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Establishing the use of spp. as biocontrol agents of fungal and nematode

Dissertation

Presented in Partial Fulfillment of the Requirements for the Degree Doctor of Philosophy in the

Graduate School of the Ohio State University

By

Rebecca B. Kimmelfield, B.S.

Graduate Program in Translational Plant Sciences

The Ohio State University

2020

Dissertation Committee:

Associate Professor Christopher G. Taylor, Advisor

Professor Michelle Jones, Member

Professor Sally Miller, Member

Associate Professor Joshua Blakeslee, Member

Associate Professor Stephanie Strand, Member

Copyrighted By Rebecca B. Kimmelfield 2020

Abstract The use of microbial inoculants to control plant disease is an increasingly used method in agriculture to mitigate damage caused by phytopathogens across a variety of systems. Best management practices to control many plant diseases can include use of multiple types of control measures in which biocontrol is one of a suite of tools used. One commonly investigated as biocontrol agents is Pseudomonas. These bacteria are known to be capable of promoting plant growth and reducing damage caused by disease though a variety of modes of action including nutrient competition and niche exclusion, secretion of compounds including , DAPG, and pyoluteorin, and production of volatile organic compounds

(VOCs). The primary focus of this dissertation, broadly, is the use of microorganisms

(specifically Pseudomonas spp.) as biocontrol agents. Studies performed using these bacteria, both physically and conceptually, ranged from basic science, to small-scale microplot field trials, to applied market research.

The focus of Chapters 2 and 3 of this work was investigating the role of VOCs in the biocontrol of nematodes (Caenorhabditis elegans) and fungi (Fusarium oxysporum) under in vitro conditions. The first objective of this work was to investigate how bacterial VOCs affected the growth and activity of other microorganisms, and determine what bioactive VOCs are produced by the bacteria. In shared-air indirect exposure assays using a diverse group of 20 bacteria (19 strains of Pseudomonas representing seven and one of agglomerans) we established that a majority the of the bacteria tested produced VOCs inhibitory

ii to both C. elegans and F. oxysporum while other strains were only effective in inhibiting C. elegans. We performed VOC profiling using proton transfer reaction time-of-flight mass- spectrometry (PTR-ToF-MS) to compare differences in volatile production between the bioactive and non-bioactive strains. Hydrogen (HCN) and organosulfur compounds were associated with F. oxysporum inhibition, while only HCN was correlated with C. elegans inhibition. These findings generally confirmed our knowledge of antagonistic bacterial VOCs, as members of these categories of compounds have been shown to be antagonistic toward microorganisms. The second objective of this dissertation was to build off this knowledge, in which we sought to determine whether manipulation of the bacteria could selectively enhance production of specific VOCs. To test this, in vitro assays and VOC profiling were performed with three strains of Pseudomonas (P. chlororaphis, P. rhodesiae, P. protegens) on three media (minimal medium± glycine or L-methionine). These amino acids were selected because they are precursors to HCN (glycine) and methanethiol (methionine), two compounds highly produced by the inhibitory bacteria in the first objective. HCN is a VOC with well- established control potential, and methanethiol is the precursor to multiple organosulfur compounds, some of which have control potential. The addition of each amino acid affected bacterial VOCs to different extents. L-methionine could effectively prime the system. Bacteria grown on minimal media supplemented with L-methionine produced more organosulfur compounds and had greater bioactivity in bioassays compared to bacteria growth on minimal media. Of the three strains, the P. rhodesiae was enhanced by L-methionine to the greatest extent. In both in vitro agar-based and soil-based assays, P. rhodesiae inhibitory behavior against

F. oxysporum was increased with the addition of L-methionine. We also found that addition of only L-methionine to a soil system was sufficient to prime the native microorganism population

iii to produce inhibitory VOCs against F. oxysporum. The addition of glycine to the system promoted an increase in bacterial but varied in increased efficacy against microorganisms; for the strains that produced hydrogen cyanide, the VOCs produced by bacteria grown on minimal medium±glycine had no differences in F. oxysporum inhibition; however, an increase was seen in C. elegans inhibition. Results from this study indicate that VOCs can contribute to the control potential of pseudomonads, and the compounds produced by the bacteria can be manipulated though the inputs added to the growth matrix.

The third objective of this work was to investigate the potential for Pseudomonas,

Bacillus, and Pantoea strains to control soybean cyst nematode (SCN) in the greenhouse and microplot (small-scale field trial) settings. These experiments move the biocontrol research from basic (in vitro laboratory assays) to more applied. In total, eight strains (six Pseudomonas spp., one sp., and one Pantoea agglomerans) were used in these trials. Bacteria were tested using multiple formulations including individual strains and consortia of bacteria, and soil drench and seed treatments. In the microplot trials, nematode control efficacy investigated two parameters: end of season SCN egg counts and soybean yield. The results of the studies were varied. Efficacy of individual treatments was inconsistent from trial to trial. There were no treatments that either caused significantly lower SCN egg densities or significantly higher yield in all microplot experiments, however select treatments showed potential in at least one experiment.

Finally, the last objective of this work was to investigate the current environment for biocontrol research and product development within the industry. This project, presented in

Chapter 5, explored the potential for increased collaborations between university researchers and the microbial bioproducts industry. Companies are continuing to explore new actives for

iv bioproducts, and professors continue to research potential beneficial microorganism and natural products. We interviewed professors from the state of Ohio who research in the fields of microorganism and natural products and learned while many professors want to commercialize their research, not all have gone through the necessary steps required to do so. We also interviewed companies that develop microbial inoculants, specifically individuals involved in research and development, and discovered that many companies obtain microorganisms and natural products from external sources. Companies and university faculty also collaborate in research projects. The results from this project indicated that there is no uniform method of collaborating between university and industry, but there is potential to streamline the process. In this way, bioproducts research could be done to meet the needs and wants of both the industry developing the products and university researchers performing the basic science.

The results obtained in each chapter, from the basic science presented in Chapters 2 and 3 to the market research project in Chapter 5, present evidence that there is potential for

Pseudomonas as biocontrol agents. The VOCs produced by the bacteria have significant inhibitory activity against F. oxysporum and C. elegans. While we saw varied efficacy of the bacteria against SCN, future studies can continue to explore the mode of action of these bacteria and determine whether there is applicability in other field and greenhouse systems. With sufficient in vitro and mode of action studies, paired with applied greenhouse and field trials, our best candidates can be further explored to determine whether they have potential from a commercial perspective.

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This work is dedicated to the memory of my Grandma Sue Krolikowski. Thank you for being my most vocal cheerleader though all my studies. You have inspired me to continue on my quest of being a lifelong learner.

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Acknowledgements

I am truly grateful for the tremendous support—both professionally and personally—that

I have received from countless individuals over my time in this program. I would first like to thank my advisor, Dr. Chris Taylor, for his support and guidance over the past six years. Chris has encouraged me, in the best possible way, to forge my own path and tackle scientific queries as an independent, critical thinker. I am also grateful for the rest of my scientific advisory committee, both current and past members. Thank you for your patience and sharing of scientific knowledge over the years.

The bulk of the research presented within this dissertation succeeded because I had many great people helping me along the way. The success of the science truly took a village. There are multiple people in particular I would like to thank. Department of members Dr.

Xiao-Yuan Tao, Rachel Kaufman, Dr. Anna Testen and Therese Miller for helping train me to work with the microorganisms and field work and Wanderson Bucker Moraes for his help and patience with statistics; Dr. Shauna Brummet was an invaluable mentor for the entrepreneurial study presented in Chapter 5; Multiple interns—Heather, Jack, Justin—both helped with the experiments and helped me develop leadership skills. Thank you to current and recent members of the Taylor Lab: Dr. Tim Frey, Cecilia Chagas de Freitas, Leslie Taylor, and Edwin D. Navarro

Monserrat, and many others for helping me with lab work and reasoning though questions, as well as providing me with friendship, emotional support, and endless laughter over the years.

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Multiple studies presented here were done at the International Laboratory for Plant

Neurobiology (LINV). Thank you to all members of the LINV, specifically Drs. Stefano

Mancuso, Cosimo Taiti and Diego Comparini, for being fantastic collaborators on the volatile organic compounds experiments. You made me welcome during my time spent in your lab, and I gained a tremendous amount knowledge working with you.

Finally, I’d like to give a huge thank you to my friends and family. My parents have been nothing but supportive of me in every adventure and challenge, and that means the world. To

Michael, Abby, Alison, Emily, Norman, Nathan, Brian, Francesca, Joe, Edwin, Cecilia, Tim, Ali, and many others, I have endless appreciation for your love and friendship, it’s helped me celebrate the highs, and survive the lows.

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Vita

2013...... B.S. Environmental Science, The Ohio State University

2013 to present .... Graduate Fellow (Translational Plant Sciences Graduate Program) or Graduate Research Associate (Department of Plant Pathology), The Ohio State University

Publications

Cocuron, J. C., Koubaa, M., Kimmelfield, R., Ross, Z., & Alonso, A. P. (2019). A combined metabolomics and fluxomics analysis identifies steps limiting oil synthesis in maize embryos. Plant Physiology, 181(3), 961–975. https://doi.org/10.1104/PP.19.00920

Fields of Study

Major Field: Translational Plant Sciences

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Table of Contents

Abstract ...... ii Dedication ...... vi Acknowledgements ...... vii Vita ...... ix Table of Contents ...... x List of Tables ...... xiii List of Figures ...... xv Chapter 1 Literature Review ...... 1 1.1 Introduction to Biocontrol...... 2 1.2 Ohio Agriculture ...... 2 1.3 Pathogens Affecting Ohio Crops ...... 3 1.3.1 Soybean diseases ...... 3 1.3.2 Tomato diseases ...... 7 1.4 Management Strategies for Controlling Pathogens ...... 8 1.4.1 Soybean cyst nematode management strategies ...... 8 1.4.2 Fusarium oxysporum management strategies ...... 15 1.5 Pseudomonas ...... 17 1.5.1 Pathogenic Pseudomonas...... 18 1.5.2 Beneficial Pseudomonas ...... 19 1.6 Commercial Pseudomonas-Based Products ...... 31 1.7 Objectives ...... 32 Chapter 2: Determination of the Volatile Compounds Produced by Pseudomonas spp. Strains and Establishing Their Role in Biocontrol...... 49 2.1 Abstract ...... 50 2.2 Introduction ...... 51 2.3 Materials and Methods ...... 55 2.3.1 Microorganism maintenance ...... 55 2.3.2 Pseudomonas mode of action assays ...... 56 2.3.3 Pseudomonas single strain VOC measurement ...... 58 2.3.4 HCN measurement ...... 59 2.3.5 F. oxysporum inhibition using HCN ...... 60 2.3.6 Data analysis and statistics ...... 61 2.4 Results ...... 63 2.4.1 In vitro bioassays ...... 63 2.4.2 PTR-ToF-MS and HCN quantification ...... 65 2.4.3 Correlation between in vitro assays and volatile compounds ...... 68 2.5 Discussion ...... 69 2.6 Conclusions and Future Directions ...... 78

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Chapter 3: Identifying the Potential to Prime Pseudomonas spp. for Volatile Production Though Manipulation of the Culture Medium ...... 109 3.1 Abstract ...... 110 3.2 Introduction ...... 111 3.3 Materials and Methods ...... 114 3.3.1 Microorganism maintenance ...... 114 3.3.2 In vitro volatile inhibition assays ...... 115 3.3.3 Pseudomonas volatile organic compound (VOC) quantification ...... 117 3.3.4 Pseudomonas mining for methanethiol and hydrogen cyanide synthesis genes ...... 118 3.3.5 Fusarium inhibition with organosulfur VOCs ...... 119 3.3.6 Data analysis ...... 120 3.4 Results ...... 121 3.4.1 In vitro VOC inhibition assays ...... 121 3.4.2 Inhibition of F. oxysporum by volatiles produced by Pseudomonas grown on soil...... 122 3.4.3 VOC production by Pseudomonas ...... 123 3.4.4 Correlation of F. oxysporum inhibition with volatile production ...... 126 3.4.5 Presence of genes involved in methanethiol and hydrogen cyanide production ...... 126 3.4.6 F. oxysporum 289 inhibition by DMS and DMDS ...... 127 3.5 Discussion ...... 127 3.6 Conclusions and Future Directions ...... 133 Chapter 4: Evaluation of Bacterial Treatments as Biocontrol Agents of Soybean Cyst Nematode in Microplot and Greenhouse Trials ...... 155 4.1 Abstract ...... 156 4.2 Introduction ...... 156 4.3 Materials and Methods ...... 160 4.3.1 Plant material ...... 160 4.3.2 Nematode inoculum preparation-microplots ...... 160 4.3.3 Bacteria preparation-microplots ...... 161 4.3.4 Microplot setup and yield measurements ...... 163 4.3.5 Determination of SCN infestation of microplots ...... 164 4.3.6 SCN greenhouse assay ...... 165 4.3.7 Data analysis ...... 165 4.4 Results ...... 166 4.4.1 2017 microplot study ...... 167 4.4.2 2018 microplot study ...... 167 4.4.3 SCN greenhouse assays ...... 170 4.5 Discussion ...... 170 4.6 Conclusions and Future Directions ...... 176 Chapter 5: Market Research on the Development of a Platform for Streamlined University-Industry Collaboration in the Field of Microorganisms and Natural Products ...... 201 5.1 Key Takeaways ...... 202 5.2 Introduction and Project Rationale ...... 202 5.3 Methodology ...... 206

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5.4 Results and Discussion ...... 207 5.4.1 Interview summary ...... 208 5.4.2 Business model canvas and business model: Hypotheses validation ...... 212 5.5 Conclusions and Future Directions ...... 213 Chapter 6: Perspectives ...... 231 References ...... 236 Appendix A1: Volatile Organic Compounds Quantified in the Headspace of Pseudomonas spp. and Pantoea agglomerans ...... 261 Appendix A2: Root Exudate Profile of 10-day Old Glycine max ‘Lee’ Seedlings ...... 272 A2.1 Materials and Methods ...... 273 A2.1.1 Plant material ...... 273 A2.1.2 Experimental setup and quantification: Root exudates ...... 273 A2.2 Results ...... 274

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List of Tables

Table 1.1. Representative list of commercially available Pseudomonas-based bioproducts in the United States ...... 48 Table 2.1. Pseudomonas strain information ...... 99 Table 2.2. Pearson’s correlation coefficients for the volatile compounds most positively correlated with fungal inhibition ...... 100 Table 2.3. Inhibition of F. oxysporum 289 by HCN ...... 101 Supplemental Table S2.1. Organosulfur compounds produced by Pseudomonas spp. and Pantoea agglomerans strains ...... 107 Table 3.1. Pearson’s correlation coefficients for VOCs correlated with F. oxysporum 289 inhibition ...... 149 Table 3.2. Genome search for the presence of genes coding for enzymes involved in methanethiol and hydrogen cyanide biosynthesis...... 150 Table 3.3. Inhibition of F. oxysporum 289 by DMDS and DMS ...... 151 Supplemental Table S3.1 Protein sequences used in tblastn search for presence of organosulfur compound and hydrogen cyanide synthesis genes in three Pseudomonas strains ...... 152 Supplemental Table S3.2. Organosulfur compounds produced by Pseudomonas spp. on M9 minimal medium±amino acids ...... 153 Table 4.1. Bacteria strains used in microplot and greenhouse experiments ...... 189 Table 4.2. Bacteria treatments used in 2017 microplot study ...... 190 Table 4.3. Bacteria treatments used in 2018 microplot study ...... 191 Table 4.4. 2017 microplot summary ...... 192 Table 4.5. 2018 microplot summary ...... 193 Table 4.6. Statistical differences between 2017 SCN microplot treatments-75,000 egg inoculum ...... 195 Table 4.7. Statistical differences between 2018 SCN microplot treatments-50,000 egg inoculum ...... 197 Table 4.8. Statistical differences between 2018 SCN microplot treatments-5,000 egg inoculum...... 199 Table 5.1 Ratio of gross licensing income to total research expenditures for Big Ten universities in 2017 ...... 224 Table 5.2 Federal budget information for the National Science Foundation and US Department of Agriculture from FY2016-FY2021...... 225 Table 5.3. Questions asked in I-CORPS@Ohio interviews ...... 226

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Table 5.4. Industry collaborations with universities and/or private research contract companies ...... 228 Table 5.5. Company sourcing for microorganisms and natural products ...... 229 Table 5.6. Responses from technology commercialization officers, other university administration, and similar organization interview segments ...... 230 Table A1.1. Compounds identified with PTR-ToF-MS analysis ...... 263 Table A2.1. Amino acid external standard ...... 277 Table A2.2. Amount of 24 amino acids in root exudates of Glycine max ‘Lee’ seedlings ...... 278 Table A2.3. Proportion of 24 amino acids in root exudates of Glycine max ‘Lee’ seedlings .....279

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List of Figures

Figure 2.1. Top agar growth inhibition of F. oxysporum 289 by Pseudomonas spp. and Pantoea agglomerans strains ...... 86 Figure 2.2. Dual plating growth inhibition of F. oxysporum 289 by Pseudomonas spp. and Pantoea agglomerans strains ...... 87 Figure 2.3. Indirect volatile exposure inhibition of F. oxysporum isolates 289 (A) and 197 (B) with Pseudomonas spp. and Pantoea agglomerans strains ...... 88 Figure 2.4. Indirect volatile exposure inhibition of F. oxysporum isolates 289 (A) and 197 (B) by Pseudomonas sp. and Pantoea agglomerans ...... 90 Figure 2.5. Volatile activity against C. elegans by Pseudomonas spp. and Pantoea agglomerans ...... 92 Figure 2.6. Heat map showing the average intensities (ppbv) of 20 strains of Pseudomonas spp. and Pantoea agglomerans...... 93 Figure 2.7. Cyanide and sulfur-containing compounds produced by the Pseudomonas spp. and Pantoea agglomerans...... 94 Figure 2.8. Hydrogen cyanide quantification by Pseudomonas spp. and Pantoea agglomerans + strains using either A) PTR-ToF-MS (H2CN , m/z 28.018) or B) a colorimetric semi-quantitative assay ...... 95 Figure 2.9. Signal intensity of organosulfur compounds produced by 20 Pseudomonas spp. and Pantoea agglomerans strains...... 96 Figure 2.10. Principal component analysis (PCA) biplots of 20 Pseudomonas and Pantoea strains and LB controls ...... 97 Supplemental Figure S2.1. In vitro inhibition assay setup ...... 102 Supplemental Figure S2.2. Variable reductive principal component analysis (PCA) of the volatile profiles produced by Pseudomonas spp. and Pantoea agglomerans strains ...... 103 Figure 3.1. Pathways of (A) hydrogen cyanide (HCN) and (B) organosulfur compounds biosynthesis ...... 140 Figure 3.2. Indirect volatile exposure inhibition of F. oxysporum 289 by Pseudomonas spp. grown on minimal medium with and without supplementation of amino acids ...... 141 Figure 3.3. Indirect volatile exposure inhibition of C. elegans by Pseudomonas spp. grown on LB or minimal medium with and without supplementation of amino acids ...... 142 Figure 3.4. Indirect volatile exposure inhibition of F. oxysporum 289 by P. rhodesiae 88A6 grown on topsoil supplemented with L-methionine ...... 143 Figure 3.5 Heat map showing the average intensities (ppbv) of the volatile profile of Pseudomonas spp. strains grown on media with different amino acid compositions ...... 144

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Figure 3.6. Principal component analysis (PCA) score plot of Pseudomonas spp. grown on minimal media with and without supplementation of amino acids ...... 145 Figure 3.7. Cyanide and sulfur-containing VOCs compared to the total amount of volatile organic compounds produced by each treatment ...... 146 + Figure 3.8. Hydrogen cyanide (CH2N , m/z 28.018) produced by Pseudomonas spp. strains grown on media with different amino acid compositions ...... 147 Figure 3.9. Organosulfur compounds produced by Pseudomonas spp. strains grown on media with different amino acid compositions ...... 148 Figure 4.1 SCN hatch rate and fecundity assay for a collection of Pseudomonas spp. strains ...182 Figure 4.2 Microplot setup ...... 183 Figure 4.3 Correlation between eggs/100 cubic-centimeters soil and soybean yield in microplot trials...... 184 Figure 4.4 Yield comparison between egg load in 2018 microplot study ...... 186 Figure 4.5 Box and whisker plots of SCN greenhouse assays ...... 187 Figure 5.1 Total research expenditures versus industry research expenditures ...... 217 Figure 5.2 Research expenditures versus gross licensing income ...... 218 Figure 5.3. Business model initially proposed by MO-NP@OSU ...... 219 Figure 5.4. Business model canvas (BMC) for I-CORPS@Ohio Project ...... 220 Figure 5.5. Proposed business model for MO-NP@OSU ...... 223 Figure A2.1. Setup of root exudate experiment ...... 276

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Chapter 1: Literature Review

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1.1 Introduction to Biocontrol

Biocontrol was described by DeBach and Rosen (1991) as “the utilization of natural enemies to reduce the damage caused by noxious organisms to tolerable levels.” An early record of biocontrol in the United States dates to 1888, with use of beneficial vedalia beetles (Rodolia cardinalis) to control cottony-cushion scale (Icerya purchase) in California citrus, and has been used ever since (DeBach & Rosen,1991). Biocontrol of pests and pathogens can be achieved with beneficial insects, nematodes, fungi, viruses and bacteria. This is a relevant area of study because the demand for biocontrol products has grown in recent years, and the trend is forecasted to continue. In the United States, sales of biological products is predicted to increase from 750 million USD in 2015 to 3 billion USD in 2025 (Dunham, 2017). The purpose of this work seeks to investigate the potential for the bacteria Pseudomonas spp. to act as biological control agents of relevant Ohio plant pathogens, namely Heterodera glycines (soybean cyst nematode, SCN) and Fusarium oxysporum. This literature review will explore each facet of the biological control system, namely the plant, , and biological control agent, with emphasis on pathogen and biocontrol agent mode of action.

