Plant Biol (Stuttg) 2005; 7(6): 728-736
DOI: 10.1055/s-2005-872987
Research Paper

Georg Thieme Verlag Stuttgart KG · New York

Short Term Effects of Ozone on the Plant-Rhizosphere-Bulk Soil System of Young Beech Trees

M. Schloter1 , J. B. Winkler2 , M. Aneja1 , N. Koch3 , F. Fleischmann4 , K. Pritsch5 , W. Heller6 , S. Stich6 , T. E. E. Grams3 , A. Göttlein7 , R. Matyssek3 , J. C. Munch1
  • 1Institute of Soil Ecology, GSF - National Research Center for Environment and Health, Ingolstädter Landstraße 1, 85764 Neuherberg, Germany
  • 2Institute of Soil Ecology, Department of Environmental Engineering, GSF - National Research Center for Environment and Health, Ingolstädter Landstraße 1, 85764 Neuherberg, Germany
  • 3Ecophysiology of Plants, Technische Universität München, Am Hochanger 13, 85354 Freising, Germany
  • 4Section Pathology of Woody Plants, Technische Universität München, Am Hochanger 13, 85354 Freising, Germany
  • 5Soil Ecology, Technische Universität München, Ingolstädter Landstraße 1, 85758 Oberschleißheim, Germany
  • 6Institute of Biochemical Plant Pathology, GSF - National Research Center for Environment and Health, Ingolstädter Landstraße 1, 85764 Neuherberg, Germany
  • 7Plant Nutrition and Water Ressources, Technische Universität München, Am Hochanger 13, 85354 Freising, Germany
Further Information

Publication History

Received: October 5, 2005

Accepted: October 12, 2005

Publication Date:
17 February 2006 (online)

Abstract

Plant growth largely depends on microbial community structure and function in the rhizosphere. In turn, microbial communities in the rhizosphere rely on carbohydrates provided by the host plant. This paper presents the first study on ozone effects in the plant-rhizosphere-bulk soil system of 4-year-old beech trees using outdoor lysimeters as a research platform. The lysimeters were filled with homogenized soil from the corresponding horizons of a forest site, thus minimizing field heterogeneity. Four lysimeters were treated with ambient ozone (1 × O3) and four with double ambient ozone concentrations (2 × O3; restricted to 150 ppb). In contrast to senescence, which was almost unaffected by ozone treatment, both the photochemical quantum yield of photosystem II (PSII) and leaf gas exchange were reduced (11 - 45 %) under the elevated O3 regime. However, due to large variation between the plants, no statistically significant O3 effect was found. Even though the amount of primary metabolites, such as sugar and starch, was not influenced by elevated O3 concentrations, the reduced photosynthetic performance was reflected in leaf biochemistry in the form of a reduction in soluble phenolic metabolites. The rhizosphere microbial community also responded to the O3 treatment. Both community structure and function were affected, with a tendency towards a lower diversity and a significant reduction in the potential nutrient turnover. In contrast, litter degradation was unaffected by the fumigation, indicating that in situ microbial functionality of the bulk soil did not change.

