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Brief Communications |
2UFZ-Centre for Environmental Research Leipzig-Halle, Ltd., Department of Community Ecology, Theodor-Lieser-Strasse 4, D-06120 Halle (Saale), Germany; 3Institut für Umweltwissenschaften, Universität Zürich, Winterthurerstrasse 190, CH-8057 Zürich, Switzerland
Received for publication April 25, 2003. Accepted for publication September 12, 2003.
| ABSTRACT |
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Key Words: allelopathy biological invasion competition garlic mustard Geum laciniatum Geum urbanum
| INTRODUCTION |
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Allelopathic interference must be species-specific to explain why nonindigenous species dominate an invaded community while they normally do not reach high dominance in their native community. It is possible that co-occurring species adapt to allelochemicals released by competitors; hence, it might be difficult to find pronounced effects in established communities (Harper, 1977
). Invasive species, however, do not share a coevolutionary history with the community they invade, and one might therefore expect greater allelopathic effects in such systems. However, only a few studies compared the allelopathic effects of an invasive species on competitors from the native and the invaded range. Callaway and Aschehoug (2000)
found that the outcome of competition between the invasive Centaurea diffusa and grass species from the new and the old range depended on whether or not activated carbon reduced allelopathic interference among them. To our knowledge, no one has ever tested the possibility that the degree of allelopathy of an invader may change as a result of encountering new competitors.
Garlic mustard [Alliaria petiolata (Bieb.) Cavara & Grande (Brassicaceae)] is a biennial (and sometimes perennial) species native to Europe that was introduced to North America in the middle of the 19th century. In the last few decades it started to expand rapidly its range and has invaded the understory of mesic forests in the northern United States and in southern Canada (Nuzzo, 1999
). Garlic mustard reduces the abundance of native species and decreases diversity in its new range in North America because of its high competitive ability (McCarthy, 1997
; Meekins and McCarthy, 1999
; B. Blossey, Cornell University, personal communication). In addition, a number of putative allelopathic chemicals have been isolated (glucosinolates and their degradation products) that could be responsible for the success of garlic mustard (Vaughn and Berhow, 1999
; but see also McCarthy and Hanson, 1998
).
Here, we tested for allelopathic inhibition of germination through the presence of garlic mustard in two congeneric competitor species. Geum urbanum is a native European species that often co-occurs with garlic mustard, whereas Geum laciniatum is a member of the invaded North American communities (McCarthy, 1997
). In addition to comparing an old with a new competitor, we used plants from native European and invasive North American garlic mustard populations and asked whether their allelopathic potential differed depending on the origin of the plants. In contrast to the laboratory bioassays often used to test for allelopathic effects, our approach was to grow garlic mustard in flower pots and let the species contaminate the substrate with root exudates. Seed germination was then tested in the contaminated substrate and compared with a control where activated carbon was added to neutralize contamination.
| MATERIALS AND METHODS |
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Garlic mustard cultivation
Seeds of garlic mustard were dark-stratified for 3 mo at 5°C. Transplanted seedlings were cultivated in small pots of 125 cm3 for 4 wk. Then 28 seedlings of European and 28 of North American origin were planted into pots containing 0.5 L of a 1 : 1 mixture of sand and compost substrate. To half of the pots, finely ground activated carbon was added at a concentration of 20 mL/L substrate. Activated carbon is often used to reduce interference by allelopathic chemicals in the soil because it has a high affinity to organic compounds and a weak affinity to inorganic nutrients (Callaway and Aschehoug, 2000
; Ridenour and Callaway, 2001
). Activated carbon did not have any direct effect on the growth (+6% aboveground biomass, F1,52 = 0.767, P > 0.3) and reproduction (+16% number of pods, F1,52 = 0.774, P > 0.3) of garlic mustard.
From spring 2001 to early summer 2002, the plants were grown in a greenhouse with a 25°/15°C day/night cycle and additional light provided by 500-W lamps. During winter, the plants were vernalized in an unheated greenhouse or in a climate chamber at 5°C when the greenhouse was too cold. Plants were harvested after seed set, and the substrate was carefully separated from the roots.
The germination experiment
Ten petri dishes were filled with the substrate from each flower pot totalling 560 dishes. In half of these, we placed 10 seeds of Geum urbanum, and in the other half of the petri dishes, we placed 10 seeds of G. laciniatum. To test for a direct effect of activated carbon on the germination of either species, 10 control petri dishes were filled with the same 1 : 1 mixture of sand and compost substrate but without precultivation with garlic mustard. Activated carbon was added at the same concentration to half of these dishes. The petri dishes were kept in a refrigerator for 1 wk and transferred to a climate chamber at 15°C with 14 h light. The number of germinated seeds was recorded weekly for 8 wk.
Statistical analysis
The total number of seedlings that germinated after 8 wk was analyzed using a split-plot analysis of deviance with activated carbon and origin of garlic mustard (Europe vs. North America) as plot level treatment and with species (G. urbanum vs. G. laciniatum) and its interactions as within-plot treatment. As seed germination follows a binomial distribution, a likelihood ratio test was used with logit-link function to calculate variance ratios that are approximately F-distributed (McCullagh and Nelder, 1989
, pages 98 and following). The analyses were computed using the program GENSTAT 6 (Payne et al., 1987
).
| RESULTS |
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| DISCUSSION |
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We found that the two species of Geum differed in their sensitivity to allelochemicals. When activated carbon was added there was a much greater increase of germination in the American G. laciniatum than in the European G. urbanum. There still was allelopathic inhibition of G. urbanum when growing in substrate precultivated with European garlic mustard, but North American garlic mustard has obviously lost its "nastiness" to a former competitor. This was the most remarkable finding of our experiment: germination of G. urbanum depended on the origin of garlic mustard populations. It is tempting to invoke local adaptation to explain this pattern. However, examination of evolutionary changes in garlic mustard during the colonization of North America was out of the scope of this paper. Our results do suggest that North American garlic mustard behaved differently than European garlic mustard, but whether this resulted from a single introduction of one particular population that then spread in North America or whether the two types of garlic mustard differ consistently must remain open. One would need to have greater information regarding the number of initial populations and the colonization history in North America, but little is available (Cavers et al., 1979
). Alternatively, one would have to compare a much larger number of European and North American populations of garlic mustard to test the consistency of the difference. Nevertheless, our results suggest that plant material should be carefully selected when testing allelopathy in invasive species.