1.2 Ohio Agriculture

Ohio has the 16th largest agriculture economy in the United States, responsible for 2.4% of the nationwide commodity sales receipts in 2018 (USDA-ERS, n.d). In 2019, Ohio had over

77,000 individual farms with approximately 13.5 million acres of land used in agriculture; over 8 million acres were planted with crops (USDA-NASS, n.d. a). In 2015 agriculture production contributed to 0.63% of Ohio’s gross state product (3.9 billion USD), and accounted for over

83,000 jobs in the state. Many additional jobs and revenue also came downstream from

2 agriculture and food processing (DiCarolis et al, 2017). In 2018 the top five crops produced within the state (according to state receipts) were soybean (Glycine max), corn (Zea mays), wheat

(Triticum spp.), hay and tomatoes (Solanum lycopersicum); Ohio production of these crops made up respectively 6.5%, 4.2%, 1.8%, 1.6%, and 2.8% of the nationwide totals. (USDA-ERS, n.d).

With such a large portion of the state economy (in both jobs and GSP) dependent on agriculture, it is important to maximize crop production as efficiently as possible. As such, the focus of this chapter is to investigate the use of control agents to mitigate plant pathogens. Emphasis will be put on describing soybean cyst nematode (SCN), the primary pathogen of the state’s most widely grown crop, soybean, as well as Fusarium oxysporum, which can infect multiple crops in Ohio.

Both SCN and F. oxysporum are used in biocontrol experiments in subsequent chapters of this dissertation.

1.3 Pathogens Affecting Ohio Crops

1.3.1 Soybean diseases

There are many phytopathogens, including fungi, oomycetes, bacteria, viruses, and nematodes that are causal agents for diseases that can negatively affect soybean yield. These pathogens can attack the aboveground portion of the plant, or dwell in the soil and affect the root system. Soybean pathogens in Ohio resulted in estimates of 2.75 billion dollars (USD) lost between 2010 and 2014; the only states that had estimated losses higher than Ohio were Illinois and Minnesota (Allen et al, 2017). Three pathogens that cause some of the highest soybean yield loss in Ohio are Phytophthora sojae, Fusarium spp., and SCN (Wrather & Koenning, 2006).

Phytophthora sojae has been found widely around the state of Ohio (Dorrance et al,

2003). It is a pathogen responsible for stem and root rot and affects plants at every stage of

3 development (Martin & Dorrance, 2019). Between 2003 and 2005, disease caused by P. sojae resulted in an estimated loss of 1.45 million metric tons (MT) of soybeans in Ohio, and 3.93 million MT across 28 US states (all of the soybean producing states in the United States), as compared to estimated yield in a healthy soybean production system (Wrather & Koenning,

2006). A second common soybean pathogen is Fusarium spp, and although multiple species can infect soybeans, F. graminearum was the most virulent species among a collection of Ohio isolates (Broders et al, 2007). In Ohio multiple Fusarium diseases have caused substantial economic damage due to soybean loss. Fusarium spp. is a causal agent of soybean root rot, and between 2003 and 2005 had estimated yield loss of over 55,000 MT in Ohio, and over 0.53 million MT across 28 US states; over the same timeframe sudden death syndrome (causal agent

F. virguliforme) accounted for losses of 58,000 MT Ohio and nearly 2 million MT across 28 states. The damage caused annually by Phytophthora was more consistent than damage caused by the Fusarium pathogens, which has fluctuated more over the years (Allen et al, 2017; Wrather

& Koenning 2006).

Finally, SCN is among the most economically devastating pathogens of soybean in the

United States soybean growing region, including Ohio (Wrather & Koenning, 2006). SCN was used in microplot studies in Chapter 4 of this work, and as such more information will be detailed for this pathogen than other soybean pathogens. It is newly known to Ohio, first found in

1987 (Reidel & Golden, 1988). SCN is a root parasitic nematode which feeds on plant host roots, ultimately taking nutrients from the host plant, subsequently resulting in reduced plant yield.

SCN infestation in fields can be asymptomatic. Susceptible and resistant soybean cultivars planted in the same infested field grew visually similar, although yield was higher in resistant cultivars (Young 1996). Damage due to SCN has increased immensely in recent years. Between

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2003 and 2005, SCN damage resulted in an estimated yield loss of 0.92 million MT in Ohio and

8.3 million MT lost in 28 US states (Wrather & Koenning 2006). Approximately one decade later, between 2010 and 2014, SCN damage resulted in an estimated 16.8 million MT lost across

28 US states and Ontario, Canada (Allen et al, 2017). SCN presence in soybean growing states has increased in recent years. In Ohio, SCN has been found in over 80% of counties and was newly detected in three Ohio counties between 2014 and 2017 (SCN in Ohio, n.d, Tylka &

Marett 2017). At the national scale, SCN detection has increased from North Carolina in 1954 to a majority of soybean growing counties in the US (Tylka & Marett 2017; USDA-NASS, n.d. b).

Soybean cyst nematode lifecycle

SCN is a sedentary obligate biotroph parasitic nematode, meaning the nematode needs a living plant host to grow on and reproduce. The reproductive cycle of SCN is as short as 3 weeks under ideal conditions (Niblack, 2005). This short cycle means single fields can experience multiple SCN generations though a growing season; small initial nematode populations may grow large over the course of a few months. There are multiple crop hosts of SCN including soybean (Glycine max, namesake of this disease), dry beans (Phaseolus vulgaris, including pinto and kidney beans), and select weed hosts including purple deadnettle (Lamium purpureum) and field pennycress (Thlaspi arvense) (Abawi & Jacobsen 1984; Poromarto & Nelson

2009;Venkatesh et al, 2000). Under proper conditions including temperature (approximately 25-

36ºC), adequate moisture, cation concentrations and presence of a host, eggs are stimulated, undergo their first molt, hatch into second-stage juveniles (J2s) and begin migrating towards the host root (Niblack, 2005; Tefft et al, 1982). The presence of a host root is important as the roots exude compounds important in stimulating hatching, including glycinoeclepin A, produced by

5 common bean, and other uncharacterized compounds produced by soybean (Masamune et al,

1984; Okada, 1971; Schmitt & Riggs, 1991; Tefft et al, 1982).The importance of host root exudates is further demonstrated as hatch rates in the exudates of non-hosts were significantly lower than in the exudates of soybean or a water control (Medina, 2016; Schmitt & Riggs, 1991).

Once arriving at the plant, the J2 penetrates the root using a needle-like stylet and secretes a number of enzymes to degrade the . Smant et al (1998) first reported on the isolation of β-1,4-endoglucanases (cellulases) from H. glycines juveniles’ esophageal glands.

Since then, additional genes have been discovered in the genome of SCN that are expressed in the esophageal glands of J2s and encode for enzymatic proteins involved in cell wall degradation and are important to SCN’s ability to parasitize the host plant (Gao et al, 2003). Wang et al

(1999) demonstrated that one esophageal β-1,4-endoglucanase, HG-ENG-2, is secreted though the nematode stylet into root tissue while another, HG-ENG-1 is not secreted into the root. When secreted, these enzymes can break down the plant cell wall so the nematode can enter the plant root. Once in the root at the feeding site, the nematode secretes additional effector proteins to induce the plant to create a multi-nucleated syncytium (feeding site) (Bohlmann and Sobczak,

2014; Mejias et al 2019). In an infected plant, cell wall breakdown at the feeding site occurs within days of infection, a true syncytium forms after a week, and individual cells are no longer distinguishable at 15 days after infection (Gipson et al, 1971). At the syncytium, the J2 becomes sedentary and loses its somatic musculature, and undergoes two additional molts, J3 and J4, before reaching the adult stage (male or female). SCN is an obligately sexual parasite, and the male adults regain their somatic musculature and leave the root to fertilize the females, which remain adhered to the syncytium (Niblack, 2005). SCN undergoes epidermal proliferation

(number and ploidy of cells) after infection, and the adult female nematode is more saccate-

6 shaped than the juveniles and males (Thapa et al, 2019). After fertilization, female SCN produce hundreds of eggs, and finally die, leaving a protective cyst surrounding the eggs. The females also deposit eggs unprotected external from the cyst in a gelatinous matrix (Niblack, 2005; Sipes et al, 1992). Protected within the cyst, SCN eggs can remain viable for multiple years in the soil.

SCN-cyst infested soil stored indoors had viable eggs for at least 7 years that could hatch out and infect soybean plants (Inagaki & Tsutumi, 1971). It is imperative to control for SCN because the nematode is both so economically destructive and persistent in the soil.

1.3.2 Tomato diseases

Many foliar and soilborne pathogens can affect tomatoes grown in high tunnels and the field. Within the state of Ohio, soilborne diseases affecting tomato crops include Verticillium wilt (Verticillium dahlia), corky root rot (Pyrenochaeta lycopersici), root knot nematode

(Meloidogyne spp.) and Fusarium wilt (Fusarium oxysporum f. sp. lycopersici) (Testen & Miller,

2017a). In high tunnels, pathogens can form disease complexes and contribute to reduced health of the plant (Testen & Miller, 2018). Fusarium oxysporum was used in in vitro assays in

Chapters 2 and 3 of this work, and as such more information will be detailed about this pathogen than other tomato pathogens. Multiple subspecies of F. oxysporum have demonstrated a damaging effect on tomato yield. Tomato yield in field trials inoculated with a consortium of pathogens (Sclerotinia rolfsii, Pythium ultimum, Rhizoctonia solani, F. oxysporum f.sp. lycopersici (FOL)) was significantly lower compared to uninoculated plants (Mao et al, 1998). In greenhouse assays, tomatoes inoculated with F. oxysporum f.sp. radicis-lycopersici (FORL, causal agent Fusarium crown and root rot) had substantial plant death and a threefold reduction of tomato yield in plants as compared to uninoculated plants (Lafontaine & Benhamou, 1995).

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Both FOL (causal agent Fusarium wilt) and FORL can be introduced to a system via infected transplants or though infected equipment. The fungi can survive for multiple cropping seasons in infected soil due to the production of chlamydospores. Both pathogens are found widely where tomatoes are grown (Davis & Paulus, 2014; Correll & Jones, 2014).

There are multiple management strategies used for controlling these soilborne plant pathogens. Control strategies are diverse and include one or a combination of genetic, cultural, chemical and biological practices. Some of the management strategies are described in the following sections.

1.4 Management Strategies for Controlling Pathogens

1.4.1 Soybean cyst nematode management strategies

Discussed here are some methods for controlling SCN: genetic resistance, crop rotation, chemical control, and biological control.

SCN management: Genetics (resistance)

The primary strategy used to control SCN is use of resistant soybean cultivars. Trials across the state of Iowa demonstrated that within the same SCN-infested environment, resistant cultivars can have significantly higher yield compared to a susceptible cultivar (Tylka et al,

2019). In the United States, genetics has been used to prevent SCN infection in soybeans since the nematode was first detected in North Carolina. Field testing in 1957 demonstrated that of the soybean lines tested, only 0.28% were highly resistant to SCN (Ross & Brim, 1957). Over the next few decades, further studies revealed that SCN populations have variable infection ability.

That is, individual populations could reproduce on some resistant soybean lines but not on

8 others, which indicates the presence of multiple resistance genes within the soybean genome

(Anand & Brar, 1983; Golden et al, 1970). Quantitative trait locus (QTL) mapping in 16 studies on crosses between a susceptible and resistant line of soybean has identified two common gene loci involved in resistance: rhg1 and Rhg4 (Concibido et al, 2004). The genes (type and copy number) involved in resistance vary among SCN-resistant soybean lines. For example, in both plant introduction (PI) 437654 and Peking the rhg1 allele interacts with the Rhg4 allele to achieve resistance against SCN, while in PI88788 only the rhg1 allele is responsible for resistance (Brucker et al, 2005; Yu et al, 2016). Yu et al (2016) also demonstrated the importance of increased Rhg1 copy number in resistance against multiple SCN populations.

Many soybean accessions have demonstrated resistance to SCN, however few of these lines have been used in the field as sources of genetic resistance in commercial varieties (Arelli et al, 2000; Rao Arelli et al, 1997; Tylka & Mullaney, 2019). SCN resistant cultivar PI88788 contributes to the genetic resistance of over 95% of commercially sold SCN-resistant varieties in the northern and central United States (Maturity Groups (MGs) 0, I, II, and III). Accessions

Peking and PI737654 also contribute resistance to commercial varieties in MGs 0, I, II, and III, however to a much lesser extent than PI88788 (Tylka and Mullaney 2019). Ohio is in MG zones

II, III, and IV (Stowe & Dunphy, 2017). Soybeans planted in southern Ohio (MG IV) may be different SCN-resistant cultivars than those grown in Northern Ohio (MGs II and III). Careful consideration must be used for determining which SCN-resistant cultivars to plant. There is variability in the effectiveness of resistant cultivars to control SCN reproduction and increase yield, even when cultivars have the same genetic source of resistance (Tylka et al, 2019).

Soil samples from around the United States have contained populations of nematodes able to grow at elevated levels (>10% of susceptible control) on PI88788, which indicates that

9 nematode populations are overcoming soybean genetic resistance (scncoalition.com, n.d.).

Samples in Ohio have also contained nematodes able to grow at elevated levels on Peking. At this time, no Ohio soil samples has contained nematodes capable of growing on PI437654 at elevated levels (Therese Miller & Christopher Taylor, unpublished). Because these soils contain nematodes adapted to reproducing on the most commonly used genetic source of SCN-resistance in soybean, additional methods of nematode management must also be utilized.

SCN management: Cultural (crop rotation)

Crop rotation with SCN non-hosts is an effective strategy to reduce nematode impact.

Over 20 crops are suggested for use in rotation with soybean as poor- or non-hosts of SCN

(Niblack & Tylka, n.d) Trials have demonstrated that planting corn (non-host) in an infested field increased soybean yield in the subsequent season compared to treatments with continuous soybean (Porter et al, 2001; Sasser & Uzzell, 1990). The number of SCN eggs in soil decreased over time when growing corn in a field previously planted with soybean, but when soybeans were planted in an SCN-infested field after multiple seasons of corn, SCN populations rebounded (Porter et al, 2001). Rotations using bahiagrass and velvetbean, a leguminous cover crop, were also effective at reducing SCN and increasing soybean yield, as compared to a continuous soybean planting, however neither of these crops is widely grown in most of the soybean growing region of the United States (Hancock et al, 2017; Weaver et al, 1993; Weaver et al, 1998; USDA-NASS, n.d. b, UDSA-NRCS, n.d.). Niblack (2005) and Niblack and Tylka

(n.d) also suggest rotating different SCN-resistant cultivars. In this approach, the nematodes present may have to overcome multiple sources of resistance which may slow their adaptability to growing on soybean.

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SCN non-hosts produce compounds which may contribute to nematode control. In greenhouse experiments, a variety of plant residues, including clover and ryegrass, were incorporated into soil and decreased nematode numbers after 8 weeks (Riga et al, 2001). This suggests the residues contain nematocidal compounds. Additionally, plant root exudates

(including clover, ryegrass, and corn) have been shown to alter (both increasing and decreasing) the hatching rate of SCN eggs as compared to either soybean or water controls (Medina, 2016;

Riga et al, 2001). Much is unknown about the individual bioactive compounds within plant residues and root exudates. The importance of selecting the proper non-host, cover crop, host, and rotation length suggests that careful planning must be used to establish the best crop rotation strategy.

SCN management: Chemical (synthetic nematicides and fumigants)

Chemical nematicides and less targeted fumigants have been sold for decades, however, they are not the optimal strategy for SCN control. Through the years multiple active ingredients in nematicides and fumigants including 1,2-Dibromo-3-chloropropane (DBCP), methyl bromide, and aldicarb have been banned or limited by the EPA and/or individual states due to their serious human health and environmental consequences (Osteen, 2003; Tomasko, 2018; USEPA, 2000;

USEPA, 2010). The nematicides and fumigants that are currently on the market have had varying levels of success in SCN control, both in terms of increasing yield and reducing nematode numbers in the soil. According to the Soybean Cyst Nematode Management Guide, while nematicides are available, they are rarely recommended for use (Niblack & Tylka, n.d)

De Bruin and Pedersen (2008) conducted field trials using the fumigant Telone® C-35

(Corteva AgriScience; 1,3-dichloropropene and chloropicrin) in combination with resistant and

11 susceptible soybean cultivars. Telone® did not affect all cultivars equally, contributing to significant yield increases in the susceptible cultivar and only one of the resistant cultivars. In both field and microplot testing of seed treatments Avicta® (Syngenta Corporation; Abamectin) and Aeris® (Bayer CropScience; Imidacloprid+Thiodicarb) on both SCN-resistant and - susceptible cultivars, there were no significant differences in yield (Frye, 2009). Additional field trials have demonstrated the minimal effect of Avicta® on both SCN-susceptible and -resistant cultivars (Ahmed et al 2018, Yabwalo et al, 2019). Finally, BASF recently introduced a new product, ILeVO® (Fluopyram), to control SCN. Greenhouse and laboratory trials have demonstrated that ILeVO® significantly reduced nematode reproduction on susceptible cultivars, and both seed and radicle exudates of nematicide treated susceptible seed significantly reduced egg hatching (Beeman & Tylka, 2018). Field efficacy of ILeVO® is varied (Ahmed et al, 2018;

Yabwalo et al, 2019). While nematicides and fumigants may be a useful strategy to mitigate yield loss, selection of cultivar is important. SCN-susceptible seed grown on a field treated with

Telone® had significantly increased yield than non-treated plots, however the yields of all SCN- resistant cultivars were significantly higher than the susceptible cultivar in fumigated soil (De

Bruin & Pedersen, 2008). Alternatively, ILeVO® treated SCN-susceptible seed resulted in yields significantly higher than the untreated control, and comparable to all treatments of the SCN- resistant cultivar (Yabwalo et al, 2019).

SCN management: Biological control

Multiple biological products are sold commercially to control SCN. The bio-nematicides available in the United States are bacteria based or derived. Bacterial-based products sold specifically to target soybean cyst nematode include Clariva® (Syngenta Corporation, active

12 microbe Pasteruia nishizawae Pn1), Poncho®/VOTiVO® (BASF, active microbe Bacillus firmus

I-1582), Aveo® EZ (Valent Biosciences, active microbe B. amyloliquefaciens PTA 4838), and

BioST® Nematicide 100 (Albaugh LLC, rinojensis A396). The aforementioned products all use whole (living or dead) microorganisms in their formulations. N-Hibit® (Plant

Health Care) is a bioproduct that uses bacteria derived Harpin αβ proteins. Genetically engineered Escherichia coli produces the protein, which is harvested and purified in the production formulation process (USEPA-OPP, n.d.). Like chemical nematicides, the efficacy of biological nematicides is varied. Multiple studies demonstrated that Clariva® neither produces significant yield increases nor nematode end-of-season-population decreases (Ahmed et al 2018;

Musil et al, 2015; Yabwalo et al, 2019). Alternatively, in a series of small-scale field experiments with Clariva®, Bissonnette et al (2018) saw yield increases in some plots but not others. Poncho®/ VOTiVO® studies had variability in egg reduction and yield increase, and efficacy can vary by study (Ahmed et al, 2018; Chilvers et al, 2012; Musil et al, 2015) In 2007 field trials with SCN-susceptible and -resistant seed treated with N-Hibit® (Plant Health Care, harpin protein) there was no significant effect on end of season SCN egg density. Of all seed treatments a significant yield increase was seen only in two of the treated SCN-susceptible seed plots as compared to the untreated control (Tylka & Marrett, 2008). Finally, Aveo® EZ had no effect on nematode populations, but had varied effects on yield in 2017 and 2018 field trials

(Tylka, 2019). To the best of my knowledge, there is no publicly available trial data on BioST® against SCN. The commercial biological products have different modes of action. P. nishizawae

Pn1, the active ingredient in Clariva® Complete is an obligate parasite of the nematode, and prevents SCN infection by directly infecting SCN juveniles, which subsequently alters the ability of the nematode to infect the soybean roots (Syngenta, 2013). Alternatively, B. firmus I-1582

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(Poncho®/VoTiVO®) and B. amyloiquefaciens PTA 4838 (Aveo® EZ) colonize the plant roots and prevent infection by acting as physical barriers of entry to the juvenile SCN (BASF, n. d.;

Valent Biosciences, n.d.). Burkholderia rinojensis A396 (BioST®), in contrast to the other microorganisms, is applied as a dead microbe, and the modes of action is though enzymes and in the growth medium (Albaugh, n.d.). The Harpin αβ protein in N-Hibit® induces systemic acquired resistance in treated plants, rather than directly targeting the pathogen

(USEPA-OPP, n.d).

Substantial effort has been expended into discovering additional “novel” microbes for use in SCN control. Marrone BioInnovations, Inc. submitted product registration with the EPA in

2013 for MBI-302, a formulation containing Flavobacterium sp. strain H492 (Marrone Bio

Innovations, 2013). While MBI-302 is not yet a commercially available product, isolates within this genus can reduce SCN activity. Two isolates of Flavobacterium johnsoniae showed activity against nematodes in greenhouse trials (Tian et al, 2000). Additional studies have investigated the potential for additional bacteria (including Bacillus and Burkholderia) as SCN biocontrol agents (Kloepper et al, 1992; Xiang et al, 2017). Fungi have also been investigated as biocontrol agents. Multiple studies demonstrated the ability of a collection of fungi isolated from soil across the Mid-South United States to parasitize SCN at multiple life stages in vitro and in greenhouse assays (Kim & Riggs 1991; Timper et al, 1999). Despite the potential of this fungal collection, a commercial product was not developed. At present there are no commercial, fungal-based biological nematicide for Soybean Cyst Nematode.

Finally, our lab has a collection of Pseudomonas spp. strains with demonstrated nematode activity against SCN in greenhouse trials, reducing cyst numbers compared to the

14 control (Aly, 2009; Xiao-Yuan Tao and Christopher Taylor, unpublished). The collection of bacterial strains used by Aly (2009) was used in many of the studies presented in future chapters.

1.4.2 Fusarium oxysporum management strategies

Genetics, soil disinfestation, biocontrol and best cultural practices are among strategies used to control diseases caused by Fusarium oxysporum. According to the Midwest Vegetable

Production Guide for Commercial Growers 2020 there are no fungicides recommended for control of Fusarium wilt of tomato (Egel, 2020). Metam sodium has been recommended as a fumigant for managing Fusarium crown and root rot of tomato, especially when combined with solarization, however efficacy of this compound is varied and could depend upon the method of application (Davis & Paulus 2014; McGovern et al, 1998). There are a limited number of fungicides recommended for control of Fusarium wilt and other Fusarium diseases in other crops, however additional methods of control are commonly suggested and will be discussed in the subsequent paragraphs (Egel, 2020).

