Growth patterns of the alien perennial Bunias orientalis L. (Brassicaceae) underlying its rising dominance in some native plant assemblages

The polycarpic perennial Bunias orientalis L. (Brassicaceae) introduced to Central Europe in the 18th century recently entered a phase of rapid spread accompanied by sudden establishments of extensive dominance stands mainly on roadside locations. We studied vegetation structure and expansion rate of B. orientalis stands and performed a series of experiments to investigate key factors that underlie the colonizing and establishment of B. orientalis. Reiterated observations exposed a high current expansion rate of B. orientalis populations and vegetation surveys of B. orientalis stands showed that these stands were mainly composed of Artemisietea and Arrhenateretea species. Regeneration experiments with root fragments revealed high regeneration capacities: root fragments of 3 cm length showed 93% regeneration, varying water content (10–50% water loss) and separation into root cortex and root stele yielded regeneration of 30 to 50%. In a field study high regrowth after mowing with varying mowing intensity indicates B. orientalis to be well adapted to disturbed sites as its preferential locations for development of dominance stands. Vegetative growth parameters were studied in two controlled growth experiments with elevated nutrient availabilities. B. orientalis exhibited a high sensitivity to nutrient addition and rosette sizes of maximal 90 cm were reached. Biomass was comparable or even higher than that of native ruderals grown in the same experiment. Measurements of reproductive parameters revealed a high reproductive effort (0.2 to 0.45 g g-1) even under intense mowing regimes, resulting in a dense seed bank with maximal values of about 400 fruits (≅550 seeds) l-1 soil. With respect to colonization and establishment of B. orientalis the results of our study enable the formulation of three hypotheses.

[1]  H. Heilmeier,et al.  Nitrogen and carbohydrate storage in biennials originating from habitats of different resource availability , 1993, Oecologia.

[2]  Harold A. Mooney,et al.  Ecology of Biological Invasions of North America and Hawaii , 1986, Ecological Studies.

[3]  E. Jäger Möglichkeiten der Prognose synanthroper Pflanzenausbreitungen) , 1988 .

[4]  A. Rouw The invasion of Chromolaena odorata (L.) King & Robinson (ex Eupatorium odoratum), and competition with the native flora, in a rain forest zone, south-west Côte d'Ivoire , 1991 .

[5]  Marcel Rejmánek,et al.  Invasibility of plant communities , 1989 .

[6]  James A. Drake,et al.  Biological invasions : a global perspective , 1989 .

[7]  Michael J. Crawley,et al.  Seed limitation and the dynamics of feral oilseed rape on the M25 motorway , 1995, Proceedings of the Royal Society of London. Series B: Biological Sciences.

[8]  H. G. Baker,et al.  The Evolution of Weeds , 1974 .

[9]  Roderick Hunt,et al.  Relative growth-rate: its range and adaptive significance in a local flora. , 1975 .

[10]  H. G. Baker Patterns of Plant Invasion in North America , 1986 .

[11]  H. Ellenberg,et al.  Vegetation Mitteleuropas mit den Alpen , 1984 .

[12]  F. Bazzaz Life History of Colonizing Plants: Some Demographic, Genetic, and Physiological Features , 1986 .

[13]  E. Oberdorfer Pflanzensoziologische Exkursionsflora für Süddeutschland und die angrenzenden Gebiete , 1951 .

[14]  J. Andel,et al.  REPRODUCTIVE ALLOCATION IN PLANTS OF SCROPHULARIA-NODOSA GROWN AT VARIOUS LEVELS OF IRRADIANCE AND SOIL FERTILITY , 1990 .

[15]  P. B. Cavers,et al.  REPRODUCTIVE EFFORT OF TWO PERENNIAL WEED SPECIES IN DIFFERENT HABITATS , 1980 .

[16]  R. Hunt Plant growth analysis , 1980 .

[17]  J. Roy In search of the characteristics of plant invaders , 1990 .