Impacts of Nutrient Loads on the Invasion Potential of Butomus Umbellatus L

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Impacts of Nutrient Loads on the Invasion Potential of Butomus Umbellatus L IMPACTS OF NUTRIENT LOADS ON THE INVASION POTENTIAL OF BUTOMUS UMBELLATUS L. ON OTTAWA NATIONAL WILDLIFE REFUGE DIKED WETLANDS Erica L. Forstater A Thesis Submitted to the Graduate College of Bowling Green State University in partial fulfillment of the requirements for the degree of MASTER OF SCIENCE August 2020 Committee: Helen Michaels, Advisor Andrew Gregory Kevin McCluney Angélica Vázquez-Ortega © 2020 Erica Forstater All Rights Reserved iii ABSTRACT Helen Michaels, Advisor Introduced to the Great Lakes Region from Europe before 1900, invasive Butomus umbellatus (Flowering rush) forms monotypic stands that crowd native species and cover open water systems across Great Lakes shorelines and reservoirs in the northern US. Factors contributing to invasion persistence and impacts on ecosystem function by this species are poorly understood. This study characterizes vegetation and environmental factors at the Ottawa National Wildlife Refuge, which borders Lake Erie, to understand how sediment nutrient levels in watersheds affect B. umbellatus invasion. We hypothesized that increased sediment nutrient levels are important drivers of B. umbellatus invasion success. Sediment nutrient levels, matter, water depth, and vegetation were sampled within 1m2 plots throughout the management units of the marsh complex. Vegetation of B. umbellatus and 18 other species present were harvested or canopy characteristics measured to estimate biomass. B. umbellatus was the most abundant of all identified emergent invasive species found, occurring at 55 % of the surveyed plots. B. umbellatus rhizome bud count averaged 509 per plot, with a range of 0 – 2760 buds. While sediment nutrient analysis of nitrogen and phosphorus showed heterogeneity within and across management units, nutrient levels did not predict B. umbellatus abundance. However, B. umbellatus biomass decreased with increasing community biomass. Vegetative propagule production via rhizome buds decreased with increased nutrients and increased community biomass. B. umbellatus was found to have a wide range of nitrogen and phosphorus in leaf tissue, and 2 – 4 times more average phosphorus than all analyzed native species. This data will assist managers in identifying timing and approaches for controlling this invasive species and restoring wetland biodiversity. iv ACKNOWLEDGMENTS Thank you to my advisor, Dr. Helen Michaels, and my committee members, Dr. Kevin McCluney, Dr. Andrew Gregory, and Dr. Angélica Vázquez-Ortega for their patience and commitment to guiding me through my degree. Thank you for encouraging me to continue my education and research. I would also like to thank my lab mates, Haley Meek, Rachel Wilson, and Meigan Day, for their assistance in my fieldwork and their company through our graduate careers. Thank you for all of your help at the refuge and in the lab, and for dealing with the mud everywhere. I would also like to thank Andie Fisher, Mary Jane Walther, and the General Botany undergraduates who assisted me in the field and in counting endless numbers of rhizome buds. I would likely still be counting buds if it were not for you. Thank you as well to my family members, friends, and new coworkers for all of the support as I worked through the most difficult time of my college career. I would like to especially thank my partner, Tyler, for his unwavering support of my research and my career interests. Finally, thank you to the Ottawa National Wildlife Refuge and Ron Huffman for allowing me to sample on refuge land. Without their investments in my project, I would not have been able to learn as much as I have in the last few years. This project was funded by through the Ohio Lake Erie Commission (OLEC) and the Lake Erie Protection Fund (LEPF). The LEPF is supported by the citizens of Ohio through their purchase of the Lake Erie license plate. v TABLE OF CONTENTS Page INTRODUCTION ........................................................................................................... 1 Wetlands .............................................................................................................. 1 Invasive Species in the Great Lakes ................................................................... 1 Natural History of Butomus umbellatus .............................................................. 3 Restoration Challenges ........................................................................................ 4 Scientific Gaps – Butomus umbellatus ................................................................ 6 Research Objective .............................................................................................. 7 Questions ............................................................................................................. 7 METHODOLOGY ........................................................................................................... 8 Site Description ..................................................................................................... 8 Survey Design ....................................................................................................... 10 Vegetation Sampling ............................................................................................. 11 Sediment Sampling ............................................................................................... 13 Biomass Regression Models ................................................................................. 15 Statistical Analyses ............................................................................................... 16 Question 1 ................................................................................................ 16 Question 2 ................................................................................................ 18 Question 3 ................................................................................................ 18 RESULTS ......................................................................................................................... 20 Site Description: Maps .......................................................................................... 20 Question 1 ............................................................................................................. 21 vi Community Composition and Environmental Correlates ......................... 21 Effects of Landscape Variables on B. umbellatus Biomass and Vegetative Bud Production ................................................................................................. 23 Question 2 ............................................................................................................. 24 Spatial Autocorrelation of B. umbellatus and Landscape Variables ......... 25 Question 3 ............................................................................................................. 26 Aboveground Tissue Concentrations ........................................................ 26 Effects of Landscape Variables on B. umbellatus Tissue Composition ... 27 DISCUSSION ................................................................................................................... 29 Effects of Landscape Variables on B.umbellatus Biomass and Bud Production .. 29 Effects of Landscape Variables on B.umbellatus Tissue Composition ............... 31 Aboveground Tissue Concentrations ................................................................... 33 Implications for Management ............................................................................... 36 REFERENCES ................................................................................................................. 39 APPENDIX A: FIGURES ................................................................................................ 49 APPENDIX B: TABLES .................................................................................................. 72 APPENDIX C: ADDITIONAL MAPS OF SAMPLE LOCATIONS .............................. 101 APPENDIX D: MODEL ANALYSES USING SEDIMENT N:P AS AN INDEPENDENT VARIABLE ...................................................................................................................... 109 APPENDIX E: COMPARISON OF CARBON CONCENTRATIONS IN B. UMBELLATUS AND NATIVE PLANT SPECIES.................................................................................... 127 1 INTRODUCTION Wetlands Since the beginning of the 20th century, 64 – 71 % of wetlands in the world have disappeared (Davidson 2014). Today, wetlands make up approximately 6 % of the Earth's land surface (Ramsar Convention Secretariat 2013). Despite their limited range, wetlands provide almost 40 % of the world's renewable ecosystem services, including water filtration and nutrient cycling (Costanza et al., 1997; Zedler and Kercher 2005). As technologies have improved and our population continues to grow, a reduction in and degradation of wetlands has occurred, through widespread habitat fragmentation for urban and agricultural development, alterations to irrigation across the landscape, and the spread of invasive species (Bedford 1999; Zedler 2012; Davidson 2014). Invasive Species in the Great Lakes Although an estimated $100 million is spent annually for invasive species management in the Great Lakes region alone, invasive species are still problematic (Rosaen et al., 2012). Well- studied invasive aquatic plant species, including Phalaris arundinacea L. (reed canary grass), Phragmites australis (Cav.) Trin. Ex Steud. (common reed), Typha angustifolia
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