F. oxysporum management: Genetics (resistance)

Grafting and resistant tomato cultivars are two commonly used methods to control the pathogen in a variety of crops (Egel, 2020). Many commercial tomato varieties (both seed and rootstock used for grafting) have resistance to a multitude of diseases including both Fusarium wilt and Fusarium crown rot (McGrath, n.d.). In a field trial where heirloom tomato scions were grafted to F. oxysporum f.sp. lycopersici resistant rootstock, disease incidence was significantly reduced in the plants with resistant rootstock, however significant increases in yield varied between field sites (Rivard & Louws, 2008). On the other hand, compared to the control plants

15 watermelon scion grafted with F. oxysporum f. sp. niveum race 2 resistant rootstocks grown in a severely infested field had significantly lower disease incidence and a significantly higher proportion of marketable-sized fruit (Keinath & Hassel, 2014). While grafting may be an effective tool, the economic benefit of resistant rootstock can depend on high enough disease pressure (and as it relates to yield not lost due to disease), particularly due to the high cost of grafted plants verses non-grafted (Rivard et al, 2010).

F. oxysporum management: Anaerobic soil disinfestation

Anaerobic soil disinfestation (ASD) has also been shown to control Fusarium oxysporum spp. In this strategy, organic amendments are first applied to soil infested with a phytopathogen, then the soil is saturated and covered to induce anaerobic conditions, and a subsequent decline in the pathogen population will occur (Testen & Miller, 2017b). One of the first reported accounts of ASD described control of F. oxysporum f. sp. asparagi (causal agent of crown and root rot of asparagus) added to soil amended with broccoli or grass clippings and covered in plastic. A similar level of control was not achieved with only the vegetal matter or plastic (Blok et al 2000).

F. oxysporum f. sp. lycopersici viability was reduced when soil containing the inoculum was watered with ethanol and stored in an airtight box as compared to the water- and non- treated soil

(Momma et al, 2010).

F. oxysporum management: Biological control

Biological control is another management strategy for disease caused by Fusarium.

Multiple biofungicides including Mycostop® (AgBio, active microbe Streptomyces K61),

Prestop® (AgBio, active microbe Gliocladium catenulatum J1446) and RootShield® (BioWorks,

16 active microbe Trichoderma harzianum T-22) are registered for activity against a number of fungal and oomycete pathogens including Fusarium. In greenhouse trials with F. oxysporum f. sp. radicis-cucumerinum (causal agent root and stem rot of cucumber) and the three

® aforementioned biological pesticides, only cucumber seedlings inoculated with Prestop had significantly lower disease incidence than plants inoculated with only the pathogen (Rose et al,

2003). Addition of RootShield® or SoilGard® (Certis USA, active microbe Trichoderma virens

GL-21) at sufficient rates to the potting media significantly reduced Fusarium wilt in F. oxysporum inoculated tomatoes (Larkin & Fravel, 1998). Many additional studies have investigated the potential of additional microorganisms (including Pseudomonas) to control both

Fusarium wilt and Fusarium crown and root rot (Larkin & Fravel, 1998; Mao et al, 1998;

McGovern, 2015; Rezzonico et al, 2007).

1.5 Pseudomonas

Pseudomonas is a diverse genus of gram-negative bacteria belonging to the λ- family. According to the List of Prokaryotic Names With Standing in

Nomenclature database, as of April 2020 there are over 300 species listed as Pseudomonas

(Parte, 2018). The number of species in this list is fluid, as species continue to be discovered and species reclassification occurs. Phylogenetic analysis of 141 strains has revealed Pseudomonas to be primarily divided into two distinct lineages, “P. fluorescens” and “P. aeruginosa.” (Mulet et al, 2012). Individual species within the genus cluster into phylogenetically distinct groups and sub-groups based on the 16S rDNA and housekeeping genes sequences. All of the Pseudomonas strains worked with in subsequent chapters of this dissertation are part of the group, but represent multiple subgroups based on species designation. Likewise,

17 most (if not all) of the plant pathogenic and biocontrol species described in this dissertation are part of the Pseudomonas fluorescens lineage (Anzai et al, 2000; Mulet et al, 2012).

Pseudomonads are found in a variety of environments, including soil, water, plants, and animals and occupy a variety of ecological niches.

1.5.1 Pathogenic Pseudomonas

Some species of Pseudomonas are pathogenic, including P. aeruginosa and P. syringae, which respectively infect humans and plants. Between 2011-2014, P. aeruginosa was the 6th most prevalent pathogen cause of healthcare associated infections in the United States, accounting for 7.3% (29,636 of a reported 365,490 pathogen infections) as reported to the CDC.

P. aeruginosa was found in a variety of infection types including surgical site infections, ventilator-associated pneumonias and catheter-associated urinary tract infections (Weiner et al,

2016). Additionally, individuals with cystic fibrosis (CF) are particularly susceptible to P. aeruginosa infection. In 2016, out of 29,497 patients in the United States with CF, over 46% tested positive for P. aeruginosa (Cystic Fibrosis Foundation, 2016). Epithelial cells from cystic fibrosis patients were conducive for bacteria growth, while cells from healthy individuals had bactericidal activity (Smith et al, 1996).

In 2012 plant bacteriologists associated with Molecular Plant Pathology voted P. syringae (all pathovars) to be the most important bacterial plant pathogen, taking both scientific and economic impact into consideration (Mansfield et al, 2012). The P. syringae group has over

60 pathovar types of P. syringae and other plant pathogenic Pseudomonas species (Baltrus et al,

2017). These bacteria primarily cause symptoms in the aboveground portion of the plant, including , bacterial blight, bacterial canker, and galls, but can also affect the root

18 portion. Disease symptoms vary by host plant and pathovar type. (Höfte & De Vos, 2007). P. syringae can cause significant monetary loss in crops. An outbreak beginning in 2010 of P. syringae pv actinidiae (Psa) on kiwifruit had devastating effects on the New Zealand economy.

In 2012 it was estimated that Psa would cost the economy between 2012-2017 310-410 million

(NZD), with thousands of jobs lost and reduced fruit production (Greer & Saunders, 2012).

1.5.2 Beneficial Pseudomonas

Multiple strains of Pseudomonas have demonstrated beneficial activity through disease control or plant growth promotion. As of 2018 nine Pseudomonas strains were registered as biopesticide active ingredients with the United States Environmental Protection Agency, and many more strains have been investigated as biological control agents (USEPA, 2018). Burr et al

(1978) identified P. fluorescens and P. putida strains which were both antagonistic towards

Erwinia carotovora pv. carotovora in in vitro assays and increased yield of inoculated potatoes as compared to uninoculated controls in field trials. A collection of Pseudomonas strains isolated from water, soil and plants have exhibited biocontrol activity in in vitro assays against several bacterial and fungal phytopathogens including Fusarium graminearum, F. solani, Pythium irregulare, P. cryptoirregulare, Rhizoctonia solani, solanacearum, Botrytis cinera, and Sclerotinia sclerotiorum (Aly, 2009; Martin, 2017; Mavrodi et al, 2012; McSpadden

Gardener et al, 2005; Raudales et al, 2009; South et al, 2020; Subedi et al, 2019). The

Pseudomonas strains mentioned here were also tested in subsequent chapters of this dissertation.

Multiple pseudomonads have been reported to affect plant parasitic nematode activity. For example, Pseudomonas fluorescens F113 both increased the hatch rate and decrease juvenile of Globodera rostochiensis (Cronin et al, 1997). Both root knot nematode (Meloidogyne

19 javanica) and soil fungal pathogens were inhibited with the addition of P. aeruginosa IE-6S+ and

P. fluorescens CHA0 (Siddiqui & Shaukat, 2002; Siddiqui et al, 2006).

In addition to beneficial results achieved though adding bacteria into the system, disease control also occurs though antagonistic activity by native Pseudomonas populations in the rhizosphere. Some soils contain native microorganisms that suppress pathogen activity though general or specific mechanisms. Pseudomonas present in suppressive soil contributes to the control of take all disease (TAD) (causal agent Gaeumannomyces graminis var. tritici) in wheat through the production of various antifungal metabolites. Higher levels of beneficial pseudomonads indicated soil less conducive to TAD (Weller et al, 2002).

Pseudomonads, both singular strains and in suppressive soils, use one or a combination of mechanisms to control plant disease and promote plant growth. Within each mode of action, the plant pathogen is controlled by biocontrol agents either through antagonism or induction of systemic resistance in the plant. Some important mechanisms used by Pseudomonas in biocontrol will be described here. The collection of Pseudomonas strains used in the subsequent chapters of this work (Chapters 2, 3, and 4) may use one or multiple of the mechanisms described here in their bioactivity against phytopathogens. Full genome sequencing and analysis on the collection of bacteria has indicated the presence of genes coding for , secretion systems, and antimicrobial compounds (Xiao-Yuan Tao & Christopher Taylor, unpublished data).

Pseudomonas biocontrol: Siderophores and competition

Antagonistic pseudomonads can control phytopathogens though competition for nutrients and root space in the soil. Iron is an essential nutrient required by many living organisms but is

20 predominantly present in the soil in its non-bioavailable, insoluble form. Microorganisms, including Pseudomonas, produce siderophores, metal-chelating agents, to solubilize iron in the soil (Andrews et al, 2003). Removing essential nutrients from the soil can be an effective competition strategy. Pseudomonads can produce multiple siderophores including , which is widespread across many species, pyochelin, and quinolobactin (Budzikiewicz, 1997;

Cox et al, 1981; Mossialos et al, 2000). In environments with low iron availability, - producing Pseudomonas were antagonistic towards fungal and bacterial phytopathogens, while the antagonism was lost in the presence of high bioavailable iron. (Duijff et al, 1994; Kloepper et al, 1980a; Xu & Gross, 1985). A siderophore-producing P. putida strain was able to control fusarium wilt in carnation while a siderophore-lacking mutant was unable to, indicating that within certain bacteria siderophores may be involved in disease control (Duijff et al, 1994).

Siderophores can also contribute to the effectiveness of suppressive soil; soil originally conducive to either fusarium wilt or TAD became suppressive though the addition of

Pseudomonas or purified siderophores, and suppressive soil became conducive to disease with the addition of Fe3+ (Kloepper et al, 1980b).

In addition to suppressing disease, siderophore-producing bacteria can also promote plant growth and yield. In low Fe3+ soil, both siderophore-producing Pseudomonas B10 and pure siderophore inoculated on potatoes significantly enhanced plant growth, while the effect was lost in high Fe3+ soil (Kloepper et al, 1980a). Similarly, in greenhouse and field trials, potato seed tubers treated with siderophore-producing WCS358 had significantly higher root weights and yields than the non-inoculated and WCS358-siderophore mutant treatments (Bakker et al, 1988).

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Siderophores produced by other microorganisms can affect the bioactivity of those produced by the biocontrol agent. Pseudomonas strains were unable to antagonize siderophore producing Escherichia coli K-12 AN194 but were active against siderophore-lacking E. coli K-

12 AN193. (Kloepper et al, 1980a). Alternatively, in greenhouse assays siderophore-producing

Pseudomonas putida A12 was active against pathogenic, siderophore-producing fusaria (Scher &

Baker, 1982). These examples indicate bioactivity can depend on a number of factors, including the ability of competing microorganism to also produce siderophores.

Another competition strategy used by Pseudomonas is niche exclusion. Beneficial bacteria can outcompete the pathogen if both organisms occupy the same niche in the rhizosphere. Confocal laser microscope analysis revealed that beneficial P. chlororaphis

PCL1391 and P. fluorescens WCS365, and pathogenic F. oxysporum f. sp. radicis-lycopersici all colonized tomato- root cellular junctions. When the pseudomonads were present fungal colonization of the root cells was inhibited (Bolwerk et al, 2003). Similarly, P. fluorescens

PCL1751 treated tomato seeds had significantly lower disease as compared to the non-treated control when planted into F. oxysporum f. sp. radicis-lycopersici infested soil. PCL1751 neither induced systemic resistance (in contrast, WCS365 induced resistance) in inoculated tomato plants nor was bioactive in vitro, which indicates the bacteria may compete with the through niche exclusion (Kamilova et al, 2005).

Pseudomonas biocontrol: Secretion systems

There are six known secretions systems used by gram-negative bacteria. Pseudomonads may contain one or multiple secretions systems which can directly antagonize other microorganisms. Described here are type three (T3) and type six (T6) secretion systems (SS),

22 which have been shown to play a role in the ability of Pseudomonas to control phytopathogen activity.

Pseudomonas biocontrol: Type three secretion systems

T3SS was first characterized in many gram-negative animal- and plant- as a mechanism of protein transport from the pathogen to the host organism (Hueck,

1998). While there are at least seven characterized families of T3SS across all plant and animal associated bacteria, three types of T3SS are known to be utilized by Pseudomonas: Hrp/Hrc-1, -3

(hypersensitive response and pathogenicity; requires respectively presence of hrp/hrc1 and hrp/hrc2 gene clusters), and SPI-1 (Salmonella pathogenicity island; requires presence of inv/mxi/spa-like gene cluster). The structure of the T3SS gene clusters is not conserved across all

Pseudomonas species and strains (Egan et al, 2014; Loper et al, 2012; Tampakaki et al, 2010). In plant pathogenic bacteria including Erwinia spp., , and P. syringae the

T3SS is involved in inducing hypersensitive response (HR), programmed cell death of infected cells in resistant plants, and causing disease in susceptible plants (Hueck, 1998; Tampakaki et al,

2010). Bacteria that have these gene clusters can produce a multitude of proteins which play a role in bacteria pathogenicity. Harpin and harpin-like proteins are well characterized effector proteins that play a role in Pseudomonas phytopathogenicity via T3SS Hrp/Hrc (Tampakaki et al, 2010). Wei et al (1992) originally isolated harpin (hrpN) from E. amylovora Ea321. When either pure bacteria culture or isolated proteins were infiltrated into tobacco (non-host of E. amylovora) leaves HR was induced; this activity was lost upon of the hrpN gene (Wei et al, 1992). Since the original discovery of harpin in Erwinia, additional harpins produced by P.

23 syringae (HrpZ (HrpZ1), HrpW (HrpW1), HopAK1) have been identified as elicitors of HR in tobacco (Charkowski et al, 1998; He et al, 1993; Kvitko et al, 2007).

Beneficial Pseudomonas strains across multiple species also contain the genes coding for

T3SS. In a comparative genomic analysis, Loper et al (2012) identified the presence of gene clusters rsp/rsc (rhizosphere-expressed secretion protein and rsp- conserved), similar to the hrp/hrc gene clusters of Hrp1 of phytopathogenic Pseudomonas, in six known biocontrol strains across three species (P. fluorescens, P. brassicacearum, P. synxantha). Additionally, one of these strains also contained similarity to a SPI-1 family T3SS gene of Salmonella enterica (Loper et al,

2012). There is evidence for the importance of T3SS in P. fluorescens SBW25, one of the isolates studied in Loper et al (2012), for rhizosphere colonization. On inoculated sugar beet root tips, wild-type SBW25 were significantly better colonizers than select rsp mutants (Jackson et al,

2005). This indicates the T3SS may play a role in niche exclusion in a system where a pathogen is present. The T3SS can also play a role in phytopathogen control. Rezzonico et al (2005) demonstrated plant growth promotion of Pythium ultimum infected-cucumber seedlings inoculated with P. fluorescens KD as compared to its hrcV mutant and the untreated control.

Neither P. fluorescens SBW25 nor KD were able to elicit the traditional T3SS HR in inoculated plants, further demonstrating that the role of the T3SS varies between pathogenic and beneficial bacteria (Preston et al, 2001; Rezzonico et al 2004).

Pseudomonas biocontrol: Type six secretion systems

T6SS is present across multiple classes of gram-negative bacteria including alpha- proteobacteria, beta-proteobacteria, and gamma-proteobacteria. It plays a role in multiple bacterial functions including the interbacterial competition, host manipulation, and

24 formation. Many Pseudomonas strains (including human pathogenic, plant pathogenic and non- pathogenic strains), contain gene sequences encoding for the secretion systems, although differences occur both in T6SS copy number and type (genetic structure and secreted proteins) among different species and strains (Bernal et al, 2017; Bernal et al, 2018; Filloux et al, 2008).

Within the Pseudomonas genus, multiple gene clusters code for T6SS proteins. P. aeruginosa contains three T6SS gene loci (Hcp (Haemolysin A co-regulated protein) Secretion Island (HSI)-

I, -II, -III). The HSI loci contain genes coding for both secreted (Hcp and VgrG) and non- secreted proteins (Filloux et al, 2008; Lesic et al, 2009; Mougous et al 2006). The T6SS loci play a role in P. aeruginosa virulence in animal and plant systems. Deletion of both the HSI-II and -

III clusters in P. aeruginosa PA14 both significantly decreased the mortality rate of mice infected with the bacteria and lowered the amount of bacteria colonizing inoculated Arabidopsis thaliana plants as compare to the controls (Lesic et al, 2009).

The T6SS can also play a role in beneficial plant bacteria controlling phytopathogenic bacteria. Wild type P. fluorescens MFE01, capable of secreting Hcp- and VgrG-like proteins, was able to inhibit both Pectobacterium atrosepticum growth in vitro in co-culture assays and soft-rot on potato tubers inoculated with P. atrosepticum, while treatment with the Δhcp2 mutant was comparable to the controls (Decoin et al, 2014). P. putida KT2440 has three main T6SS clusters (KI, -II, -III) as well as hcp and vgr “orphan” clusters. When subjected to competition assays with campestris, Nicotiana benthamiana leaves treated with KT2440 had less leaf tissue necrosis and X. campestris colonization as compared to the control and

KT2440ΔT3SS triple mutant. KT2440 has 10 potential T6SS effector proteins, all of which may play a role in bioactivity against prey bacteria (Bernal et al, 2017).

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Pseudomonas biocontrol: Antimicrobial secondary metabolites

Pseudomonads can produce numerous secondary metabolites that demonstrate antagonistic activity against competing organisms. Many bacteria produce more than one antibiotic and bioactivity can be due to a combination of metabolites. Many of the antimicrobial compounds (including secreted, volatile, and siderophores) produced by Pseudomonas (both antagonistic and beneficial strains) are controlled by presence of the GacA/GacS (global activator of antibiotic and cyanide synthesis) system (Heeb & Haas, 2001). For example, unlike their wildtype, gacA mutants of P. fluorescens CHA0 produced negligible to no 2,4- diacetylphloroglucinol (DAPG), pyoluteorin, and hydrogen cyanide (HCN) (Laville et al, 1992).

Likewise, Gac mutants of additional Pseudomonas strains were unable to produce select volatile compounds (including HCN, organosulfur compounds, and 2R, 3R-butanediol) (Han et al, 2006;

Ossowicki et al, 2017). Bacterial production of certain metabolites can be associated. For example, Rezzonico et al (2007) found that over 98% of DAPG producers also produced HCN; however, the inverse was not true: many HCN producers did not produce DAPG. Genetic analysis of the Pseudomonas collection used in this work revealed this same association of

DAPG and HCN (Xiao-Yuan Tao & Christopher Taylor, unpublished) (Table 2.1). Described below are some examples of antimicrobial secondary metabolites, including both non-volatile and volatile compounds.

Pseudomonas biocontrol: Non-volatile antimicrobials

Beneficial pseudomonads can produce numerous antimicrobial metabolites including, but not limited to, DAPG, phenazines, and pyrrolnitrin. Weller et al (2002) proposed that within a wheat monoculture system, soil suppressiveness increases with the increasing abundance of

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DAPG producing bacteria. P. fluorescens CHA0, a known DAPG producer, has shown inhibitory activity against several pathogens. Wildtype CHA0 was able to inhibit both F. oxysporum and G. graminis var. tritici in vitro while inhibition was not seen with the DAPG- deficient mutant (Keel et al, 1992). Disease severity in tobacco plants inoculated with both

Thielaviopsis basicola and CHA0 was reduced, while mutants were comparable to the controls

(Keel et al, 1992; Laville et al, 1992). Similarly, tomato plants co-inoculated with Clavibacter michiganensis subsp. michiganensis and Pseudomonas sp. LBUM300 had better disease control than plants co-inoculated with the pathogen and a LBUM300 DAPG-minus mutant (Lanteigne et al, 2012). Genotypic variation of the phlD (DAPG marker) gene occurs across Pseudomonas, which leads to varied biocontrol activity of individual bacteria. In vitro inhibition assays against

Pythium using Pseudomonas strains representative of four phlD genotypes had mixed results, dependent on the nutrient composition of the media used (McSpadden Gardener et al, 2005).

Synthetic DAPG inhibited the growth of multiple fungal and bacterial pathogens and reduced potato cyst nematode (Globodera rostochiensis) juvenile mobility (Cronin et al, 1997; Keel et al

1992).

Pseudomonads can also produce multiple phenazines (e.g. and -1- carboxylic acid), some of which have known biocontrol potential. The efficacy of the compounds in the control of microorganisms can be dependent on multiple factors including pH and quorum sensing of the beneficial bacteria (Cezairliyan et al, 2013; Chin-a-Wong et al 1998;

Wood & Pierson, 1996). Phenazine producing pseudomonads (wild type or mutants) were able to significantly inhibit C. elegans in vitro and reduce symptoms of multiple fungal diseases in planta as compared to their PCA-deficient mutants (Arseneault et al, 2013; Cezairliyan et al,

2013; Chin-A-Woeng et al, 1998; Thomashow & Weller, 1988). Additionally, pyocyanin

27 producer P. aeruginosa 7NSK2 controlled foliar phytopathogens through induction of systemic resistance in inoculated plants while the pyocyanin-mutants were comparable to the control treatments (Audenaert et al, 2002; De Vleesschauwer et al, 2006). The activities of individual phenazines have been investigated for antagonistic activity towards microorganisms both in vitro and in planta (Cezairliyan et al, 2013; Chin-A-Wong et al, 1998; De Vleesschauwer et al, 2006;

Gurusiddaiah et al, 1986)

Pyrrolnitrin also plays a role in the biocontrol potential of pseudomonads. Originally isolated from a Pseudomonas and characterized by Arima et al (1964), the antibiotic showed activity against multiple human bacterial pathogens. In addition, pyrrolnitrin is effective in vitro or in planta against multiple fungal phytopathogens (Howell & Stipanovic, 1979; Pfender et al,

1993) Studies have also investigated the biocontrol potential of P. fluorescens strains capable of producing pyrrolnitrin. Fungal pathogen (Sclerotinia homoeocarpa and Pyrenophora tritici- repentis) growth was inhibited with addition of P. fluorescens Pf-5 to inoculum containing the fungus as compared to the negative controls and pyrrolnitrin-deficient mutants (Pfender et al,

1993; Rodriguez & Pfender, 1997). Damping off (causal agent R. solani) was also significantly reduced by treating seeds with P. fluorescens strains BL915 or PF-5 before planting in inoculated soil as compared to the control (Hill et al, 1994; Howell & Stipanovic 1979). Insertion of pyrrolnitrin biosynthesis genes into Pseudomonas strains that were both unable to produce the antibiotic and were not inhibitory against R. solani in vitro enabled them to antagonize the pathogen in vitro and produce a measurable amount of pyrrolnitrin (Hill et al, 1994).