In conclusion, our data suggest that allelopathy may contribute to the success of garlic mustard as an invader of North American forests, but field trials are needed to examine the relative importance of allelopathy vs. other factors. The use of activated carbon to test for allelopathy is a fruitful approach as compared with laboratory bioassays. Finally, the degree of allelopathic interference is species-specific and can even vary within species. This is particularly important for invasive species that compete with different sets of species in the native and invasive ranges. Target species should be used that co-occur with the allelopathic species in nature to produce meaningful data.
| FOOTNOTES |
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| LITERATURE CITED |
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Cavers P. B. M. I. Heagy R. F. Kokron 1979 The biology of Canadian weeds. 35. Alliaria petiolata (M. Bieb.) Cavara and Grande. Canadian Journal of Plant Science 59: 217-229[ISI]
Choesin D. N. R. E. J. Boerner 1991 Allyl isothiocyanate release and the allelopathic potential of Brassica napus (Brassicaceae). American Journal of Botany 78: 1083-1090[CrossRef][ISI]
Conway W. C. L. M. Smith J. F. Bergan 2002 Potential allelopathic interference by the exotic Chinese tallow tree (Sapium sebiferum). American Midland Naturalist 148: 43-53[CrossRef][ISI]
Dietz H. T. Steinlein P. Winterhalter I. Ullmann 1996 Role of allelopathy as a possible factor associated with the rising dominance of Bunias orientalis L. (Brassicaceae) in some native plant assemblages. Journal of Chemical Ecology 22: 1797-1811[CrossRef][ISI]
Dolling A. O. Zackrisson M.-C. Nilsson 1994 Seasonal variation in phytotoxicity of Bracken (Pteridium aquilinum L. Kuhn). Journal of Chemical Ecology 20: 3163-3172[CrossRef][ISI]
Goslee S. C. D. P. C. Peters K. G. Beck 2001 Modeling invasive weeds in grasslands: the role of allelopathy in Acroptilon repens invasion. Ecological Modelling 139: 31-45[CrossRef]
Harper J. L. 1977 The population biology of plants. Academic Press, London, UK
Keay J. W. E. Rogers R. Lankau E. Siemann 2000 The role of allelopathy in the invasion of the Chinese tallow tree (Sapium sabiferum). Texas Journal of Science 52: S57-S64
McCarthy B. C. 1997 Response of a forest understory community to experimental removal of an invasive nonindigenous plant (Alliaria petiolata, Brassicaceae). In J. O. Luken and J. W. Thieret [eds.], Assessment and management of plant invasions, 117130. Springer-Verlag, New York, New York, USA
McCarthy B. C. S. L. Hanson 1998 An assessment of the allelopathic potential of the invasive weed Alliaria petiolata (Brassicacea). Castanea 63: 68-73
McCullagh P. J. A. Nelder 1989 Generalized linear models, 2nd. ed. Chapman & Hall/CRC, Boca Raton, Florida, USA
Meekins J. F. B. C. McCarthy 1999 Competitive ability of Alliaria petiolata (garlic mustard, Brassicaceae), an invasive, nonindigenous herb. International Journal of Plant Sciences 160: 743-752[CrossRef][ISI]
Nilsson M.-C. 1994 Separation of allelopathy and resource competition by the boreal dwarf shrub Empetrum hermaphroditum Hagerup. Oecologia 98: 1-7[CrossRef][ISI]
Nuzzo V. 1999 Invasion pattern of the herb garlic mustard (Alliaria petiolata) in high quality forests. Biological Invasions 1: 169-179[CrossRef]
Payne R. W. P. W. Lane A. E. Ainsley K. E. Bicknell P. G. N. Digby P. Harding K. Leech H. R. Simpson A. D. Todd P. J. Verrier R. P. White 1987 GENSTAT 5 reference manual. Clarendon Press, Oxford, UK
Ridenour W. M. R. M. Callaway 2001 The relative importance of allelopathy in interference: the effects of an invasive weed on a native bunchgrass. Oecologia 126: 444-450[CrossRef][ISI]
Siemens D. H. S. H. Gardbner T. Mitchell-Olds R. M. Callaway 2002 Cost of defense in the context of plant competition: Brassica rapa may grow and defend. Ecology 83: 505-517[ISI]
Vaughn S. F. M. A. Berhow 1999 Allelochemicals isolated from tissues of the invasive weed garlic mustard (Alliaria petiolata). Journal of Chemical Ecology 25: 2495-2504[CrossRef][ISI]
Wardle D. A. K. S. Nicholson A. Rahman 1993 Influence of plant age on the allelopathic potential of nodding thistle (Carduus nutans L.) against pasture grasses and legumes. Weed Research 33: 69-78[CrossRef][ISI]
Wardle D. A. M.-C. Nilsson C. Gallet O. Zackrisson 1998 An ecosystem-level perspective of allelopathy. Biological Reviews 73: 305-319[CrossRef]
Williamson G. B. 1990 Allelopathy, Koch's postulates, and the neck riddle. In J. B. Grace and D. Tilman [eds.], Perspectives in plant competition, 143162. Academic Press, San Diego, California, USA
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