF RHIZOSPHERE MICROBIAL COMMUNITIES OF PARENTAL AND TRANSGENIC ALFALFA BY COMMUNITY-LEVEL METABOLIC (BIOLOG) AND MOLECULAR (ERIC-PCR) ANALYSES
G.D. Di Giovanni1 L.S. Watrud2 F. Widmer1 W.G. Landis3 G. Mobus3 and R.J. Seidler3
1National Research Council Research Associate, US EPA NHEERL-WED; 2US EPA NHEERL-WED, 200 SW 35th Street, Corvallis, OR; 3Western Washington University, Bellingham, WA
SUMMARY
Current advances in biotechnology have allowed the construction of genetically engineered plants possessing novel and useful characteristics for applications such as crop protection, phytoremediation of polluted soils and production of specialty chemicals. Commercial development and field testing of engineered plants is far exceeding the knowledge of the potential ecological effects of their introduction into the environment (Krattiger, 1994). Concerns regarding the effects of transgenic plant introductions on soil and rhizosphere microorganisms have been raised by the scientific community (Seidler and Levin, 1994; Donegan et al, 1995). In addition, a more thorough understanding of rhizosphere microbial communities has been identified as a research need by a recent workshop on phytoremediation (U.S. DOE, 1994). A particular area of need is in the understanding of plant-microbe interactions. We have developed a novel approach to rhizosphere microbial community analysis using two of the most promising new techniques in microbial ecology, community metabolic profiles and community DNA fingerprinting. This study describes the application of this new methodology for evaluation and characterization of rhizosphere microbial communities of parental and transgenic alfalfa.
A new approach to the characterization of microbial communities based on communitylevel sole-carbon-source utilization patterns was reported by Garland and Mills (1991). The authors used Biolog Gram negative (GN) microplates (Biolog, Inc., Hayward, CA) inoculated with soil bacterial extracts of environmental samples to generate "metabolic fingerprints" of microbial communities. Substrate utilization patterns can then be used as indicators of the metabolic potential, genetic diversity and species diversity of microbial communities.
A recently developed molecular technique in microbial ecology relies on the amplification of enterobacterial repetitive intergeneric consensus (ERIC) DNA sequences by the polymerase chain reaction to fingerprint soil bacteria (De Bruijn, 1992). ERIC-PCR generates multiple distinct amplification products of sizes ranging from approximately 100 to 3,000 bp. Until this study ERIC-PCR has only been used to fingerprint pure cultures. We present its use in fingerprinting pure cultures, defined mixtures of microbes and rhizosphere microbial communities of environmental samples.
For this study isogenic strains of a parental and two transgenic alfalfa were used. The two transgenic strains express fungal genes for Mn dependent lignin peroxidase and bacterial genes for alpha amylase respectively (Austin et al, 1995). Community-level metabolic analysis detected subtle differences between the rhizosphere microbial communities of the parental (P), alpha amylase (AA) and lignin peroxidase (LP) alfalfa strains. Similarity analysis of the rhizosphere microbial community metabolic fingerprints demonstrated clustering based on genotype. Binarypattern comparison and multivariate analysis identified several significant substrates which can be used to differentiate the rhizosphere communities.
ERIC-PCR was used to fingerprint DNA extracted from the microbial consortia (elective cultures) present in the Biolog substrate wells. These DNA fingerprints were used to characterize and compare specific heterotrophic populations of the alfalfa rhizosphere communities. ERIC-PCR screening of bacterial colonies obtained from the Biolog elective cultures allowed the isolation and identification of several key species associated with the alfalfa strains. Use of this new methodology will enable us to better characterize plant-microbe relationships and to identify potential interactions between microbial populations in the rhizosphere.
REFERENCES
Austin, S., E.T. Bingham, D.E. Matthews, M.N. Shahan, J. Will and R.R. Burgess. 1995. Production and field performance of transgenic alfalfa (Medicago sativa L.) expressing alphaamylase and manganese-dependent lignin peroxidase. Euphytica 85:381-393.
De Bruijn, F. J. 1992. Use of repetitive (repetitive extragenic palindromic and enterobacterial repetitive intergeneric consensus) sequences and the polymerase chain reaction to fingerprint the genomes of Rhizobium meliloti isolates and other soil bacteria. Appl. Environ. Microbiol. 58:2180-2187.
Donegan, K. K., C. J. Palm, V. J. Ficland, L. A. Porteous, L. M. Ganio, D. L. Schaller, L. 0. Bucao and R. J. Seidler. 1995a. Changes in levels, species and DNA fingerprints of soil microorganisms associated with cotton expressing the Bacillus thuringiensis var. kurstaki endotoxin. Appl. Soil Ecol. 2:111-24.
Garland, J. L. and A. L. Mills. 1991. Classification and characterization of heterotrophic microbial communities on the basis of patterns of community-level sole-carbon-source-utilization. Appl. Envir. Microbiol. 57:2351-2359.
Krattiger, A. F. 1994. The field testing and commercialization of genetically modified plants: A review of worldwide data (1986 to 1993/94) In Biosafety for a Sustainable Agriculture: Sharing Biotechnology Regulatory Experiences of the Western Hemisphere (Krattiger, A. F. And A. Rosemarin, eds.), pp. 247-266. ISAA, Ithaca and Stockholm.
Seidler, R. J. And M. Levin. 1994. Potential ecological and non-target effects of transgenic plant gene products on agriculture, silviculture and natural ecosystems: general introduction. Molecular Ecol. 3:1-3.
U.S. DOE. 1994. Summary Report of a Workshop on Phytoremediation Research Needs. DOE/EM-0224. Washington, D.C.