Pseudomonas biocontrol: Volatile antimicrobials

Many pseudomonads, representative of both pathogenic and beneficial bacteria, spread across the genus can produce volatile organic compounds (VOCs) with antagonistic activity

28 against a wide diversity of pathogens. Some well characterized antimicrobial volatiles include

HCN, organosulfur compounds, and hydrocarbons. HCN was fully inhibitory to nematodes (C. elegans) and fungus (Puccinia recondita f. sp. tritici and Septoria tritici) (Flaishman et al, 1996;

Gallagher and Manoil 2001). In vitro volatile assays with HCN-producing pseudomonads demonstrated antagonistic activity against multiple plant pathogens (Ahl et al, 1986; Hunziker et al. 2015; Ossowicki et al, 2017). Multiple studies determined cyanide production and control against black root rot (causal agent Thielaviopsis basicola) in tobacco were substantially higher in P. protegens (formerly P. fluorescens) CHA0 than multiple HCN-deficient mutants (anr, gacA and hcn) while the complemented mutants had restored activity to varying extents (Laville et al,

1998; Laville et al, 1992; Voisard et al, 1989). HCN-producing Pseudomonas strains have also been investigated against nematode species. C. elegans and Meloidogyne javanica were inhibited to varying extents by HCN-producing pseudomonads as compared to their cyanide-mutant strains (Gallagher & Manoil, 2001; Siddiqui et al, 2006). Addition of amino acids including glycine (direct precursor to HCN) and threonine to the media enhanced cyanide production of pseudomonads (Aly, 2009; Castric, 1977; Gross & Loper, 2009; Kang et al, 2018).

Pseudomonads can also produce a variety of organosulfur compounds, some of which have demonstrated antimicrobial activity. Organosulfur volatiles produced by bacteria are originally derived from methionine converted into methanethiol, which is subsequently converted into more complex molecules including sulfides and thioesters (Carrión et al, 2015;

Yvon & Rijnen, 2001). One well studied organosulfur compound is dimethyl disulfide (DMDS), which is currently sold commercially as an alternative to the fumigant methyl bromide (Paladin®,

Arkema Inc, France) (USEPA, 2012). When applied to soil in field trials as a synthetic fumigant

(rate 300-600 liters/ha), DMDS decreased disease caused by Meloidogyne spp. and F. oxysporum

29 f. sp. radices-lycopersici (Gómez-Tenorio et al, 2018; Leocata et al, 2014). Multiple

Pseudomonas strains capable of inhibiting fungal pathogens in vitro produced organosulfur compounds including dimethyl sulfide (DMS), DMDS, dimethyl trisulfide (DMTS), and S-

Methyl methanethiosulfonate (MMTS), as measured in the headspace of cultures using GC-MS.

Some studies reported that DMDS was one of the most abundant VOCs quantified in the headspace (Briard et al, 2016; De Vrieze et al, 2015; Hunziker et al, 2015; Ossowicki et al, 2017;

Zhou et al, 2014). Activity of organosulfur compounds can vary against specific organisms. Pure

DMDS and/or DMTS inhibited select bacterial, fungal, and oomycete pathogens to varying extents when exposed indirectly to the microorganism (Briard et al, 2016; De Vrieze et al, 2015;

Ossowicki et al, 2017; Zhou et al, 2014). DMTS and MMTS were more effective at inhibiting P. infestans mycelial growth and spore production/germination than DMDS (De Vrieze et al, 2015).

Not every organosulfur compound is inhibitory, and inhibition may be environment dependent.

Both P. aeruginosa volatiles and DMS stimulated the growth of the human pathogen Aspergillus fumigatus. Additionally, both DMS and DMDS stimulated the growth of A. fumigatus when the fungus was grown on a sulfur-depleted medium (Briard et al, 2018).

Hydrocarbons are another class of VOCs commonly produced by Pseudomonas. 1- undecene (C11H22) was a highly abundant compound in the volatile profile of multiple strains

(De Vrieze et al, 2015; Hunziker et al, 2015; Lo Cantore et al, 2015; Ossowicki et al, 2017; Zhou et al, 2014). Control activity due to 1-undecene was dose dependent. Growth of fungi and oomycetes was lowered to when exposed to 1-undecene at high enough levels, however significance and degree of inhibition varied between both the organisms and chemical concentration (De Vrieze et al, 2015; Hunziker et al, 2015; Lo Cantore et al 2015; Zhou et al,

2014).

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Not all volatiles produced by Pseudomonas are involved in direct antagonism of a competing microorganism. 2R, 3R-Butanediol provides multiple benefits to inoculated plants. It can promote plant growth, yield, and ISR, as evidenced in both tobacco seedlings inoculated with Pectobacterium carotovorum (causal agent of soft rot) and pepper plants planted in soil naturally infested with multiple pathogenic viruses (Han et al, 2006; Kong et al, 2018). Drought symptoms in Arabidopsis thaliana were alleviated in plants inoculated with 2R, 3R-butanediol as compared the control (Cho et al, 2008). 2R, 3R-Butanediol producer

O6 both induced resistance to P. carotovorum in tobacco and alleviated drought symptoms in A. thaliana as compared to its gacS- mutant and controls. While the gacS complemented mutant restored activity (either partial or full), it is possible that the effect was due to a combination of factors including 2R, 3R-butanediol, as the GacA/GacS complex regulates many genes (Cho et al, 2008; Han et al, 2006).

Chapters 2 and 3 of this dissertation will focus on identifying the volatile profile of

Pseudomonas strains, their impact on plant pathogens, and determining whether the bacteria can be primed for the production of specific volatile compounds.

1.6 Commercial Pseudomonas-based products

Multiple Pseudomonas strains have been formulated for sale in the United States as either biopesticides or biostimulants. Microbial biopesticides are products that are microbe based, and specific in their target organisms. Per USEPA rules, despite them being considered less toxic and quicker to breakdown than conventional pesticides, sufficient data and product registration is still required for biopesticides to be made commercially available (USEPA, n.d.). Biostimulants on the other hand do not have a set definition or regulatory requirements in the United States but are

31 intended to enhance plant health though a variety of mechanisms (du Jardin, 2015). As of April

2020, the USEPA is working on framework for biostimulants, but no decisions are available on the topic (Dunn, 2019). A representative list of commercially sold Pseudomonas products in the

United States is found in Table 1.1. While the biopesticides listed in Table 1.1 contain only

Pseudomonas strains as the active ingredient, the biostimulants include the pseudomonad as part of a consortium.

Worldwide, companies are continuing to develop new microorganism-based products

(biopesticide and biostimulant). Chapter 4 of this dissertation will describe a collaboration with a biologicals company to determine the potential of Pseudomonas strains to control SCN; Chapter

5 will describe university-company relationships in regard to product discovery and development.

1.7 Objectives

The overarching goal of this dissertation is investigating the potential for Pseudomonas as biocontrol agents. To accomplish this, this work is divided into four primary objectives:

1) To determine the global volatile profile of a diverse collection of Pseudomonas strains

and identify the biocontrol potential of the bacterial volatiles.

2) To determine whether manipulation of the growth medium can enhance production of

specific VOCs and bioactivity of the bacteria.

3) To assess the potential of Pseudomonas to control SCN in the greenhouse and microplot

settings. This objective was conducted in collaboration with 3Bar Biologics Inc.

(Columbus, OH, USA).

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4) To investigate the potential for increased industry-university collaborations in the fields

of microorganisms and natural product discovery and development. This objective was

completed as part of the I-CORPS@Ohio training program.

33

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Xiang, N., Lawrence, K. S., Kloepper, J. W., Donald, P. A., & McInroy, J. A. (2017). Biological control of Heterodera glycines by spore-forming plant growth-promoting rhizobacteria (PGPR) on soybean. PLoS ONE, 12(7). https://doi.org/10.1371/journal.pone.0181201 Xu, G.-W., & Gross, D. C. (1986). Selection of fluorescent pseudomonads antagonistic to Erwinia carotovora and suppressive of potato seed piece decay. Phytopathology, 76, 414– 422. https://doi.org/10.1094/phyto-76-414 Yabwalo, D., Tande, C., & Byamukama, E. (2019). 2018 field plot summaries for soybeans: Plant disease and fungicide trials. South Dakota State University Extension. https://extension.sdstate.edu/sites/default/files/2019-02/P-00081.pdf Young, L. D. (1996). Yield loss in soybean caused by Heterodera glycines. Journal of Nematology, 28(4 SUPPL.), 604–607. Yu, N., Lee, T. G., Rosa, D. P., Hudson, M., & Diers, B. W. (2016). Impact of Rhg1 copy number, type, and interaction with Rhg4 on resistance to Heterodera glycines in soybean. Theoretical and Applied Genetics, 129(12), 2403–2412. https://doi.org/10.1007/s00122-016- 2779-y Yvon, M., & Rijnen, L. (2001). Cheese flavour formation by amino acid catabolism. International Dairy Journal, 11(4–7), 185–201. https://doi.org/10.1016/S0958- 6946(01)00049-8 Zhou, J. Y., Zhao, X. Y., & Dai, C. C. (2014). Antagonistic mechanisms of endophytic Pseudomonas fluorescens against Athelia rolfsii. Journal of Applied Microbiology, 117(4), 1144–1158. https://doi.org/10.1111/jam.12586

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Table 1.1. Representative list of commercially available Pseudomonas-based bioproducts in the United States. The target pathogens and crops may not be a comprehensive, but rather representative list of the bioproduct targets. For the most up to date information on each product, visit the manufacturers’ websites.

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Chapter 2

Determination of the Volatile Compounds Produced by Pseudomonas spp. Strains and

Establishing Their Role in Biocontrol

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2.1 Abstract

Biocontrol is has become an increasingly relied upon strategy in the control of certain phytopathogens. Bacteria as biocontrol agents can utilize multiple modes of action against competing microorganisms, including direct antagonism, secretion of antibiotics, and/or production of volatile organic compounds (VOCs). The study presented here investigated these three modes of action using Pseudomonas (19 strains representing eight different species) and

Pantoea agglomerans (one strain) against the fungal pathogen Fusarium oxysporum. We further characterized VOC action against the bacterial feeding nematode, Caenorhabditis elegans. We were particularly interested in the antagonistic volatiles and determined the global profile of each bacterium utilizing proton transfer reaction time-of-flight mass spectrometry (PTR-ToF-MS).

PTR-ToF-MS is a system that has been extensively used in the quantification and identification of volatiles in systems ranging from bacteria to fungi to fruit, however to the best of our knowledge this is the first study using this analytical system with Pseudomonas. We quantified

39 VOCs produced by Pseudomonas, Pantoea, and the controls, ranging in size from m/z (mass- to-charge ratio) 27.023 to 153.120 that were produced at levels >1ppbv. Six compounds were significantly correlated with inhibition of F. oxysporum, five of which were putatively identified as and organosulfurs. We found that production of hydrogen cyanide was required for bacterial VOCs to inhibit F. oxysporum, and in multiple strains cyanide was the dominantly measured compound; in contrast pseudomonads that did not produce any measurable cyanide were also able to inhibit the reproduction of C. elegans over a weeklong experiment. Of the nine bacteria species investigated, volatiles produced by P. fluorescens and P. protegens were the most effective in reducing growth or reproduction of F. oxysporum and C. elegans. Our findings demonstrated that the volatile profiles of bacteria are complex and can contribute to

50 microorganism inhibition. This work has laid the groundwork for future, more in-depth studies of bacterial volatile profiles and their role in microorganismal inhibition.

2.2 Introduction

Synthetic pesticides can be linked to negative human health and environmental downstream effects in addition to reduced crop yield and increased pest resistance, accounting for billions of dollars of lost economic value (Pimentel & Burgess, 2014). Biologicals are increasingly used to suppress plant diseases and pests (i.e. biocontrol) in agriculture as a substitute for or supplement to synthetic pesticides. Over the past few decades both the European

Commission and the United States Environmental Protection Agency (USEPA) have promoted biocontrol as a key part of integrated pest management programs. This is due in part to bioproducts’ reduced toxicity and increased target specificity as compared to some chemical pesticides. Additionally, use of biocontrol agents can provide help in preventing the buildup of target pest/pathogen resistance to commercially used pesticides (Chandler et al, 2011; Leahy et al, 2014). As the demand for organic food increases, the use of biocontrol products is also expected to rise to replace the use of synthetic chemical pesticides. To be labelled as organic by the US Department of Agriculture (USDA), synthetic chemicals may not be used on plants while non-synthetic substances (including biological products) may be applied, save for certain exceptions (National Organic Program, 2020). According to the market research company

DunhamTrimmer LLC, the value of the worldwide biocontrol industry will be as high as 11 billion USD by 2025, increasing over 100-fold from 1993 (Dunham, 2017). Many organisms, macro- and micro-, are used in biocontrol. Bacteria are commonly used biocontrol agents.

Bacillus spp. were the first microbial biopesticide active ingredients, registered with the USEPA

51 in 1971. Since then, dozens more strains representing multiple genera have been added to the list

(USEPA, 2018). One such widely studied bacterial genus for biocontrol potential is

Pseudomonas. There are currently three Pseudomonas strains that have been registered with the

USEPA and formulated into biopesticides to control bacterial and fungal diseases. Additional pseudomonads have been developed into biostimulants, which are beneficial to plants, but do not have marketed pesticide activity (Table 1.1).

Multiple species of Pseudomonas have demonstrated biocontrol activity. The bacteria show antagonistic activity towards a wide spectrum of pathogens under a variety of conditions

(Haas & Defago, 2005). Bioactivity from Pseudomonas is due to several modes of action including inducing systemic plant resistance (ISR), competitive niche exclusion and antibiotic production. Pseudomonads are capable of secreting multiple antibiotic compounds effective against competing microorganisms including 2,4-diacetyl phloroglucinol (DAPG), phenazine-1- carboxolyic acid (PCA), pyoluteorin, and pyrrolnitrin (Bolwerk et al, 2003, Haas & Defago,

2005, Van Loon & Bakker, 2008). These bacteria can also produce low molecular weight volatile organic compounds (VOCs), some of which have biocontrol potential. Unlike other compounds, VOCs are of particular interest because the source organism does not need to be in direct contact with the target plant or pathogen to have the desired effect.

Pseudomonads are capable of releasing VOCs representing multiple classes of compounds including alcohols, cyanides, hydrocarbons, and organosulfur compounds (Effmert et al, 2012). Some strains antagonize competing organisms using VOCs, as demonstrated with shared-air in vitro assays. VOCs including hydrogen cyanide (HCN), dimethyl disulfide

(DMDS), dimethyl sulfide (DMS) and undecene, can have antagonistic activity to varying extents against microorganisms including nematodes, fungi, and oomycetes (Briard et al, 2016;

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De Vrieze et al, 2015; Gallagher & Manoil 2001; Hunziker et al, 2015; Lo Cantore et al, 2015,

Ossowicki et al, 2017). Bacterial volatiles also play a role in promoting induced systemic resistance (ISR) in plants. Both pure 2R,3R-butanediol and Pseudomonas chlororaphis O6, which is capable of producing 2, 3-butanediol, induced systemic resistance in inoculated tobacco plants challenged with Pectobacterium carotovorum (Han et al, 2006).

It is imperative to choose the correct technique of volatile analysis. For example, Bean et al (2012) and Zhu et al (2010) analyzed the VOCs of the same Pseudomonas strain utilizing different methodology and quantified different volatiles for the strain. A commonly used method of global volatile profiling across Pseudomonas species is gas chromatography-mass spectrometry (GC-MS), or other iterations (solid phase microextraction GC-MS; GC-Qtime-of- flight-MS; closed-loop-striping analysis-GC-MS (Briard et al, 2016; Cellini et al, 2016; De

Vrieze et al, 2015; Hunziker et al, 2015; Labows et al, 1980; Lo Cantore et al, 2015; Ossowicki et al, 2017 ). One drawback when using these analytical techniques is the difficulty to measure

HCN. In the aforementioned examples, if HCN was measured, the authors used complementary experiments to the GC-MS. Alternatively, cyanide was quantified in blood samples analyzed with GC-MS and SPME GC-MS, which indicates to us that HCN could be quantified in bacteria samples using GC-MS/SPME GC-MS under the proper experimental and analytical conditions

(Calafat & Stanfill 2002; Frison et al, 2006). Two other mass spectrometry methods, selected ion flow tube mass spectrometry (SIFT-MS) and 2 dimensional GC-MS (GCxGC-time-of-flight

(ToF)-MS) have been used to identify the volatile compounds, including HCN, produced by P. aeruginosa (Bean et al, 2012; Carrol et al, 2005; Shestivska et al, 2011). Two-dimensional GC has greater sensitivity than 1-dimensional GC and allows substances to be separated by polarity as well as volatility, which can account for peak differentiation (Phillips & Xu, 1995). To the

53 best of our knowledge, SIFT-MS and GCxGC-ToF-MS technology have not been applied to other species of Pseudomonas. A newer method of volatile analysis is proton transfer reaction- mass spectrometry (PTR-MS). In this technique, the VOCs are protonated, and compound identification is done based on the protonated mass value. PTR-MS is sensitive (limit of detection at the parts-per-trillion scale) and capable of measuring very small compounds. One drawback of PTR-MS is low mass resolution, which results in an inability to differentiate isobaric compounds. This drawback led to the development of PTR-time of flight-MS (PTR-

ToF-MS) (Jordan et al, 2009; Yuan et al, 2017). The VOC profiles of multiple biological systems, including, fungi, bacteria, yeast, and fruit inoculated with bacteria have been investigated utilizing this system (Cellini et al, 2015; Infantino et al, 2017; Khomenko et al,

2017; Kuppusami et al, 2014; Vita et al, 2015). HCN can be detected using PTR-ToF-MS

(Moussa et al, 2016). We are not aware of any studies applying PTR-ToF-MS to determine the volatile profile of Pseudomonas strains, making this technique novel to our system.

The aims of this study were threefold. First, the biocontrol potential of 19 Pseudomonas strains representative of eight species and one Pantoea agglomerans strain, was investigated in vitro using nematode (C. elegans) and fungal (Fusarium oxysporum) systems to elucidate potential modes of action. Additionally, the global volatile profiles of the bacteria were analyzed using PTR-ToF-MS to determine which compounds are produced by the bacteria. Similarities and differences within the strains were investigated to identify patterns in volatile production between the species. Finally, in vitro assays were performed using hydrogen cyanide against F. oxysporum to determine the inhibitory activity of the individual compound.

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2.3 Materials and Methods

2.3.1 Microorganism maintenance

Bacteria: The 20 Pseudomonas spp. and Pantoea agglomerans strains used in this study were collected by the Taylor and Brian McSpadden Gardener (Ohio State) laboratories from river water, soil, and plant samples from across the United States. The origin and species of each strain are shown in Table 2.1. Species designation for the Pseudomonas strains is based off an analysis of 10 housekeeping genes (Loper et al, 2012; Xiao-Yuan Tao & Christopher Taylor, unpublished). Pantoea agglomerans MBSA-3BB1 was identified using 16S sequencing and deposited in GenBank (Molecular Cell Imaging Center (MCIC), Ohio State University, Ohio-

USA). Strains sourced from the Taylor lab were initially screened for in vitro activity against

Caenorhabditis elegans. This collection has previously been tested for biocontrol activity against phytopathogens including bacteria, fungi, and nematodes (Aly, 2009; Martin, 2017; Mavrodi et al, 2012; South et al, 2020; Subedi et al, 2019). Genome mining was performed on the strains to search for the presence of biocontrol-related gene clusters (including, but not limited to HCN,

DAPG, and phenazines) (Xiao-Yuan Tao and Chris Taylor, unpublished). Bacteria were stored in the long term as glycerol stocks at -80°C, and cultures were maintained on Luria-Bertani (LB) agar plates (1L: 10g tryptone, 5g yeast extract, 10g NaCl, 15g agar). In each assay, overnight culture (16 to 18-hour growth, Pseudomonas spp. and Pantoea agglomerans: 28-30°C, ~200-

225RPM, E. coli 37°C, ~200-250RPM) in 5±0.5ml LB liquid media was used.

Fungi: Fusarium oxysporum isolates from Ohio tomato high tunnels were obtained from

Dr. Sally Miller (The Ohio State University). In the experiments presented here, two isolates were used, F. oxysporum 289 and 197, taken from diseased tomato roots in high tunnels in Ohio.

Fungi were cultured on ½ potato dextrose agar (PDA) (1L: 19.5g DifcoTM Potato Dextrose Agar,

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7.5g agar). In the in vitro assays, six to eight-day-old old mycelial plugs (size 3 cork borer,

5/6mm inner/outer diameter) were used. Unless otherwise noted, fungal experiments were performed on ½ PDA plates (100mm) containing 20±0.5ml. The identity of the isolates was confirmed using ITS sequencing (MCIC, Ohio State University).

Nematodes: C. elegans were maintained on Nematode Growth Media (NGM) plates seeded with Escherichia coli OP50 as a food source. C. elegans were synchronized so that L1 stage juveniles were used in the in vitro assays. Eggs were harvested from adult nematodes using reagent recipes and a modified protocol from Stiernagle (2006). Briefly, under sterile conditions

C. elegans were washed from plates into a 15ml-tube using S Basal or M9 media and settled on ice. The supernatant was removed and an alkaline bleach solution (500µl 10N NaOH + 750µl commercial bleach + 5.75ml S. Basal or M9 medium) was added to the tube. After gently inverting the tube to mix, the worms sat in the bleach solution for 7-10 minutes, after which the tube was centrifuged at 750RPM (4ºC) for 5 minutes. The supernatant was removed, and eggs were transferred to a 50ml centrifuge tube with 15ml of S Basal or M9 media. The nematodes were washed 3 times in 15ml using the same centrifuge settings. Finally, harvested eggs were kept at 15°C. Eggs hatched after 24-hours and were viable for up to a few weeks after harvest.

