1. Effects of Simulated Herbivory on Alliaria petiolata Ashley Paschal, Brian Scott, Kyle Burns, and Tyler McPheters

2. Background Problems with invasive species –Cause a decline in native populations –Leads to a loss of biodiversity Difficult and expensive to manage

3. Garlic mustard invasion Eradication might be nearly impossible for colonized sites –Autogamous breeding system, high seed production, and rapid growing season (Anderson et al. 1996) –Successful in outcompeting other plants (Meekins and McCarthy 1999) –High tolerance to environmental variation (Meekins and McCarthy 2001)

4. How do we get rid of them? Non-biological eradication –Fires, herbicides, floods, and mowing –Possibly effective, but damaging to surrounding environment Biological controls –Host-specific herbivores might be a suitable solution (Blossey et al. 2001)

5. Deciding on a control Simulated herbivory –Benefit from controlling multiple variables –Better understanding what types of herbivores are effective (Baldwin 1990) Rebek and O’Neil (2005) –Simulated herbivory shortens lifespan and decreases biomass of garlic mustard

6. Our study How does simulated herbivory affect garlic mustard populations in the DePauw Nature Park? Hypothesis: Increased herbivory will reduce survival, growth, and reproduction of garlic mustard Indicated by differences in height, above-ground biomass, and flower number

7. Methods Location: DePauw Nature Park – Creekside Trail. Initially labeled 40 plots that contained at least three (3) rosettes of garlic mustard (Hula-hoop sized plots) Labeled one plant in each plot as control, low, and high. Counted leaves on each plant and then performed treatments.

8. Methods – Treatment Standard hole–punch Half of leaves from the two treatment levels were punched Low – One fourth of leaf area removed. High – Half of leaf area removed

9. Methods Measured light intensity using a light meter Measured soil moisture levels Post-treatment: –Number of flowers, height of plants, and above-ground biomass.

10. Methods Statistical Analysis: –Pearson Correlations –ANOVA

11. Results F = 0.530 P > 0.05

12. F = 2.861 P > 0.05

13. F = 0.229 P > 0.05

14. Correlation Data

15. Significant Correlations Initial height was correlated with density, total number of leaves, number of flowers, final height, and biomass. Final height was correlated with number of flowers, and biomass. Biomass was correlated with number of flowers. There was also a correlation between initial number of leaves and amount of sunlight. Flowering date was not correlated with the different treatments. Most plants had flowered by March 20, 2006 and the remainder had flowered by March 27, 2006.

16. Discussion Our low herbivory and high herbivory treatments showed no significant effects on garlic mustard plant height, biomass, or number of flowers (p>0.05) No significant ANOVA tests, so plants started off comparably and treatments did not detectably affect growth or reproduction

17. Discussion Many obvious correlations between response variables and initial variables –i.e. initial number of leaves and initial height –Less expected but significant correlation seen between plant density and height

18. Discussion Published results have used different methods Rebek and O’Neil 2005 – Effects of simulated herbivory on A. petiolata. –Study on manual flower shoot damage –Led to decreased plant size and reproduction. Bossdorf et al. 2004 – Leaf removal led to reduced production of seeds and fruits. –75% of leaf removal reduced fitness to 81% of that of controls.

19. Implications Results imply that the level of simulated herbivory used was not effective –Currently there are no herbivores in the Nature Park that eat garlic mustard –If we were to introduce an herbivore, it would have to more drastically affect garlic mustard to be successful in controlling the garlic mustard population

20. Implications Garlic mustard is currently affecting the native species of plants at the DePauw Nature Park, so it is important to control garlic mustard Control of garlic mustard important also for regeneration of forest New York Times article (May 2, 2006) says that GM disrupts interactions between tree seedlings and soil mycorrhizae

21. Recommendations Other strategies for removal of garlic mustard: pulls, herbicides, controlled fire Small, isolated patches that are more manageable should be controlled to prevent spread –Rim trail patches in contrast to rail trail flourishing populations

22. Works Cited Baldwin, I.T. 1990. Herbivory simulations in ecological research. TREE 5: 91-93. Bossdorf, O., S. Schroder, D. Prati, and H. Auge. 2004. Palatability and tolerance to simulated herbivory in native and introduced populations of Alliaria petiolata (Brassicaceae). American Journal of Botany 91 (6):856-862. Blossey, B., V. Nuzzo, H. Hinz, E. Gerber. 2001. Developing biological control of Alliaria petiolata (M. Bieb.) Cavara and Grande (garlic mustard). Natural Areas Journal 21: 357-367. Meekins, J.F., and B.C. McCarthy. 1999. Competitive ability of Alliaria petiolata (garlic mustard, Brassicaceae), an invasive, nonindigenous forest herb. International Journal of Plant Sciences 160: 743-752. Meekins, J.F., and B.C. McCarthy. 2001. Effect of environmental variation on the invasive success of a nonindigenous forest herb. Ecological Applications 11: 1336-1347. Rebek, K.A., and R.J. O’Neil. 2005. Impact of simulated herbivory on Alliaria petiolata survival, growth and reproduction. Biological Control 34:283-289.