References

  • 1 Andersen C. P.. Source-sink balance and carbon allocation below ground in plants exposed to ozone.  New Phytologist. (2003);  157 213-228
  • 2 Aneja M., Sharma S., Munch J. C., Schloter M.. RNA fingerprinting - a new method to screen for differences in plant litter degrading microbial communities.  Journal of Microbiological Methods. (2004);  59 223-231
  • 31 Bahnweg G., Heller W., Stich S., Knappe C., Betz G., Heerdt C., Kehr R. D., Ernst D., Langebartels C., Nunn A. J., Rothenburger J., Schubert R., Wallis P., Müller-Starck G., Werner H., Matyssek R., Sandermann Jr. H.. Beech leaf colonization by the endophyte Apiognomonia errabunda dramatically depends on light exposure and climatic conditions.  Plant Biology. (2005);  7 659-669
  • 3 Baudoin E., Benizri E., Guckert A.. Impact of growth stage on the bacterial community structure along maize roots, as determined by metabolic and genetic fingerprinting.  Applied Soil Ecology. (2002);  19 135-145
  • 5 Bortier K., DeTemmermann L., Ceulemanns R.. Effects of ozone exposure in open top chambers on poplar (Populus nigra) and beech (Fagus sylvatica): a comparison.  Environmental Pollution. (2000);  109 509-516
  • 6 Braun S., Zugmaier U., Thomas V., Flückiger W.. Carbohydrate concentrations in different plant parts of young beech and spruce along a gradient of ozone pollution.  Atmospheric Environment. (2004);  38 2399-2407
  • 8 Cairney J., Meharg A.. Influences of anthropogenic pollution on mycorrhizal fungal communities.  Environmental Pollution. (1999);  106 169-182
  • 9 Dixon M., LeThiec D., Garrec J. P.. Reactions of Norway spruce and beech trees to 2 years of ozone exposure and episodic drought.  Environmental and Experimental Botany. (1998);  40 77-91
  • 10 Fleischmann F., Schneider D., Matyssek R., Oßwald W.. Investigations on net CO2 assimilation, transpiration and root growth of Fagus sylvatica infested with four different Phytophthora species.  Plant Biology. (2002);  4 144-152
  • 11 Gregory R., Cawthray A.. An improved reversed-phase liquid chromatographic method for the analysis of low-molecular mass organic acids in plant root exudates.  Journal of Chromatography A. (2003);  1011 233-240
  • 12 Heukeshoven J., Dernick R.. Neue Ergebnisse zum Mechanismus der Silberfärbung. Radola, B. J., ed. Electrophorese Forum' 86. Munich; Technische Universität München (1986): 22-27
  • 13 Lehtola M., Miettinen I., Vartiainen T., Myllykangas T., Martikainen P.. Microbially available organic carbon, phosphorus and microbial growth in ozonated drinking water.  Water Research. (2001);  35 1635-1640
  • 14 Loranger G., Pregitzer K., King J. S.. Elevated CO2 and O3 concentrations differentially affect selected groups of the fauna in temperate forest soils.  Soil Biology and Biochemistry. (2004);  36 1521-1524
  • 15 Manning W., Tiedemann A.. Climate change: potential effects of increased atmospheric carbon dioxide, ozone and ultraviolet-B radiation on plant diseases.  Environmental Pollution. (1995);  33 219-245
  • 17 McCrady J., Andersen G.. The effect of ozone on belowground carbon allocation in wheat.  Environmental Pollution. (2000);  107 465-472
  • 18 Nautiyal C. S., Bhadauria S., Kumar P., Lal H., Mondal R., Verma D.. Stress induced phosphate solubilization in bacteria isolated from alkaline soils.  FEMS Microbial Letters. (2000);  182 291-296
  • 19 Olszyk D., Johnson M., Phillips D. L., Deidler R. J., Tingey D. T., Watrud L.. Interactive effects of CO2 and O3 on a ponderosa pine plant/litter/soil mesocosm.  Environmental Pollution. (2001);  115 447-462
  • 20 O'Connell K., Goodman R., Handelsman J.. Engineering the rhizosphere: expressing a bias.  Trends in Biotechnology. (1996);  14 83-88
  • 21 Personeni E., Loiseau P.. Species strategy and N fluxes in grassland soil: a question of root litter quality or rhizosphere activity?.  European Journal of Agronomy. (2005);  22 217-229
  • 22 Pritsch K., Luedemann G., Matyssek R., Hartmann A., Schloter M., Scherb H., Grams T. E. E.. Mycorrhizosphere responsiveness to atmospheric ozone and inoculation with Phytophthora citricola in a phytotron experiment with spruce/beech mixed cultures.  Plant Biology. (2005);  7 718-727
  • 23 Reddy G. B., Reiner R. A., Eason G.. Loblolly pine needle nutrient and soil enzyme activity as influenced by ozone and acid rain chemistry.  Soil Biology and Biochemistry. (1995);  27 1059-1064
  • 24 Rees R., Bingham I., Baddeley J., Watson C. A.. The role of plants and land management in sequestering soil carbon in temperate arable and grassland ecosystems.  Geoderma. (2005);  in press
  • 32 Sandermann H., Matyssek R.. Scaling up from molecular to ecological processes.  Molecular Ecological Studies. (2003);  170 in press
  • 25 Sandnes A., Eldhuset T., Wollebæk G.. Organic acids in root exudates and soil solution of Norway spruce and silver birch.  Soil Biology and Biochemistry. (2005);  37 259-269
  • 26 Sariyildiz T., Anderson J. M.. Variation in the chemical composition of green leaves and leaf litters from three deciduous tree species growing on different soil types.  Forest Ecology and Management. (2005);  210 303-319
  • 27 Sylvia D., Chellemi D.. Interactions among root-inhabiting fungi and their implications for biological control of root pathogens. Sylvia, D., ed. Advances in Agronomy. New York; Academic Press (2001): 1-33
  • 28 Tiquia S. M., Lloyd J., Herms D. A., Hoitink J., Michel F.. Effects of mulching and fertilization on soil nutrients, microbial activity and rhizosphere bacterial community structure determined by analysis of TRFLPs of PCR-amplified 16S rRNA genes.  Applied Soil Ecology. (2002);  21 31-48
  • 29 Turunen M., Heller W., Stich S., Sandermann H., Sutinen M. L., Norokorpi Y.. The effects of UV exclusion on the soluble phenolics of young Scots pine seedlings in the subarctic.  Environmental Pollution. (1999);  106 219-228
  • 30 Zagal E., Bjarnason S., Olsson U.. Carbon and nitrogen in the root zone of barley (Hordeum vulgare L.) supplied with nitrogen fertilizer at two rates.  Plant and Soil. (1993);  157 51-63

M. Schloter

Institute of Soil Ecology
GSF - National Research Center for Environment and Health

Ingolstädter Landstraße 1

85764 Neuherberg

Germany

Email: schloter@gsf.de

Editor: H. Rennenberg