Recipes for media used for C. elegans experiments are described in Stiernagle (2006).

2.3.2 Pseudomonas mode of action assays

Growth inhibition assays were performed in vitro to elucidate the mode of action of the bacteria. Bioactivity of each strain was tested against F. oxysporum 289 utilizing top agar, dual plating, and VOC exposure assays. F. oxysporum 197 and C. elegans were also used in the VOC exposure assays. An individual plate was considered an experimental unit. LB was used in each

56 assay as the negative control. In the C. elegans volatile assays, E. coli OP50 was also used as a negative control. Three or four experimental units were used per treatment in each fungal experiment. Five experimental units were used per treatment in each C. elegans experiment. All plates used in the experiments were sealed with at least three layers of parafilm and kept on the laboratory bench at ambient temperature and light conditions. Total fungal growth area was assessed after a one-week period, which included thicker “inner growth” and thinner “outer growth” mycelium (Supplemental Figure 1.1). In the fungal inhibition assays, total growth (full area of thin and thick hyphal growth) was measured. The proportion of “thin” and “thick” mycelial growth varied from plate to plate. Every bacterium was tested in two independent assays. Supplemental Figure 1.1 shows the experimental setup for each assay type.

Top agar assay: The top agar assay was used to determine activity associated with direct bacteria-fungal contact, metabolites in the supernatant, and volatile compounds produced by the bacteria. For each bacteria strain, 500µl of undiluted overnight culture was added to cooled, liquified 50ml of ½ PDA (0.75% agar). 10ml of the top agar bacteria suspension was pipetted on a 100mm plastic plate containing 15±0.5ml ½ PDA. A fungal plug was placed in the center of the plate on top of the solidified top agar.

Dual plating assay: The dual plating assay was used to determine activity due to compounds secreted into the growth medium and volatile compounds produced by the bacteria.

A fungal plug was placed in the center of a ½ PDA plate. A sterile inoculating loop was dipped into liquid bacterial culture and streaked three centimeters to the left and right of the plug, running the length of the plate.

VOC exposure assay: The VOC exposure assay was used to determine activity due to volatile compounds produce by the bacteria. The Pseudomonas VOC assays were done with both

57

F. oxysporum 289 and 197 and C. elegans. In the fungal assays, 100µl of overnight

Pseudomonas culture was spread on 100mm plastic plates containing 20±0.5ml LB agar. A fungal plug was placed in the center of a ½ PDA plate. The ½ PDA plates were inverted on top of the LBA plates and sealed with parafilm.

In the C. elegans assays, 30µl of overnight Pseudomonas or E. coli OP50 culture was spread on a 35mm plastic plate containing 3±0.3mL LB agar. Approximately 10-25 L1 stage C. elegans were added to 35mm plastic plates containing 3±0.3mL NGM and a freshly spread lawn of 30µl E. coli OP50. The NGM plates were inverted and placed on top of the LB plates and sealed with parafilm.

2.3.3 Pseudomonas single strain VOC measurement

+ Pseudomonas volatiles were measured by PTR-ToF-MS using H3O as reagent ions.

These experiments were conducted at the LINV (International Laboratory of Plant

Neurobiology) of the University of Florence (Tuscany-Italy). Overnight bacteria culture (50µl) was spread on a 60mm glass plate containing 10±0.2ml LB agar. Plates were sealed with parafilm and bacteria were grown at 28ºC for about 24 hours, at which point a bacteria lawn covered the plate. After the overnight growth period, the lid was removed, and the bottom half of each plate was placed in a 750 cubic-centimeter glass jar which was lidded and sealed with

TEROSON® RB IX (Rubix Group), an inert putty. Subsequently, each glass jar was flushed with zero air for 120 seconds through two Teflon tubes placed on the lid, after which the tubes were sealed with the putty and the samples were incubated for 20 minutes (Zero air generator, Peak

Scientific Instruments, USA). Bacteria had either two or three biological replicates. With the exception of three bacteria (P. brassicacearum 37D10, P. poae 36C8, P. chlororaphis 14D6),

58 three biological replicates of each strain were used for analysis. Those three strains had poor growth from one experimental run which were removed from analysis. With the exception of one bacterium (P. frederiksbergensis39A2), all bacteria had each biological replicate run on separate days. Two of the 39A2 replicates were run on one day. Bacteria growth varied from day to day, which may account for differences within the replicates. LB agar plates were used as negative controls, two in each experimental run. Additionally, clean air was flushed though the machine between all sample measurements, and to verify no contaminating volatiles were in the system, empty glass jars were run at the beginning of each experimental run as a negative control.

After incubation the headspace sampling was carried out for 120 seconds (with a flow rate of 50 standard cubic centimeters per minute), which corresponds to 120 mass spectra

(acquiring 1 spectrum per second). The last 100 seconds were used for analysis. Values for each compound were corrected to the blank headspace values. Moreover, as reported by Taiti et al,

(2019) to avoid different experimental conditions, all the samples were analyzed in an air- conditioned room, with a constant temperature of 25°C ± 1°C. For all sample analysis the PTR parameters were set as follows: a mass spectrum comprised between m/z 1 and m/z 250, pressure

2.3 mbar, drift voltage 600V, temperature of 100°C, extraction voltage at the end of the pipe

(Udx) 35 V and corresponding to an E/N value of 134 Td (Td, 1 Td = 10−17 cm2/V s). As reported previously by Pang (2015), the E/N value that is used gives a good balance between excessive water cluster formation and product ion fragmentation.

2.3.4 HCN measurement

HCN production was measured for each Pseudomonas isolate using a protocol modified from Carterson et al (2004). Bacteria (40µl, OD600 0.45-0.55) were spread onto plastic 35mm

59 plates containing approximately 4ml LB agar. Each plate was placed on top of a second 35mm plate containing 1ml 4M NaOH and sealed with at least three layers of parafilm. Once sealed, the bacteria were incubated at 28-30°C for approximately 24 hours. During this period, the 4M

NaOH absorbed HCN produced by the bacteria. After the incubation period the 4M NaOH was diluted to 0.09M and HCN was quantified using a 96-well plate spectrophotometer. A 1:1 o- dinitrobenzene in 2-methoxyethanol:p-nitrobenzaldehyde in 2-methoxyethanol solution was used to quantify bacterial cyanide. Seventy microliters of the 1:1 solution was added to 21μl of each sample. After a 30-minute incubation at room temperature the OD600 was measured. Samples were quantified relative to a potassium cyanide standard curve (1-20μM in 0.09M NaOH).

Additional dilutions were made with 0.09M NaOH if needed. Every strain was quantified in at least triplicate.

2.3.5 F. oxysporum inhibition using HCN

The inhibitory activity of HCN was tested against F. oxysporum 289. The experimental setup was similar to the Pseudomonas-Fusarium volatile assay. A stock solution KCN was prepared by dissolving 0.30g in 10ml 0.09M NaOH. The KCN was further diluted in 0.09M

NaOH and 823µl KCN was combined with an equivalent volume of 0.2N HCl to achieve final concentrations of 6.25, 12.5, 25, 50, 100, and 200 KCN parts per million (ppm) per plate. The plates were sealed with at least three layers of parafilm and gently rocked to combine the NaOH and HCl solutions to release HCN gas. The KCN quantities correspond to final concentrations of

2.59, 5.19, 10.37, 20.75, 41.49, 82.99 HCN ppm per plate if all cyanide in the solution was converted to HCN. The area of fungal growth was assessed after one week. Three experimental

60 units were used per treatment in each experiment. The cyanide fungal inhibition assay was performed twice.

2.3.6 Data analysis and statistics

The spectra calibration of “time of flight” was performed off-line after dead time

+ + correction and was based on three points (m/z = 29.997 (NO ), m/z = 59.049 (C3H7O ) and m/z

+ = 137.132 (C10H17 )). Data were recorded with the software “TOF-DAQ” (Tofwerk AG,

Switzerland), and were analyzed using a “PTR-MS viewer”.

The raw data was converted on the basis of primary ion signal from cps to ppbv. Volatile compounds with <0.25ppbv and other interfering ions, were filtered following the procedure used by Taiti et al (2017). In this manner, were detected a total of 55 compounds using a threshold of 0.25ppbv; however, for downstream analysis we removed all compounds that were below 1ppbv in every replicate across all treatments (39 remaining compounds) (Supplemental

Table A1). Compounds that were not present at quantities >1ppbv in every replicate of at least one bacterium or LB control were not included in any analysis. After removing volatile compounds <1ppbv, one-way ANOVA (α=0.05) was performed for the remaining compounds to identify compounds that were significantly different between the bacteria and LB control. Thirty- three compounds were significantly different between the treatments. Compounds that were not different between the 20 bacteria and LB control were further removed from the data set.

A heat map showing the abundances of individual compounds was prepared on log(n+1) transformed data in Microsoft Excel. The average values for each bacterium and LB control are used in the heat map. Variable reduction principal component analysis (PCA) was performed on the volatile profiles of the bacteria and LB controls. In this method, only compounds that

61 accounted for the most variation in the data set were used in the final PCA (Supplemental Figure

S2.2). Before PCA, the dataset was preprocessed using log(n+1) transformation followed by mean centering. Data preprocessing using transformation and scaling is commonly used in metabolite studies (van den Berg, 2006). All bacteria treatments and controls are used in the

PCA. PCA was performing using JMP from SAS.

VOCs were assigned a tentative identification utilizing data available from previous

PTR-MS, PTR-ToF-MS, and additional methods of mass spectrometry analysis studies. Where available we tentatively identified compounds based on previously reported fragmentation patterns (Buhr et al, 2002; Gueneron et al, 2015; Maleknia et al, 2007; Mochalski et al, 2014;

Perraud et al, 2016)

Fungal mycelial growth in in vitro assays was measured using ImageJ

(https://imagej.nih.gov/ij/). Data were tested for normality and homogeneity of variances using the Shapiro-Wilk and Levene’s test. A majority of the treatments were normally distributed; however, the variances were not equal across treatments. The in vitro fungal data were subject to analysis with the parametric Welch’s ANOVA (confidence interval 95%, α= 0.05) with post-hoc

Games-Howell test. The in vitro C. elegans data were subject to analysis with the nonparametric

Kruskal-Wallis test followed by a post-hoc Dunn’s multiple comparisons test (α=0.05).

Correlations between the in vitro volatile assays and individual volatile compounds were conducted using Pearson’s correlation coefficient analysis. Average % inhibition of each F. oxysporum isolate and average C. elegans ratings were used in the correlation analysis. All

ANOVA, correlation coefficient calculations, and nonparametric statistics presented in this study were performed using Minitab (Minitab LLC, Pennsylvania, USA) or SPSS (IBM, New York,

USA).

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2.4 Results

2.4.1 In vitro bioassays

Every strain of bacteria tested inhibited the growth of Fusarium oxysporum 289 in vitro.

In the top agar inhibition assay, all bacteria significantly inhibited F. oxysporum 289 by over

65% (Figure 2.1). The nine most effective strains were those which caused over 95% reduction of growth of Fusarium in the top agar as compared to the LB control. These strains had limited to no growth past the fungal plug. The nine bacteria were spread across four Pseudomonas species (P. protegens, P. brassicacearum, P. chlororaphis, and P. poae). Further insight into mode of action was obtained from the dual plating and indirect volatile exposure assays.

In the dual plating assay only two strains (P. fluorescens 24D3 and 89F1) did not significantly inhibit growth of F. oxysporum 289 as compared to the control (Figure 2.2). The magnitude of inhibition varied between bacteria. Some strains caused fungal growth to stop upon making contact with the bacteria, however this still resulted in significant growth inhibition as compared to the controls (Supplemental Figure S2.1). Nine strains inhibited F. oxysporum 289 by over 50% compared to the LB control. There was complete overlap of the nine top strains in both the dual plating and top agar assays.

The species best at inhibiting growth of F. oxysporum in our volatile bioassays were P. fluorescens and P. protegens (Figures 2.3 and 2.4). Not every bacterium produced volatiles capable of significantly inhibiting the growth of F. oxysporum 289 (Figure 2.3A). Five of the 20 strains tested did not significantly inhibit growth of the fungus. The effects of volatiles varied among the remaining 15 bacteria. The volatiles produced by five strains (P. protegens and P. fluorescens), inhibited growth of the fungus by over 50% as compared to the control. Of the top five strains with volatile activity only one, P. fluorescens 36F3, was not a top treatment in the top

63 agar and dual plating assays. We also performed the indirect exposure inhibition assays on two other microorganisms, F. oxysporum 197 and the bacterial-feeding nematode C. elegans. Seven bacteria strains in the P. fluorescens and P. protegens species significantly suppressed the growth of F. oxysporum 197, however fungal suppression was less with this isolate than with F. oxysporum 289 (Figure 2.3B).

Due to the short reproductive cycle of the nematode, the number of C. elegans at the end of a 7-day period was recorded on a scale of 0 to 4, where zero represents no living nematodes, and four represents over 200 C. elegans adults and juveniles. In the final nematode counts only living nematodes were counted. A rating of four indicates that the nematodes were able to grow and reproduce over the duration of the experiment. With one exception, plates with a rating of zero contained only dead juvenile nematodes. The LB and E. coli OP50 negative controls had average ratings of 4 and 3.7, respectively. Volatiles of multiple strains inhibited the nematodes.

Seventeen of the strains significantly inhibited C. elegans compared to the LB and E. coli OP50 negative controls (Figure 2.5). Six bacteria (P. chlororaphis, P. fluorescens, and P. protegens) produced volatiles that resulted in complete nematode lethality. An additional seven strains (P. brassicacearum, P. chlororaphis, P. fluorescens, P. frederiksbergensis, P. poae, P. protegens) had average ratings of 0

64

2.4.2 PTR-ToF-MS and HCN quantification

In the 20 Pseudomonas spp. and Pantoea agglomerans strains and LB controls, 39 compounds were quantified at abundances >1ppbv using PTR-ToF-MS, ranging in m/z from

27.023 to 153.120. Of these, 33 were significantly different (α= 0.05) between the bacteria and controls. In general, the lower molecular weight compounds were more abundant than the higher ones. Compounds were putatively identified based on their protonated masses, from which chemical formulas could be determined. All compounds present in every replicate of at least one bacterium or the LB control above 1pppv are included in Table A1.1. Through the remainder of this text, m/z will be referred to as their theoretical (calculated mass), rather than the experimentally measured mass unless we were unable to assign a chemical formula to a compound. Categories of compounds putatively identified included hydrocarbons (alkyl fragments), alcohols, ketones, organosulfurs and cyanides. Differences in the abundance of each compound >1ppbv is shown in a heat map in Figure 2.6. Bacteria are separated by species designation in the heat map to best allow for pattern differentiation. Within the heat map, cells that are red are most abundant and cells that are black are not present in the samples. All strains and the LB controls had complex VOC profiles. There were multiple compounds quantified in which average values in the LB were higher than all the average values of every bacteria strains

(m/z 27.023, 30.046, 45.033, 47.049, 77.042, 79.054, and 97.028). As indicated in the heat map,

+ m/z 28.018 (H2CN ) was the most abundant compound in some of the bacteria but was not present in others. HCN production varied based on species. Additional differences occur in the heat map for individual bacterial strains and compounds; however, no clear patterns are viewed except for Pantoea agglomerans MBSA-3BB1 standing out from the Pseudomonas spp. strains.

Bacteria growth varied from day to day, which may account for differences within treatments.

65

Some bacteria had replicates where the lawn did not cover the entire plate which may have contributed to differences in overall volatile quantification.

Many strains produced substantial amounts of two classes of compounds: cyanides and organosulfurs. Figure 2.7 shows the abundance of HCN and organosulfur compounds as compared to the remaining compounds. Abundance of compounds varies among the strains.

Figure 2.8 shows hydrogen cyanide (HCN) production by each strain. Hydrogen cyanide quantification is shown using both a colorimetric assay and the PTR-ToF-MS quantification

+ (H2CN , m/z 28.018) to compare the results of each assay. Cyanide production varied between the strains. Of the 16 strains that emitted measurable hydrogen cyanide, average levels ranged from 25 to 1569 ppbv. No strains in the P. poae or P. rhodesiae species produced measurable amounts of cyanide. The LB control did not produce measurable cyanide in either assay. While the amount of cyanide produced was not comparable between the PTR-ToF-MS and colorimetric assay results, the same trend in HCN production among the strains was seen in both assays except for Pantoea agglomerans MBSA-3BB1. With this strain, a small amount of hydrogen cyanide was measured with PTR-ToF-MS and none with the spectrophotometer. Due to variation in the cyanide standard curve between experimental runs, the colorimetric assay is considered semiquantitative rather than quantitative.

Figure 2.9 and Supplemental Table S2.1 shows sulfur containing compounds produced by each strain and the LB control. In general, the most abundant organosulfur compound

+ produced by the bacteria was m/z 49.011 (CH5S , methanethiol/ DMDS fragment). Within this study, we were interested in volatiles with biocontrol potential, and consequently one organosulfur compound we were most interested in was DMDS and associated fragments.

Synthetically produced DMDS is sold commercially as a soil fumigant to control soilborne plant

66 pathogens, nematodes, and weeds of a variety of crops (Arkema, 2016). Seven of the 21 bacterial

+ strain produced DMDS (C2H7S2 , m/z 94.998) average levels at over 1ppbv. The top two DMDS producing strains were P. protegens strains 1B1 and Darke (average 12.1 and 8.6 ppbv,

+ respectively). All bacteria and the controls produced levels of CH3S2 (DMDS-fragment, m/z

+ 78.967) at levels greater than 1ppbv. 1B1 and Darke were also the top CH3S2 producers

(average 124.9 and 96.7, respectively). For both m/z 94.998 and 78.967, 1B1 and Darke produced approximately 1-2 log fold more than the other bacteria. An additional compound of

+ interest was methyl thiocyanate (C2H4NS , m/z 74.006), which was produced at levels >1ppbv by

19 strains. Methyl thiocyanate was the most abundant organosulfur compound produced by P. protegens strains 15G2 and 38G2. The highest producer of methyl thiocyanate was P. protegens

+ 1B1 (158.0 ppbv). Finally, nine strains produced S-methyl thioacetate (C3H7OS , m/z 91.021) at quantities >1 ppbv. The highest S-methyl thioacetate producer was P. fluorescens 24D3

+ (6.9ppbv). One organosulfur compound, m/z 77.042 (C3H9S ), was only present >1ppbv in the

LB control, which may indicate it could have been used as a nutrient source by the bacteria to generate other organosulfur compounds.

Volatile compounds >1ppbv were log transformed and mean centered and analyzed using principal component analysis, shown in Figure 2.10. The data set was reduced a set of eight compounds responsible for 75.5% the variation within the bacteria and LB controls. The bacteria did not separate into discrete groups on the PCA, rather separated along a gradient. Supplemental

Figure S2.2 demonstrates the importance of reductive PCA to reduce the complexity of correlations between variables. The eight variables used in the PCA are cyanide or sulfur containing compounds or compound fragments (m/z 28.018, 46.995, 49.011, 63.026, 74.006,

78.967, 91.021, 94.998). All variables except m/z 63.026 highly influenced PC1. All cyanide and

67 organosulfur compounds >1ppbv were included in the PCA except for m/z 77.042, which was not selected for the reductive PCA. When the bacteria are colored by species, rather than isolate designation, separation into groups is seen for some species but others are more spread across the

PCA, indicating differences in VOC production among strains within the same species

(Supplemental Figure S2.2).

2.4.3 Correlation between in vitro assays and volatile compounds

We were interested in correlations between the volatiles produced by the bacteria and microorganism inhibitory activity. The inhibitory activity of the bacteria and controls was placed on the PCA using eight cyanide and sulfur containing compounds and fragments, coloring individual samples according to fungal inhibition (Figure 2.10 B, C). Fungal inhibition by the strains is observed along the gradient. Pearson’s correlation coefficient was determined for 33 volatile compounds (>1ppbv and significance with ANOVA, α=0.05) against inhibition of both

F. oxysporum 289 and 197. Four VOCs were positively correlated with inhibition of both fungal isolates, and two additional compounds were positively correlated with F. oxysporum 197 inhibition only (Table 2.2). Five of the compounds correlated with inhibition are organosulfur and/or cyanide containing compounds and fragments. We tested the activity of pure HCN against

F. oxysporum 289. At HCN concentrations of 20.75ppm or greater (50ppm KCN or greater) growth of the fungus was inhibited (Table 2.3). In these assays we only measured the area of thick hyphal growth, because there was no growth in the inhibitory concentrations. The only

+ VOC significantly correlated with inhibition of C. elegans was H2CN (Pearson’s Correlation

Coefficient -0.692, p-value 0.001). Additional compounds were significantly associated with higher amounts of nematodes (data not shown).

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2.5 Discussion

Within the rhizosphere, a biocontrol agent may not be in direct contact with the soilborne pathogen it is controlling, and as such multiple modes of action could be contributing to bioactivity. Our study focused on multiple modes of action to explore control activity of fungal

(F. oxysporum) and nematode (C. elegans) systems by beneficial bacteria. The bioactivity mechanisms tested in the top agar assay were direct contact, secreted antibiotic and volatile compounds; dual plating assay were secreted antibiotic and volatile compounds; and shared-air inhibition assay only investigated activity though volatile compounds produced by the bacteria.

The best candidates in the top agar and dual plating inhibition assays of F. oxysporum 289 belonged to the P. protegens, P. brassicacearum, P. chlororaphis, and P. poae species (Figures

2.1 and 2.2). Except for P. poae 29G9, genome mining indicated the presence of three antibiotic gene clusters (Table 2.1: DAPG, pyrrolnitrin, and phenazine) that could play a role in fungal antagonism in the top strains. These gene clusters were only present in the most bioactive bacteria, although not every bioactive strain contained all three antibiotic gene clusters. DAPG, pyrrolnitrin, and phenazines are diffusible secondary metabolites, meaning the compounds can be secreted by the bacteria and move through the growth media (in vitro) or soil to affect the pathogen (Haas & Defago, 2005). Just as the presence of antibiotics genes is inconsistent within our collection, some well-characterized Pseudomonas strains capable of biocontrol have varied potential to produce these antibiotic compounds (Loper et al, 2012). Every P. protegens strain as well as the most active P. brassicacearum strains contain the DAPG gene cluster. DAPG is a secondary metabolite produced by Pseudomonas that can play a role in antibiosis of multiple classes of pathogens including fungi, oomycetes, and bacteria (Keel et al, 1992; Levy et al, 1992;

Rezzonico et al 2007). Soils suppressive to take all disease of wheat (causal agent

69

Gaeumannomyces graminis var. tritici) contain higher levels of pseudomonads with the DAPG gene phlD in the rhizosphere and/or root tissue (de Souza et al, 2002; Raaijmakers & Weller,

1998). Some of our bioactive P. chlororaphis and P. protegens strains also contain genes for pyrrolnitrin, an antibiotic that can be produced by Pseudomonas sp. and Pantoea agglomerans which has demonstrated activity against multiple microorganisms (Arima et al, 1964; Chernin et al, 1996; Howell & Stipanovic, 1979; Tripathi & Gottlieb, 1969). P. fluorescens Pf-5 mutants unable to produce pyrrolnitrin were less effective against fungal pathogens in vitro and in planta than the wildtype isolate (Rodriguez & Pfender, 1997). The two most bioactive P. chlororaphis strains contain the gene cluster for phenazine production. Phenazines purified from Burkholderia cepacia have shown activity against Rhizoctonia solani in vitro (Cartwright et al, 1995).

Phenazine mutant- Pseudomonas isolates were not as effective in controlling disease caused by

Fusarium oxysporum f. sp. radicis-lycopersici in planta as compared to the wildtype isolate

(Chin-A-Woeng et al, 1998). Additionally, two of our P. protegens strains also contain the gene cluster for pyoluteorin, an antibiotic compound with demonstrated oomycete (fungal-like microorganism) control activity (Howell & Stipanovic, 1980). Because it does not contain the gene clusters for any of the abovementioned antibiotics it is not clear to us what is contributing to the biocontrol activity of P. poae 29G9, and further exploration may be warranted.

The best bacteria in the shared-air indirect exposure assays of F. oxysporum isolates 289 and 197 belonged to the P. fluorescens and P. protegens species. The VOCs produced by the top

Pseudomonas strains inhibited mycelial growth by over 50% in F. oxysporum 289 and over 30% in F. oxysporum 197 as compared to the control. This indicates that the control capabilities of bacteria might differ against microorganisms of the same species, which has implications for identifying biocontrol agents with a broader spectrum of control activity. When strains were

70 pooled together and inhibition activity was determined at the species level, P. fluorescens and P. protegens were significantly better at inhibiting Fusarium mycelial growth than the other species. Strains from P. chlororaphis, P. frederiksbergensis, and P. brassicacearum also inhibited F. oxysporum 289 mycelial growth (Figures 2.3 and 2.4). It is also important to note that P. protegens and P. fluorescens both had four strains used for testing while the other species had fewer strains. It is possible that greater inhibition at the species level might have been seen if the other species had more strains used in the assays. Our results contrasted with the results of

Hunziker et al (2015), who screened a collection of bacteria representing species including P. fluorescens, P. protegens, and P. frederiksbergensis against F. oxysporum in shared-air experiments. Although the volatiles produced by some of their bacteria caused significant reduction, Hunziker et al (2015) saw substantially less inhibition of F. oxysporum mycelia

(<12%) than our top candidates (>50% reduction as compared to the control). While our results indicated patterns of inhibition among the species, the differences between our results and

Hunziker et al (2015) indicate the necessity to test more strains within the species presented here in this study, with additional isolates of F. oxysporum representative of multiple formae, to gain a more comprehensive picture of fungal volatile inhibitory activity at the species level.

Every strain that significantly inhibited growth of F. oxysporum 289 contains the hcnABC gene cluster (Figure 2.3A, Table 2.1). Through a colorimetric semi-quantitative assay, we determined that all these strains produced a measurable amount of hydrogen cyanide (Figure

2.8B), a volatile compound produced by many pseudomonads capable of biocontrol of fungi and nematodes. Pseudomonas mutants with reduced (either substantially or completely) HCN production were less effective in pathogen control in vitro or in planta (Ahl et al, 1986;

Flaishman et al, 1996; Gallagher & Manoil, 2001; Hunziker et al, 2015; Laville et al, 1998;

71

Ossowicki et al, 2017). Additionally, pure HCN and NaCN were effective against C. elegans and multiple fungal pathogens (Ahl et al, 1986; Flaishman et al, 1996; Gallagher & Manoil, 2001).

HCN was fully inhibitory to F. oxysporum 289 in vitro at concentrations 20.75ppm and greater

(Table 2.3). The level of fungal inhibition due to bacterial volatiles varied between F. oxysporum

289 and 197. Unlike for F. oxysporum 289, not every cyanide producer was capable of significantly inhibiting F. oxysporum 197. Some strains with relatively high cyanide production were not did not significantly inhibit growth of F. oxysporum 197 (Figures 2.3B, 2.8). Likewise, not every cyanide producer significantly inhibited the growth and reproduction of C. elegans

(Figures 2.5 and 2.8). Due to the differences in biocontrol capabilities among the different bacteria we were interested in seeing if any additional volatile compounds may play a role in biocontrol of nematodes and fungi. Differences in the bacteria volatilomes were determined using PTR-ToF-MS.

As seen in Figure 2.6, the volatile profile of the control and bacteria is complex, and there is large variation in the abundance of individual compounds. Cyanide production using PTR-

ToF-MS resulted in a similar pattern of production among the bacteria as the colorimetric assay

(Figure 2.8). The PTR-ToF-MS and colorimetric assay results were compared against previous qualitative and quantitative cyanide quantification done in the Taylor Laboratory in which some, but not all, of the strains matched with results presented in this study (Aly, 2009). Ultimately the previous quantification methods were different, based on color change of filter paper (qualitative, rating scale of zero to three) or micro-ion probe (quantitative). Results of those two methods did not always match in relative magnitude, and it is possible sensitivity of the quantification methods may play a role in the differing results. The similarity in measurement of hydrogen cyanide between the colorimetric assay and PTR-ToF-MS boosts our confidence in using the

72

PTR-ToF-MS to verify volatile production in our bacteria. Between these four cyanide quantifications tested in current and previous experiments, it is clear the method of volatile quantification is imperative for the most correct and informative data.

Of the 39 compounds quantified at intensities <1 ppbv, we identified eight, all cyanides and sulfur-containing compounds, that contributed to 75.5% of the variation between the bacteria and controls (Figure 2.10). There was variation in both total quantity and abundance (% total

VOC) of these compounds between the bacteria and LB controls (Figure 2.7). Strains ranged from having cyanides and organosulfur compounds comprise 3.1% (Pantoea agglomerans) to over 70% (P. fluorescens and P. protegens) of the total VOCs produced. When the PCA was colored based on fungal inhibition activity of each strain, we saw that the bacteria and controls separated along a gradient. Strains that caused limited to no inhibition of fungal growth were

+ generally in the upper left quadrant of the PCA, opposite the vectors for m/z 28.018 (H2CN ,

+ + hydrogen cyanide), 74.006 (C2H4NS . methyl thiocyanate), and 91.021 (C3H7OS , S-methyl thioacetate) (Figure 2.10 B, C). Correlation analysis indicated that these three compounds, in

+ + addition to m/z 46.995 (CH3S , methanethiol/DMS fragment), 49.011 (CH5S , methanethiol/DMDS fragment), and 51.010 (unknown fragment) may contribute to fungal inhibition (Table 2.2). Because HCN has already been discussed, we will explore the possible involvement of these additional volatiles in fungal inhibition.

Methyl thiocyanate (m/z 74.006), produced by 11 of our bacteria (P. brassicacearum, P. chlororaphis, P. fluorescens, and P. protegens) at >10ppbv, is an organosulfur cyanide compound that has been quantified in multiple Pseudomonas genera (Bean et al, 2012;

Ossowicki et al, 2017). It is lethal and/or paralytic to root-knot nematode in vitro and can act as a repellant to P. aeruginosa (Aissani et al, 2015; Ohga et al, 1993). Within our collection, the

73 strains that produced volatiles significantly inhibitory to F. oxysporum 289 produced higher quantities of methyl thiocyanate than the non-inhibitory strains. Top methyl thiocyanate producing strains also inhibited F. oxysporum 197 mycelial growth in volatile indirect exposure assays (Figures 2.3 and 2.9, Supplemental Table S2.1). Methyl isothiocyanate, isomer to methyl thiocyanate, is a fumigant (non-soil) registered with the EPA that is currently under review for registration as a pesticide, however it is not known to be produced by pseudomonads (Reaves,

2019). S-methyl thioacetate (m/z 91.021), produced by nine of our strains (P. brassicacearum, P. chlororaphis, P. fluorescens, and P. protegens) at >1ppbv has been previously quantified in other pseudomonads and shown to significantly inhibit Rhizoctonia solani hyphal growth in vitro

(Ossowicki et al, 2017). All strains that produced S-methyl thioacetate at average levels >1ppbv significantly inhibited F. oxysporum 289 mycelial growth in indirect exposure assays; however, the second highest producer (P. brassicacearum 93G8) was unable to significantly inhibit growth of F. oxysporum 197. Of the seven bacteria with significant VOC activity against of F. oxysporum 197, only four produced S-methyl thioacetate >1ppbv.

+ Other VOCs including m/z 46.995 (CH3S , methanethiol/DMS fragment) and 49.011

+ (CH5S , methanethiol/DMDS) fragments) were also correlated with F. oxysporum inhibition

(m/z 46.995 both F. oxysporum 289 and 197; m/z 49.011 F. oxysporum 197 only), however there is less evidence that these compounds are involved in microorganism control (Table 2.2).

Methanethiol, widely produced by multiple Pseudomonas species, is the precursor to other organosulfur compounds including DMDS and DMS, and thioesters (Drotar et al, 1987; Lo

Cantore et al, 2015; Thorn et al, 2011; Carrol et al, 2005; Yvon & Rijnen 2001). Lo Cantore et al

(2015) saw that pure methanethiol and DMDS were significantly inhibitory to fungal isolates in vitro, although the inhibition occurred at lower concentration of DMDS than methanethiol.

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Alternatively, the growth of human pathogen Aspergillus in vitro was significantly stimulated by

DMS (on both sulfur-containing and -deficient media) and DMDS (on sulfur-deficient medium)

(Briard et al, 2018). Ultimately production of these compounds was varied among our bacteria.

The top producers of both m/z 46.995 (>30ppbv) and 49.011 (>100ppbv) belong to strains of P. chlororaphis, P. fluorescens, and P. protegens, however multiple strains not inhibitory to either

F. oxysporum 289 or 197 produced relatively high amounts of these compounds (Figures 2.3,

+ + 2.9, Supplemental Table S2.1). The masses representing only DMDS (CH3S2 and C2H7S2 ; m/z

94.998 and 78.967) varied among the bacteria but were not correlated with fungal inhibition. The top DMDS/DMDS fragment producers, P. protegens strains 1B1 and Darke, were inhibitory to both Fusarium isolates, however not all strains that were relatively high producers of these compounds were inhibitory to F. oxysporum (P. poae and P. rhodesiae) (Figures 2.3 and 2.9,

Supplemental Table S2.1). The possible effects that DMDS may have on Fusarium inhibition will be discussed further in Chapter 3.

Dimethyl disulfide may play a role in the inhibitory activity of the four non-cyanogenic strains that significantly inhibited C. elegans (limited growth and reproduction rather than full lethality). P. poae 29G9 and P. rhodesiae 88A6 and 90F12-1 were in the top producers of m/z

94.998 and 78.967 (DMDS and its associated fragment). P. poae 36C8, also inhibitory to C. elegans, produced the greatest amount of DMS (C2H7S+, m/z 63.026), however as mentioned above, DMS is not known as a biocontrol agent (Figures 2.5 and 2.9, Supplemental Table S2.1).

Differences in inhibition between the two Fusarium isolates indicates that volatiles may affect isolates from the same species to different extents. Correlation analysis was performed between bacteria volatiles quantified after 20 minutes of volatile collection by approximately 24 hour-old plates and fungal inhibition after a weeklong assay. It is possible volatile production,

75 both in number of compounds and abundance of individual compounds is not consistent over the full week. Studies involving the volatilome of yeast and fungus over a time-course saw that quantification of individual compounds could vary over the course of the experiment (Azzollini et al, 2018; Khomenko et al, 2017). Therefore, the correlation of volatile production with fungal inhibition might be different if the volatile profiling was done at a different time point. It is also important to consider possible turnover of compounds over the course of the weeklong in vitro assay. Additionally, it is unclear to us what role volatiles produced by the fungi or nematodes may have on the bacteria in the in vitro assays. The volatile profile produced by the bacteria in the presence of other organisms may differ from the bacteria grown alone, as previously demonstrated in individual and co-culturing experiments of bacteria and fungi (Azzollini et al,

2018; Garbeva et al 2014a).

One downfall of using PTR-ToF-MS to identify bacterial volatiles is the difficulty to accurately measure the abundance of certain compounds present in the headspace. Fragmentation of hydrocarbons, alcohols, esters, aldehydes, and ketones results in many m/z associated with multiple compounds (Aprea et al, 2007; Buhr et al, 2002; Gueneron et al, 2015; Maleknia et al.

2007). Within our data set, multiple compounds are associated with groups of fragments, but a precise compound identification cannot be given due to there being multiple possible identities of the fragments. In other instances the mass and chemical formula fit certain compound

+ identities, however they did not fit within the parameters of our system; for example C2H6 (m/z

30.046) is the chemical formula for isotopic ethylene but we identified it is an acetyl fragment because it was produced at highest levels in the controls, which should not be producers of ethylene. Larger compounds including hydrocarbons, ketones, aldehydes were not specifically measured in our data, however some of the mass fragments may have been associated with them

76

(Table A1.1). These categories of compounds are ubiquitously present in the VOC profile of

Pseudomonas and certain ones have demonstrated control activity against phytopathogens. Other studies have determined multiple compounds (ketones and alkenes) including 2-docecanone, 1- undecene, 2-heptanone, and 2-undecanone can inhibit the growth of fungal and oomycete phytopathogens to varying extents in vitro (De Vrieze et al, 2015; Guevara-Avendaño et al,

2019; Hunziker et al, 2015). m/z 51.010 (chemical formula unknown) is correlated with inhibition of F. oxysporum 197; while some of the strains capable of significantly inhibiting F. oxysporum 197 mycelial growth produced measurable amounts of this compound, other high producers did not significantly impact fungal growth. We were not able to tentatively identify this compound, but it is possible it came from a larger, bioactive compound. Due to fragmentation of larger molecules, we may have missed some compounds with bioactive potential in our analysis. As seen in Appendix A1, some fragments were not significantly different between the controls and bacteria, which indicates the volatile was LB derived and likely does not play a role in biocontrol activity. Future studies with PTR-ToF-MS may need to be performed to investigate fragmentation patterns for larger compounds the bacteria may be producing, so we have a more comprehensive idea of what VOCs bacteria from the genera

Pseudomonas and Pantoea produce.

It is likely that more than one mode of action is responsible for the inhibitory activity of a given bacteria. Multiple studies have demonstrated the Pseudomonas mutants lacking the ability to produce a specific antibiotic/volatile compound (or produced the compound in negligible amounts) could inhibit growth of tested organisms in vitro or control disease in plants. Within these studies, control with the mutants was comparatively worse than with the wildtype isolate, which indicates more than one mode of action responsible for pathogen control (Chin-A-Woeng

77 et al, 1998; Hunziker et al, 2015; Keel et al, 2002; Rodriguez & Pfender, 1997). Many of our strains that were active under direct and indirect contact F. oxysporum 289 inhibition assays contain the ability to secrete multiple antibiotic diffusible and volatile compounds. Therefore, organismal control could be achieved through a single- or combination of- modes of action.

2.6 Conclusions and Future Directions

Overall, the most effective bacteria species in inhibiting F. oxysporum and C. elegans were P. fluorescens and P. protegens. The extent of control capabilities varied between individual strains. Within the framework of our analysis, we identified that cyanides and organosulfur compounds could play a role in controlling our target microorganisms. We have identified some future directions to be taken with the project: 1) the mode of action assays should be repeated using un-sealed systems so that the activity of the bacteria can be established when trapped volatiles are not a component of the system; 2) volatile profiling experiments should be repeated over a longer time frame, and with co-culturing of the fungus and nematodes to gain the most accurate representation of how Pseudomonas spp. and Pantoea agglomerans volatiles affect F. oxysporum and C. elegans; 3) volatile profiling should be done with a second method of volatile analysis to complement PTR-ToF-MS, so that all possible volatile organic compounds with biocontrol potential are identified; 4) if possible, mutants with the inability to produce specific compounds should be generated of our most bioactive bacteria to further elucidate the role a specific mode of action has on the overall inhibitory activity of the isolate.

We acknowledge Drs. Cosimo Taiti and Diego Comparini (LINV, Sesto Fiorentino, Tuscany-

Italy) for their assistance in performing and analyzing the data from the PTR-ToF-MS

78 experiments, Edwin Daniel Navarro Monserrat for help with the in vitro assays, and the

Translational Plant Sciences Graduate Program for funding the PTR-ToF-MS experiments

79

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Figure 2.1. Top agar growth inhibition of F. oxysporum 289 by Pseudomonas spp. and Pantoea agglomerans strains. Inhibition of the fungus by a bacterium was assessed after a week of direct exposure. Values are presented as a proportion of growth as compared to the LB control. Each bacterium was tested in two independent assays, and the results of all assays were combined. n= 8 for each bacterium and 20 for the LB control. Data shown are mean± standard error. Bacteria are organized by species designation: P. br, P. brassicacearum; P. chl, P. chlororaphis; P. f, P. fluorescens; P. fr, P. frederiksbergensis; P. po, P. poae; P. pr, P. protegens; P. rho, P. rhodesiae; Pa. ag, Pantoea agglomerans. Due to large differences in standard deviation between the treatments, significant differences were determined using the Welch’s ANOVA for unequal variances followed by a post-hoc Game’s Howell Test (α 0.05). All treatments significantly inhibited growth of the fungus compared to the control (p<0.05).

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Figure 2.2. Dual plating growth inhibition of F. oxysporum 289 by Pseudomonas spp. and Pantoea agglomerans strains. Inhibition of the fungus by a bacterium was assessed after a week of indirect exposure. Values presented are percentage of growth as compared to the LB control. Each bacterium was tested in two independent assays, and the results of all assays were combined. n= 8 for each bacterium and 20 for the LB control. Data shown are mean± standard error. Bacteria are organized by species designation: P. br, P. brassicacearum; P. chl, P. chlororaphis; P. f, P. fluorescens; P. fr, P. frederiksbergensis; P. po, P. poae; P. pr, P. protegens; P. rho, P. rhodesiae; Pa. ag, Pantoea agglomerans. Due to large differences in standard deviation between the treatments, significant differences were determined using the Welch’s ANOVA for unequal variances followed by a post-hoc Game’s Howell Test (α 0.05). Only treatments that are not significantly different from the control are shown and indicated with (A) (p<0.05).

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Figure 2.3. Indirect volatile exposure inhibition of F. oxysporum isolates 289 (A) and 197 (B) with Pseudomonas spp. and Pantoea agglomerans strains. Inhibition of the fungus by a bacterium was assessed after a week of indirect exposure. Fusarium was exposed to the volatiles produced by each bacterium in a closed system. To account for differences between experiments, data presented are percentage of growth compared to the LB control. Growth was recorded as percentage of the petri plate area. Each bacterium was tested in two independent assays, and the results of all assays were combined. n= 7-8 for each bacterium and 16 for the LB control. Data shown are mean± standard error. Bacteria are organized by species designation: P. br, P. brassicacearum; P. chl, P. chlororaphis; P. f, P. fluorescens; P. fr, P. frederiksbergensis; P. po, P. poae; P. pr, P. protegens; P. rho, P. rhodesiae; Pa. ag, Pantoea agglomerans. Due to large differences in standard deviation between the treatments, significant differences were determined using the Welch’s ANOVA for unequal variances followed by a post-hoc Game’s Howell Test (α 0.05). Only treatments that are not significantly different from the control are shown and indicated with (A) (p<0.05).

(Figure 2.3 continued).

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(Figure 2.3 Continued).

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Figure 2.4. Indirect volatile exposure inhibition of F. oxysporum isolates 289 (A) and 197 (B) by Pseudomonas sp. and Pantoea agglomerans. Inhibition of the fungus by a bacterium was assessed after a week of indirect exposure. Fusarium was exposed to the volatiles produced by each bacterium in a closed system. Values presented are percentage of growth as compared to the LB control. Bacteria representing a species were pooled together. Each bacterium was tested in two independent assays. n= 8-32 for each bacteria species and 16 for the LB control. Data shown are mean± standard error. Significance between all treatments was determined using Welch’s ANOVA for unequal variances followed by a post-hoc Games-Howell test. Treatments with the same letter are not significantly different from each other (α=0.05).

(Figure 2.4 Continued).

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(Figure 2.4 Continued).

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Figure 2.5. Volatile activity against C. elegans by Pseudomonas spp. and Pantoea agglomerans. A rating scale of 0-4 was used to determine the nematicidal activity of bacterial volatiles against C. elegans: 0= 0 living C. elegans; 1= 1-20 living; 2= 21-100 living; 3= 101-200 living; and 4= greater than 200 living nematodes after a week-long indirect exposure assay. Bacteria are organized by species designation: P. br, P. brassicacearum; P. chl, P. chlororaphis; P. f, P. fluorescens; P. fr, P. frederiksbergensis; P. po, P. poae; P. pr, P. protegens; P. rho, P. rhodesiae; Pa. ag, Pantoea agglomerans. Each bacterium was tested in 2 separate experiments and combined. n= 9-10 per Pseudomonas and Pantoea strain, n=20 for the control treatments. Mean± standard error is shown. Significance between the treatments and controls was determined using the Kruskal-Wallis test followed by a post-hoc Dunn’s multiple comparisons test (α=0.05). Treatments not significantly different from LB control are marked with (*) and treatments not significantly different from the OP50 control are marked with (^) (p<0.05)

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m/z 27.023 28.018 30.046 31.018 33.033 39.023 41.039 43.018 43.054 45.033 46.995 47.049 49.011 51.011 53.039 55.054 57.033 57.07 59.049 61.028 63.026 65.039 67.054 69.07 71.049 71.086 73.065 74.006 75.044 77.042 78.967 79.054 81.07 83.086 87.08 91.021 94.998 97.028 153.127 LB Control Wood3 P. br 93G8 37D10 14D6 P. chl 48G9 14B11 36F3 24D3 P. f 36G2-1 89F1 P. fr 39A2 29G9 P. po 36C8 15G2 38G2 P. pr 1B1 Darke 88A6 P. rho 90F12-1 Pa. ag MBSA-3BB1

log(n+1) Scale 0 3.5

Figure 2.6. Heat map showing the average intensities (ppbv) of 20 strains of Pseudomonas spp. and Pantoea agglomerans. Compounds at quantities >1 ppbv in every replicate of at least one bacterium or the LB control are included (39 compounds). Bacteria are organized by species designation: P. br, P. brassicacearum; P. chl, P. chlororaphis; P. f, P. fluorescens; P. fr, P. frederiksbergensis; P. po, P. poae; P. pr, P. protegens; P. rho, P. rhodesiae; Pa. ag, Pantoea agglomerans. n=2 or 3 for each bacterium and 6 for the LB control. Average values are displayed. Before averaging treatments, log(n+1) transformation was performed on the data set. This transformation was taken to better visualize differences due to the high range in abundance among compounds.

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Figure 2.7. Cyanide and sulfur-containing compounds produced by the Pseudomonas spp. and Pantoea agglomerans. A) compounds are shown as ppbv, B) compounds are shown as % total volatiles produced by a bacterium or LB control. Compounds at quantities >1 ppbv in every replicate of at least one bacterium or the control (39 total) are included. Bacteria are organized by species designation: P. br, P. brassicacearum; P. chl, P. chlororaphis; P. f, P. fluorescens; P. fr, P. frederiksbergensis; P. po, P. poae; P. pr, P. protegens; P. rho, P. rhodesiae; Pa. ag, Pantoea agglomerans. n=2 or 3 for each bacterium and 6 for the LB control. Shown are the averages± standard deviation.

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Figure 2.8. Hydrogen cyanide quantification by Pseudomonas spp. and Pantoea agglomerans strains + using either A) PTR-ToF-MS (H2CN , m/z 28.018) or B) a colorimetric semi-quantitative assay. Bacteria are organized by species designation: P. br, P. brassicacearum; P. chl, P. chlororaphis; P. f, P. fluorescens; P. fr, P. frederiksbergensis; P. po, P. poae; P. pr, P. protegens; P. rho, P. rhodesiae; Pa. ag, Pantoea agglomerans. Some of the strains as well as the LB controls (not included) do not produce a measurable amount of hydrogen cyanide. B) In the colorimetric assay LB samples were comparable to the blanks. Apart from 37D10 all cyanide producers were quantified in two independent assays and the results combined. Non-cyanide producers and 37D10 were quantified in one assay. n=2 or 3 (PTR-of-MS) and 3 or 6 (colorimetric assay). Shown are the averages ± standard deviation. cc= cubic centimeter.

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Figure 2.9. Signal intensity of organosulfur compounds produced by 20 Pseudomonas spp. and Pantoea agglomerans strains. Compounds included were present at levels >1ppbv in every replicate of at least one bacterium or control. Bacteria are organized by species designation: P. br, P. brassicacearum; P. chl, P. chlororaphis; P. f, P. fluorescens; P. fr, P. frederiksbergensis; P. po, P. poae; P. pr, P. protegens; P. rho, P. rhodesiae; Pa. ag, Pantoea agglomerans. The LB controls produce a measurable about of organosulfur compounds and are also included in the figure. Each point is the average of n=2 or 3 biological replicates for each bacterium and n=6 control replicates. Averages values are shown, and average±standard deviation are included in Supplemental Table S21. Putative chemical + + formula and identity of the masses are m/z 46.995 (CH3S ); m/z 49.011 (CH5S , methanethiol/ DMDS + + + fragment); m/z 63.026 (C2H7S , DMS); m/z 74.006 (C2H4NS , methyl thiocyanate); m/z 77.042 (C3H9S , S- + + containing fragment); m/z 78.967 (CH3S2 , DMDS fragment); m/z 91.025 (C3H7OS , S-methyl thioacetate); + m/z 94.998 (C2H7S2 , DMDS).

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Figure 2.10. Principal component analysis (PCA) biplots of 20 Pseudomonas and Pantoea strains and LB controls. Eight variables (m/z 28.018, 46.995, 49.011, 63.026, 74.006, 78.967, 91.021, 94.998) were used to construct the PCA. The first two Eigenvalues account for 75.5% of the variability within the data set. A) shows each bacterium and control colored differently to identify patterns among the bacteria; B) shows data points colored according to F. oxysporum 289 growth inhibition; C) shows data points colored according to F. oxysporum 197 growth inhibition. Inhibition indicates (100-% growth compared to LB controls). Volatile data were log(n+1) transformed and mean centered before performing the PCA. Each replicate for every treatment is shown as a point. n=2 or 3 for each bacterium or 6 for the LB control.

(Figure 2.10 Continued).

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(Figure 2.10 Continued).

.

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Table 2.1. Pseudomonas strain information. Included is species designation, source of collection, and potential for antimicrobial compound production based on presence of antibiotic gene clusters within the genome.

Antimicrobial Metabolite Strain Species a Source Potentialb Wood3 P. brassicacearum Ohio soil DAPG, HCN 93G8c P. brassicacearum Missouri soil DAPG, HCN 37D10 P. brassicacearum Wyoming soil HCN 14D6 P. chlororaphis Mississippi River HCN 48G9 P. chlororaphis Wisconsin soil HCN, PRN, PHZ 14B11 P. chlororaphis Missouri River HCN, PRN, PHZ 36F3 P. fluorescens Wyoming soil HCN 24D3 P. fluorescens Missouri Botanical Garden HCN herbarium collection 36G2-1 P. fluorescens Wyoming soil HCN 89F1 P. fluorescens Missouri soil HCN 39A2 P. frederiksbergensis Wyoming soil HCN 29G9 P. poae Missouri Botanical Garden herbarium collection 36C8 P. poae Wyoming soil 15G2 P. protegens Missouri River DAPG, HCN 38G2 P. protegens Wyoming soil DAPG, HCN 1B1 P. protegens Mississippi River DAPG, HCN, PRN, PLT DARKE P. protegens Ohio Soil DAPG, HCN, PRN, PLT 88A6 P. rhodesiae Missouri soil 90F12-1 P. rhodesiae Missouri soil MBSA-3BB1 Pantoea agglomerans unknown unknown aSamples from the herbarium collection were collected from the rhizosphere of frozen/dried plant tissue. bDAPG: 2,3-diacetylphloroglucinol; HCN: hydrogen cyanide; PRN: pyrrolnitrin; PHZ: phenazine; PLT: pyoluteorin. cGenome analysis done on clonally identical 93F8.

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Table 2.2. Pearson’s correlation coefficients for the volatile compounds most positively correlated with fungal inhibition. The peak intensities (ppbv) were averaged and correlated with the average F. oxysporum 289 and 197 indirect exposure inhibition of each bacterium and the LB control. Average inhibition values were determined relative to the LB control. N.S indicates a compound was not significant for inhibition of the fungal isolates. aProtonated chemical formula was determined based on m/z

F. oxysporum 289 F. oxysporum 197 Protonated Chemical Pearson’s Pearson’s m/z a Tentative Identification p- p- Formula Correlation Correlation value value Coefficient Coefficient + 28.018 H2CN Hydrogen Cyanide 0.872 0.000 0.869 0.000 Methanethiol/DMS + 46.995 CH3S Fragment 0.533 0.013 0.679 0.001 Methanethiol/DMDS + 49.011 CH5S Fragment N.S. N.S. 0.551 0.010 51.010 Unknown Unknown Compound N.S. N.S. 0.545 0.011 + 74.006 C2H4NS Methyl thiocyanate 0.582 0.006 0.717 0.000 + 91.021 C3H7OS S-methyl thioacetate 0.475 0.030 0.533 0.013

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Table 2.3. Inhibition of F. oxysporum 289 by HCN. The lethal dose of HCN to Fusarium was determined though indirect exposure assays. The concentrations in the table assume that the KCN was fully converted to HCN. Each treatment was tested in 2 independent assays and the results combined. n=6 for each treatment. NG indicates no growth and the only area determined was the area of the fungal plug.

0.09M Treatment Blank 2.59 ppm 5.19 ppm 10.37 ppm 20.75 ppm 41.49 ppm 82.99 ppm NaOH Average % Plate Area 67.83 65.24 54.44 47.55 7.04 NG NG NG Standard Deviation % 3.57 2.08 4.47 4.65 10.53 ------Plate Area

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Supplemental Figure S2.1. In vitro inhibition assay setup. The top left image of a plate shows thicker inner growth (indicated with red dotted line) and total growth (indicated with black dotted line). The total hyphal growth area was used in measurements.

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A) PCA with 55 compounds measured with PTR-ToF-MS. The first two Principal Components account for 42.4% of the variation in the data set when all compounds measured with PTR-ToF-MS are used.

Supplemental Figure S2.2. Variable reductive principal component analysis (PCA) of the volatile profiles produced by Pseudomonas spp. and Pantoea agglomerans strains. PTR-ToF-MS peak intensity data (ppbv) were preprocessed using a log(n+1) transformation followed by mean centering of the data. Multiple iterations of the PCA were performed, using multiple selection methods to select variables to use in the analysis. In this way, we were able to select variables accounting for the most variance in the data. Variable reduction was selected using multiple factors including peak abundance (ppbv), significance of the compound (ANOVA, α=0.05), variable weights within the PCA loading matrix, and targeted compounds of interest. A-F display the PCA score plots of the 21 bacteria and control treatments under multiple variable reductive selection guidelines and visualization methods. The specific selection parameters for each plot can be found above each plot.

(Supplemental Figure S2.2 Continued).

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(Supplemental Figure S2.2 Continued).

B) PCA with 39 compounds. The initial list of 55 compounds were filtered so that only compounds with at least one treatment with every replicate >1ppbv remained. The first two Principal Components account for 50.1% of the variation in the data set when only compounds >1ppbv are used.

C) PCA with 33 compounds. The 39 compounds >1ppbv were filtered so that only compounds that were significantly different among the treatments remained (ANOVA, α=0.05). The first two Principal Components account for 52.7% of the variation in the data set when only these compounds were used.

(Supplemental Figure S2.2 Continued).

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(Supplemental Figure S2.2 Continued).

D) PCA with 10 compounds. The Pseudomonas strains in (C) were predominantly clustered on the negative axis of PC1. The 10 compounds in PCA (C) with negative loading values (m/z 28.018, 46.995, 49.011, 51.010, 59.049, 63.026, 74.006, 78.967, 91.021, 94.998) were used to construct a PCA. These compounds primarily consisted of our compounds of interest: cyanides and organosulfurs, two categories of compounds with known biocontrol potential. The first two Principal Components account for 70.5% of variation in the data when only these compounds were used.

(Supplemental Figure S2.2 Continued).

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(Supplemental Figure S2.2 Continued).

E) PCA with 8 compounds. Eight of the 10 compounds in PCA D were tentatively identified as organosulfur and cyanide containing compounds/fragments, known categories of volatiles produced by Pseudomonas (m/z 28.018, 46.995, 49.011, 63.026, 74.006, 78.995, 91.018, 94.998). Due to known biocontrol activity of certain organosulfur compounds and hydrogen cyanide, these 8 compounds were used to construct a PCA. The first two Principal Components account for 75.5% of variation when only these compounds were used.

F) PCA with 8 compounds. PCA F is the same as PCA E, except that bacteria are labelled with species designation.

Control (LB) P. brassicacearum P. chlororaphis P. fluorescens P. frederiksbergensis P. poae P. protegens P. rhodesiae Pantoea agglomerans

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Supplemental Table S2.1. Organosulfur compounds produced by Pseudomonas spp. and Pantoea agglomerans strains. 8 compounds were measured in at least one treatment at average values >1ppbv and are included here. A) is the average of n=2 or 3 for bacteria and n=6 for controls. B) is the standard deviation for each compound. P. br, P. brassicacearum; P. chl, P. chlororaphis; P. f, P. fluorescens; P. fr, P. frederiksbergensis; P. po, P. poae; P. pr, P. protegens; P. rho, P. rhodesiae; Pa. ag, Pantoea agglomerans.

A Average (ppbv) 46.995 49.011 63.026 74.006 77.042 78.967 91.021 94.998 Treatment + + + + + + + + [CH3S ] [CH5S ] [C2H7S ] [C2H4NS ] [C3H9S ] [CH3S2 ] [C3H7OS ] [C2H7S2 ] LB Control 0.39 0.64 0.00 0.29 6.02 4.25 0.00 0.15 WOOD3 5.83 17.78 0.09 9.65 0.38 2.28 1.95 0.20 P. br 93G8 3.30 15.62 0.23 4.44 0.26 3.75 4.19 0.45 37D10 12.03 73.24 0.00 11.43 0.27 9.92 1.49 1.11 14D6 33.37 240.43 0.15 14.22 0.55 6.75 1.47 0.59 P. chl 48G9 9.70 27.79 0.32 22.59 0.39 3.61 0.59 0.39 14B11 19.87 74.45 0.24 32.22 0.60 3.99 1.93 0.45 36F3 45.06 151.65 8.68 71.58 0.64 9.79 2.87 0.91 24D3 62.98 250.18 0.63 68.83 0.61 16.13 6.87 1.21 P. f 36G2-1 8.74 32.15 0.60 18.29 0.57 3.53 0.99 0.40 89F1 3.95 15.36 0.65 7.53 0.12 2.51 0.00 0.27 P. fr 39A2 3.90 17.42 1.92 5.50 0.44 1.54 0.00 0.22 29G9 11.08 42.48 0.00 2.92 0.29 19.37 0.20 1.56 P. po 36C8 22.86 5.37 116.58 0.88 0.27 3.12 0.00 0.61 15G2 17.4 32.43 1.30 34.25 0.38 2.92 0.63 0.24 38G2 22.75 47.25 1.87 47.99 0.57 3.74 0.00 0.43 P. pr 1B1 86.53 175.64 0.37 158.00 0.55 124.91 4.00 12.09 Darke 49.20 151.56 0.29 40.35 0.62 96.72 2.40 8.57 88A6 10.90 32.53 5.30 0.00 0.63 22.51 0.05 1.60 P. rho 90F12-1 12.52 53.52 9.52 2.22 0.74 17.26 0.49 1.50 Pa. ag MBSA-3BB1 6.04 33.43 0.47 2.43 0.31 9.82 0.00 0.98

(Supplemental Table S2.1 Continued).

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(Supplemental Table S2.1 Continued).

B Standard Deviation (ppbv) 46.995 49.011 63.026 74.006 77.042 78.967 91.021 94.998 + + + + + + + + Treatment [CH3S ] [CH5S ] [C2H7S ] [C2H4NS ] [C3H9S ] [CH3S2 ] [C3H7OS ] [C2H7S2 ] LB Control 0.65 0.25 0.00 0.38 1.34 0.80 0.00 0.17 WOOD3 1.3 8.97 0.15 1.21 0.34 1.71 1.14 0.18 P. br 93G8 0.91 4.78 0.21 2.81 0.45 2.00 0.50 0.14 37D10 10.09 73.89 0.00 0.46 0.38 2.75 2.10 0.18 14D6 42.2 323.96 0.22 10.89 0.21 7.67 1.46 0.84 P. chl 48G9 3.95 11.43 0.12 15.98 0.41 2.01 0.31 0.38 14B11 10.67 25.63 0.22 21.21 0.30 2.14 1.35 0.16 36F3 31.87 90.72 7.44 74.93 0.27 7.05 4.01 0.63 24D3 6.07 102.79 0.23 17.93 0.13 4.64 2.58 0.35 P. f 36G2-1 5.62 26.06 0.53 13.03 0.65 2.61 0.68 0.46 89F1 0.66 12.00 0.28 4.08 0.21 1.40 0.00 0.28 P. fr 39A2 0.34 6.04 0.56 2.47 0.07 0.67 0.00 0.20 29G9 7.69 21.23 0.00 3.20 0.28 11.42 0.35 0.65 P. po 36C8 1.15 1.00 0.40 0.55 0.38 0.50 0.00 0.07 15G2 12.90 28.04 0.70 16.76 0.33 2.74 0.18 0.24 38G2 10.06 18.37 0.60 25.95 0.16 2.41 0.00 0.10 P. pr 1B1 34.45 90.19 0.15 135.2 0.17 68.75 2.00 7.56 Darke 10.75 37.53 0.13 20.16 0.06 12.17 0.71 1.31 88A6 3.63 4.61 1.04 0.00 0.16 11.83 0.08 0.56 P. rho 90F12-1 6.77 49.1 7.30 1.46 0.52 12.68 0.33 0.87 Pa. ag MBSA-3BB1 0.72 11.66 0.13 1.34 0.05 3.05 0.00 0.39

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Chapter 3 Identifying the Potential to Prime Pseudomonas spp. for Volatile Organic Compound

Production Though Manipulation of the Culture Medium.

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3.1 Abstract

Pseudomonads can produce multiple volatile organic compounds (VOCs) that are inhibitory to other microorganisms. Under non-nutrient limiting conditions, the bacteria produce substantial amounts of volatiles including cyanides, sulfurs, and hydrocarbons. In this study we sought to investigate the VOC production of bacteria under nutrient limiting conditions, and whether minimal medium could be primed to promote production of specific compounds. This study focused on the VOC production of three Pseudomonas strains: P. chlororaphis 14B11, P. rhodesiae 88A6, and P. protegens Darke. To test this, we performed indirect exposure inhibition assays against Fusarium oxysporum and Caenorhabditis elegans with Pseudomonas produced

VOCs generated on minimal medium, and minimal medium supplemented with substrates for

VOCs (glycine or L-methionine). The VOC profile of the Pseudomonas strains on each growth medium was also quantified using proton transfer reaction time-of-flight mass spectrometry

(PTR-ToF-MS). The addition of L-methionine to a minimal culture medium led to an increase in volatile organosulfur compound production, in some instances increasing specific compounds by multiple log-fold and increased the ability of 88A6 and Darke produced volatiles to suppress F. oxysporum and C. elegans. We also determined addition of L-methionine alone to a soil system was sufficient to produce VOCs inhibitory to F. oxysporum as compared to the controls.

Compared to L-methionine, the effects of glycine addition to the medium were not as pronounced in both volatile production and bioactivity. This study demonstrated the potential to selectively produce specific volatile compounds though addition of amino acids to the system.

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3.2 Introduction

The rhizosphere is a zone full of microbial activity. Bacteria in a plant-root system can colonize the root epidermis and soil on the root (rhizoplane, 1mm from root), and soil surrounding the root (rhizosphere, ~ one centimeter away from root) (York et al, 2016). When compared to bulk soil, microorganism populations in the rhizosphere can differ in microbial quantity, diversity, and organismal activity (predicted or measured enzyme activity) in processes including , carbon, phosphorus, and sulfur transformation and metabolism and antibiotic production (Haichar et al, 2008; Kuzyakov & Blagodatskaya, 2015; Li et al, 2014; Mendes et al,

2014). These differences can be explained in part by exudation of carbon and nitrogen- containing compounds from the roots, which some microbes use as sources of nutrition.

Approximately 5-30% of photosynthates in a plant system enter the rhizosphere as root exudates and a fraction of that is taken up by microbes (Haichar et al, 2008; Haichar et al, 2012; Haller &

Stolp, 1985; Liljeroth et al, 1990; Lynch & Whipps, 1990). Carbon-labelling studies have demonstrated soil bacteria belonging to multiple orders including Enterobacteriales,

Pseudomonales, Rhizobiales, and Bacillales are capable of assimilating root exudates or colonizing plant roots, although results varied depending on the plant species used (Haichar et al,

2008; Haichar et al, 2012). Fungal and nematode pathogens can be inhibited by root exudates from plants capable of producing toxic secondary metabolites (Ling et al, 2013; Medina, 2016).

Specific compounds produced by plant root exudates may allow for certain microorganisms to flourish and others to decline in population.

The makeup and quantity of exudates varies among plant species, and can depend on plant age and physical, nutritional, and biological conditions of the rhizosphere. Many classes of carbon and nitrogen containing compounds comprise these exudates including primary

111 metabolites (e.g. sugars, amino acids, organic acids), and secondary metabolites (e.g. phenolic compounds and phytohormones) (Curl & Truelove 1986; Haller & Stolp, 1985; Kraffczyk et al,

1984; Zhu et al, 2016). Within the rhizosphere organic nitrogen in the form of amino acids is primarily utilized by microorganisms, rather than plants (Kuzyakov & Xu, 2013). It is this microbial utilization of amino acids that is particularly interesting, specifically as it relates to biocontrol of root-colonizing pathogens. The previous chapter (Chapter 2) of this dissertation focused on quantifying and identifying Pseudomonas produced volatiles with biocontrol potential of fungi and nematodes. Volatile compounds can diffuse though pores in the soil and target pathogens via indirect exposure. Pseudomonads can produce multiple secondary volatile metabolites with biocontrol potential that have specific amino acid precursors (for example, methionine (C5H11NO2S) is the precursor to dimethyl disulfide, and glycine (C2H5NO2) is the precursor to hydrogen cyanide) (Gross & Loper, 2009; Yvon & Rijnen, 2001) (Figure 3.1).

While bacteria can synthesize amino acids when given the appropriate nutrient sources the metabolic cost of production can be quite high, and consequently amino acid biosynthesis gene expression decreases when bacteria are grown in nutrient-rich media (Akashi & Gojobori 2002;

Price et al, 2018; Tao et al, 1999). The rhizosphere, particularly regarding amino acid content, constitutes a low nutrient environment for multiple reasons. In the soil organic nitrogen pool there are greater amounts of amino acids bound up in proteins and peptides than in their free form (Yu et al, 2000). Proteins in the soil have to be broken down via proteolysis to be taken up as amino acids by microorganisms (Lipson et al, 2001). For specific compound production amino acids may need to be added to the soil in lieu of microorganisms synthesizing the compounds at a high metabolic cost.

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Amine containing compounds range from being a small proportion of the root exudates

(<2-6.2%, maize) to the most abundant class of compounds released (73.3%, cucumber), however the exact amounts can vary based on a number of factors including plant species, sterility, nutrient composition of the soil (Kraffczyk et al, 1984; Liu et al, 2007; Zhu et al, 2016).

The proportions of methionine and glycine produced by root exudates from plants (pea roots, soybean, and cucumber) grown under sterile conditions ranged from 0.11-0.93% and 0.61-3.08% of total amino acids respectively (Timothy Frey, Rebecca Kimmelfield, & Christopher Taylor, unpublished1; Liu et al, 2007; Sherrod & Domsch, 1970). The aforementioned studies tested plants of varied ages and growth conditions, which could play a role in root exudate composition. Although exact amounts vary by plant species, methionine and glycine make up a low proportion of the total root exudates. In our biocontrol scenario, the beneficial agent must be able to suppress the pathogen under the nutrient conditions of the rhizosphere. Bacteria have varied biocontrol activity under different nutrient regimes. When grown on media mimicking root exudates, Collimonas spp. strains could produce volatiles that inhibited the growth of fungal pathogens, however inhibition was greater under higher-amino acid conditions (Garbeva et al,

2014b). Additionally, volatile inhibition of Phytophthora was higher for Lysobacter strains grown on protein rich agar verses sugar rich agar (Lazazzara et al, 2017).

Therefore, the aims of this study were fourfold: 1) determine the biocontrol potential of bacteria grown on agar-based minimal media ± amino acids against Fusarium oxysporum and

Caenorhabditis elegans; 2) determine the biocontrol potential of a bacterium grown on a soil

1 Timothy Frey, Rebecca Kimmelfield, & Christopher Taylor (unpublished) measured the root exudates in 10-day old Glycine max ‘Lee’ seedlings. RBK helped to design and implement the root exudate experiments. The methodology and results from the experiments is included as Appendix B.

113 matrix against F. oxysporum 3) investigate the volatile profile of three Pseudomonas strains when grown on minimal media, and minimal media supplemented with either methionine or glycine using PTR-ToF-MS; and 4) determine the antagonistic potential of select compounds against F. oxysporum. We hypothesized that the addition of specific amino acids will promote the production of antagonistic volatiles, particularly those compounds for which the amino acids are precursors. Within our scenario, the minimal medium is representative of both rhizosphere and bulk soil. Due to the low amounts of methionine and glycine present in root exudates and high turnover of nutrients by microorganisms, we consider the minimal medium representative of the baseline nutrient levels in the rhizosphere. The minimal medium also mimics the nutrients in bulk soil, which does not have the added nutrients from root exudates.

3.3 Materials and Methods

3.3.1 Microorganism maintenance

Bacteria: Three strains of Pseudomonas from the Dr. Christopher G. Taylor and Dr. Brian

McSpadden Gardener (Ohio State) laboratories were used in the study presented here. P. chlororaphis 14B11 (isolated from Missouri River water), P. rhodesiae 88A6 (isolated from

Missouri Soil), and P. protegens Darke (isolated from rhizosphere of corn in Ohio). The bacteria were maintained on Luria-Bertani (LB) (in one liter: 10g tryptone, 5g yeast extract, 10g NaCl,

15g agar) agar plates at 4°C or stored at -80°C in glycerol. Overnight bacterial cultures were used for the in vitro assays and volatile profiling (Pseudomonas: ~28-30°C, ~200-225 rpm). The of the three bacteria were sequenced previously by the Taylor laboratory (P. chlororaphis 14B11 NCBI: MOAN00000000.1, P. rhodesiae 88A6 NCBI:

NZ_MOBA00000000.1, P. protegens Darke NCBI: NZ_MOAX00000000.1).

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Fungus: Fusarium oxysporum 289 from Dr. Sally Miller (The Ohio State University) was used in this study. The isolate was isolated from diseased tomato roots in a high tunnel in Ohio.

The fungus was maintained on ½ PDA (in one liter: 19.5g Difco™ Potato Dextrose Agar, 7.5g agar). In in vitro assays plugs from a 7-9-day old culture were grown on plastic 100mm ½ PDA or ½ PDA (0.1% lactic acid) plates containing 20±0.5ml of media.

Nematode: The model bacteria-feeding nematode Caenorhabditis elegans strain N2 was used in this study. C. elegans were maintained on Nematode Growth Medium (in one liter: 3g

NaCl, 2.5g peptone, 1ml 1M MgSO4, 1ml 1M CaCl2, 1ml 5mg/ml cholesterol in ethanol, 25ml

Potassium Phosphate Buffer, pH 6, 17g agar). Escherichia coli OP50 was used as a food source for C. elegans (overnight culture ~37°C, ~200-250RPM). 15-25 synchronized L1-stage juveniles on plastic 35mm NGM plates (3±0.3ml) seeded with 30µl E. coli OP50 were used in in vitro assays.

3.3.2 In vitro volatile inhibition assays

Pseudomonas volatiles were exposed to F. oxysporum 289 and C. elegans under nutrient limited conditions in a shared air experiment.

Fusarium-Pseudomonas (agar): Bacteria were grown for 16 to 18hours in 5ml LB, after which an aliquot of overnight culture was centrifuged at 5000rpm for 2 minutes. The supernatant was removed and replaced with sterile ddH2O, and the cells were spun for a second time. After the second centrifuge the supernatant was removed and the cells were resuspended in sterile ddH2O. Resuspended bacteria (100µl) was spread on plastic 100mm M9 minimal medium

(M9MM) agar plates containing 20±0.5ml of media (1L: 200ml 5X M9 Salts [250ml 5X M9

Salts: 8.47g Na2HPO4, 3.75g KH2PO4, 0.625g NaCl, 1.25g NH4Cl], 20ml 20% glucose, 2ml 1M

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MgSO4, 100ul 1M CaCl2, 15g agar, ±amino acids). 250mM L-methionine (1.865g/50mL) or glycine (0.938g/50mL) were added to the minimal medium to achieve a final concentration of

10mM. When the bacteria on the M9MM±amino acid plates dried, the lid was removed and the bottom half of a ½ PDA plate containing a plug of fresh mycelia (size 3 cork borer, 5/6mm inner/outer diameter) was placed on top, so that no direct contact was made between the bacteria and fungus. The system was sealed with at least three layers of parafilm to keep the volatiles in the system. Plates were kept at ambient light and temperature conditions. Fungal mycelial growth was measured after one week. Full mycelial growth, rather than the thickest inner growth, was measured for the assays (see Supplemental Figure 2.1). Similar to the plates from the experiments in Chapter 2, the proportion of “thick” and “thin” mycelial growth varied from plate to plate in the in vitro assays. Each treatment had three or four replicates, and the experiment was performed twice. LB washed with water was the negative control.

C. elegans-Pseudomonas: Experiments were performed similarly to the Fusarium-

Pseudomonas shared air assay with slight variation. The M9MM in the C. elegans assays contained 200µl 1M CaCl2/liter instead of the amount listed above. Bacteria resuspended in sterile ddH2O (30µl) was added to plastic 35mm plates containing M9MM±250mM glycine or L- methionine or LB. Between four and six replicates were used for each treatment and the experiment was performed twice. Negative controls were LB and E. coli OP50. At the end of the weeklong experiment, nematodes were scored on a scale of zero to four (0= no living nematodes;

1= 1-20 living nematodes; 2= 21-100 nematodes; 3=101-200 nematodes; 4=200+ nematodes).

The C. elegans lifecycle is approximately 72 hours, and after one week an uninhibited plate (15-

25 L1-stage juveniles initially added) should have well over 200 nematodes at various lifecycle

116 stages. At the end of the weeklong period plates with >200 nematodes were taken apart to see if the bacterial volatiles were paralyzing or lethal.

Fusarium-Pseudomonas (soil): These experiments were performed to determine the effect of growth matrix on the bioactivity of bacterial volatiles. Experimental conditions were similar to the agar-based inhibition assays, however the bacteria and LB were not washed in ddH2O before inoculation. P. rhodesiae 88A6 was the only bacterium used in the soil assays.

Bacteria was grown for 16 to18 hours in 15ml LB and added to M9MM±250mM L-methionine in dilutions of 1:100 or 1:25. The final methionine concentration of the amino acid-containing solution was 50mM. LB diluted in M9MM±250mM L-methionine were used as the negative control. Twelve milliliters of the bacterial and control suspension were added to 20±0.5g twice autoclaved topsoil in the bottom part of 100mm plastic plates. 100mm ½ PDA (0.1% lactic acid) plates containing a plug of fresh mycelia (size 3 cork borer, 5/6mm inner/outer diameter) in the center were inverted over the plate with the soil and sealed with at least three layers of parafilm

Total mycelial area was determined after a 10-day period.

3.3.3 Pseudomonas volatile organic compound (VOC) quantification

Volatiles by the three Pseudomonas strains grown on M9MM, M9MM+glycine, and

M9MM+L-methionine were quantified using PTR-ToF-MS. Five-hundred millimolar glycine

(4ml) or 250mM L-methionine (8ml) were added to M9MM (160mL dH2O, 40mL M9 5X salts,

4ml 20% glucose, 0.4mL 1M MgSO4, 20ul 1M CaCl2, 3g agar). Ten milliliters (±0.5ml) of the

M9MM±amino acids agar solutions was added to 60mm glass plates. The bacteria were grown, washed, and resuspended similarly to the in vitro inhibition assays. Resuspended bacteria (50µl) was added to each 60mm plate and spread to form a lawn across the plate. Three replicates were

117 done for each bacterial strain and control. The negative control was LB washed with sterile ddH2O. Bacteria and controls were incubated at 28°C for 21-23 hours before analysis with PTR-

ToF-MS. After the overnight growing period, the lawns on the P. protegens Darke plates were less pronounced than the other bacteria; this could have been due to poor growth by the bacteria due to atmospheric conditions or poor/slower growth on the media. VOCs were quantified and analyzed with PTR-ToF-MS according to the methodology described in Chapter 2.

3.3.4 Pseudomonas genome mining for methanethiol and hydrogen cyanide synthesis genes

Methanethiol, precursor to multiple VOCs including dimethyl sulfide (DMS) and dimethyl disulfide (DMDS), can be produced by bacteria from methionine though multiple pathways (Figure 3.1). The genomes of the three bacteria were mined for genes involved in the production of methanethiol and DMS, specifically methionine gamma-lyase (MeGL), cystathionine beta-lyase (CBL), cystathionine gamma-lyase (CGL), branched chain- aminotransferase (AT), aromatic AT, methionine AT, and Methanethiol (MeSH)-Dependent

DMS (MddA) (Carrión et al, 2015; Dias & Weimer, 1998a; Yvon & Rijnen, 2001). The genes for HCN synthesis (hcnABC cluster) were also searched for. The cluster is comprised of three genes coding for HCN synthase (Laville et al, 1998). The bacterial genomes were uploaded to the RAST (Rapid Annotation using Subsystem Technology) server and annotated (Overbeek et al, 2014). The presence of individual genes was determined using the annotated genomes and tblastn (Altschul et al, 1997). Sequences identified in the annotated genomes were confirmed using blastp. Genes that were not identified in the annotated genomes were also searched using tblastn of known protein sequences against the full genome. A tblastn hit was considered positive if there was a ≥65% identity to at least one of the reference sequences. Hit lengths of at least

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80% of the query sequence were considered for the comparison—shorter hits in tblastn were discarded. The protein sequences for HcnABC, MeGL, CBL, CGL, MddA, and MetAT used for tblastn can be found in Supplemental Table S3.1. DMS and DMDS were investigated further in this work for their possible role in biocontrol.

3.3.5 Fusarium inhibition with organosulfur VOCs

F. oxysporum 289 was exposed to DMS and DMDS to determine the inhibitory effect of single compounds. DMS was selected due to its abundance in the VOC profile of P. rhodesiae

88A6 on M9MM+L-methionine, and DMDS was selected because of its commercial use as a soil fumigant (Arkema, 2016). The single compounds were added to autoclaved filter paper on the bottom half of a 100mm plastic plate that was saturated with sterile ddH2O and a 100mm plate containing a plug of F. oxysporum 289 was placed on top. The system was sealed with at least 3 layers of parafilm to trap volatiles in the system. After seven days inhibition potential of the single compounds was assessed by measuring mycelial growth area. After the first replicate of the DMDS experiment the fungal plates were separated from the chemicals, sealed with parafilm, and allowed to grow for another week to identify possible fungicidal, rather than fungistatic, activity. DMS treatments were 0, 1, 10, 100, and 300µl, which corresponds to 0,

6.88, 68.83, 688.26, and 2064.78 ppm, if the compound fully volatilized. DMDS treatments were

0, 1, 5, 10, 50, and 100µl, which corresponds to 0, 8.62, 43.12, 86.23, 431.17, and 862.35 ppm.

The final amount of liquid (ddH2O+chemical compound) on each piece of filter paper was 300µl.

In addition to the 0ppm, blanks (empty bottom dish) were also used as negative controls. Each treatment had three replicates and the experiments were performed twice, except for DMS

2064.78ppm which was tested once. Due to the goal of these experiments—to determine the

119 minimum inhibitory concentration—only the thick “inner” mycelial growth was used for area measurements, rather than the total growth area (Supplemental Figure S2.1).

3.3.6 Data analysis

Fusarium oxysporum 289 inhibition for all experiments was measured using ImageJ < https://imagej.nih.gov/ij/>. The results from the in vitro fungus-bacteria experiments were combined for data analysis. The growth areas, expressed as a percentage of the total plate area, were tested for normality and homogeneity of variance using the Shapiro-Wilk and Levene’s tests, respectively. The combined F. oxysporum volatile assays had homogeneous variance with a majority of treatments with normal distribution, and data were analyzed using ANOVA with a post-hoc Tukey test. The results from the C. elegans in vitro assay were analyzed using the non- parametric Kruskal-Wallis test followed by the post-hoc Dunn’s multiple comparison test.

Data from the PTR-ToF-MS experiment was visualized in two ways: principal component analysis (PCA) and a heat map. All compounds present in at least one treatment with

>1ppbv in every replicate were used for construction of the heat map. The heat map was generated in Microsoft Excel. The data set was further filtered for PCA by removing compounds

>1ppbv that were not significantly different between the bacterial and control treatments

(ANOVA, α=0.05). The remaining data were processed by log(n+1) transformation followed by mean centering before subjecting to PCA. JMP (SAS Institute, North Carolina, USA) was used for PCA. All treatments and controls were included in both the PCA and heat map. Pearson’s correlation coefficients between fungal growth area and nematode rating and individual volatile compounds were calculated to determine which VOCs might influence microorganism

120 inhibition. All ANOVA, non-parametric, and correlation coefficient analyses were performed in

Minitab (Minitab LLC, Pennsylvania, USA) or SPSS (IBM, New York, USA).

3.4 Results

3.4.1 In vitro VOC inhibition assays

The composition of the growth medium affected the inhibition of F. oxysporum by

Pseudomonas produced volatiles (Figure 3.2). The amino acid media without bacteria did not influence fungal growth. All bacteria significantly inhibited growth of the fungus as compared to their corresponding blank media controls except for P. rhodesiae 88A6 grown on

M9MM+glycine. Neither amino acid affected the inhibition potential of P. chlororaphis 14B11 volatiles. Only addition of methionine to the media significantly improved the inhibitory activity of P. rhodesiae 88A6 and P. protegens Darke as compared to their corresponding activity on

M9MM. P. rhodesiae 88A6 grown on M9MM+L-methionine was the best bacteria control treatment of F. oxysporum 289, reducing growth by over 80% compared with all three control media and P. rhodesiae 88A6 (M9MM). The effect L-methionine in combination with P. protegens Darke had on the fungus was not as pronounced, however mycelial growth was significantly lower than growth when exposed to Darke grown on M9MM.

Pseudomonas VOCs also affected C. elegans viability and reproduction (Figure 3.3).

Alone neither amino acid was inhibitory to C. elegans, as the control plates all had ratings of four (>200 nematodes) after a weeklong period. The standard C. elegans food source, E. coli

OP50, was also non-inhibitory to the nematodes on all media, however it could not grow well, if at all, on M9MM±glycine or L-methionine. When the bacteria were grown on LB agar, VOCs produced by P. chlororaphis 14B11 and P. protegens Darke were completely inhibitory to the

121 nematodes. This activity was fully lost in P. chlororaphis 14B11 and partially lost in P. protegens Darke when the bacteria were grown on M9 minimal medium. The addition of either glycine or methionine to the minimal medium fully restored inhibitory activity in P. protegens

Darke, while only the addition of glycine could restore full inhibition in P. chlororaphis 14B11.

The addition of methionine to M9MM increased the ability of P. rhodesiae 88A6 VOCs to inhibit nematodes as compared to the bacteria grown on nutrient rich LB agar. Across all treatments, Pseudomonas volatiles that resulted in a rating of zero (no living or moving nematodes) were nematocidal. However, reproductive capacity of the nematodes with limited reproduction during the assay was restored after removal of the bacterial volatiles.

3.4.2 Inhibition of F. oxysporum by volatiles produced by Pseudomonas grown on soil

The addition of methionine to treatments in topsoil caused significant reduction of F. oxysporum 289 growth. In indirect exposure assays where P. rhodesiae 88A6 or LB broth in

M9MM+250mM L-methionine was inoculated onto soil, fungal growth was significantly inhibited as compared to bacteria treatments without methionine. In the methionine treatments, the degree of inhibition was higher in the bacteria treatments (Figure 3.4). To gain a better understanding of why the LB treatments were comparable to bacteria treatments, after the final repetition of the assay, we took a small amount of soil from each plate and grew in LB to estimate the microbe populations in each treatment. Dilution plating on LB agar indicated substantial microorganism growth from each treatment (data not shown). Despite the double autoclaving before experimental setup, the soil was not sterile before inoculation with the P. rhodesiae 88A6 and LB suspensions, otherwise we would have expected the soil+LB treatment to have limited to no microorganism growth.

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3.4.3 VOC production by Pseudomonas

The volatile profile of the bacteria and controls on different amino acid-containing- media was diverse and complex. The compounds used for our analysis were >1ppbv in all replicates of at least one treatment (38 compounds total). These compounds varied in size from m/z 27.023 to 153.127, and abundance of each compound varied across the treatments as can been seen in the heat map (Figure 3.5). When PCA was applied to the data set, the 26 compounds (>1ppbv) that were significantly different across treatments (ANOVA α=0.05) accounted for 75.9% of the variation between the samples (Figure 3.6). In the PCA, both the controls (PCA A, B, C) and the M9MM±glycine Pseudomonas treatments (PCA D, E, G, H, J,

K) clustered together. The addition of methionine caused further separation of the treatments. P. chlororaphis 14B11 and P. protegens Darke (M9MM+M, PCA F, L) clustered together, and P. rhodesiae 88A6 was separate from the rest of the treatments (PCA I). The treatments in the PCA also clustered by inhibitory activity to F. oxysporum 289. The volatiles produced by the most inhibitory treatment, P. rhodesiae 88A6 on M9MM containing L-methionine, were distinctly different from the other, less inhibitory treatments.

Across all bacteria the most abundant category of compounds on media containing L- methionine was organosulfur compounds (Figure 3.7). The total quantity of volatiles was most influenced by addition of L-methionine to M9MM. The largest differences in volatile production were seen in P. rhodesiae 88A6 grown on M9MM+L-methionine, which produced over a three log-fold increase in total ppbv as compared to total VOCs on M9MM±glycine (Figure 3.7). Both

P. chlororaphis 14B11 and P. protegens Darke had HCN as the most abundant VOC on

M9MM±glycine . Multiple compounds were present >1ppbv only in the bacteria treatments grown on M9MM+L-methionine (Figures 3.5, 3.9, Supplemental Table S3.2). Chemical

123 formulas were determined based on the m/z of each compound, and putative identification of each compound is found in Appendix Table A1.1. Between the volatile quantification done in

Chapters 2 and 3, there was substantial overlap of the compounds produced; compounds quantified only in one experiment are specifically marked in the table. Though the remainder of the text, m/z will be referred to as their theoretical (calculated) mass, rather than the experimentally measured mass. This is due to slight variation of mass measurements between the experiments done in Chapters 2 and 3.

We were particularly interested in hydrogen cyanide and organosulfur compound production because glycine and methionine are the respective precursors to those compounds.

+ The effect of glycine and methionine on hydrogen cyanide (m/z 28.018, H2CN ) production

+ varied between the bacteria. The addition of glycine or methionine increased H2CN production by approximately 4-fold and 2-fold, respectively in P. chlororaphis 14B11. Increases due to either amino acid were less pronounced in P. protegens Darke. Neither amino acid restored average levels of HCN to quantities produced on LB (Figure 3.8). The controls and P. rhodesiae

88A6, which does not contain the hcnABC gene cluster, did not produce any amount of measurable hydrogen cyanide (Table 2.1). The LB data included in Figure 3.8 is from the PTR-

ToF-MS studies performed in Chapter 2 (Figure 2.8A).

The effects on organosulfur compounds produced by the bacteria with supplemented amino acids were more pronounced (Figures 3.5, 3.7, 3.9, Supplemental Table S3.2). The average values of the organosulfur compounds are reported here in the text, while standard deviation information can be found in Supplemental Table S3.2. The controls produced measurable amounts of multiple compounds. Addition of methionine had the largest effect on organosulfur compound production. The most abundant organosulfur compound produced by the

124

+ bacteria was methanethiol/DMDS fragment (m/z 49.011, CH5S ). This compound was absent in the M9 minimal medium treatments. Addition of methionine increased methanethiol by almost two log-fold in P. chlororaphis 14B11 (7.61 vs 618.15 ppbv) and over three log-fold in 88A6

(2.36 vs 6454.92 ppbv) as compared to production on minimal medium. P. protegens Darke had no production of methanethiol in minimal media but produced 429.78 ppbv on M9MM+L- methionine. Two additional compounds of interest due to their abundance and/or known biocontrol potential were DMS and DMDS. P. rhodesiae 88A6+amino acids were the only

+ treatments to produce DMS (m/z 63.026, C2H7S ) in quantities >1ppv, however methionine added to the media led to a greater production of the compound than glycine (7.38 vs 176.65

+ ppbv). CH3S (DMS/methanethiol fragment, m/z 46.995) was present in all treatments, however, was higher (1-2 log-fold) in bacteria grown on M9MM+L-methionine as compared to other minimal media. Addition of L-methionine in the culture media also increased DMDS (m/z

+ 94.998, C2H7S2 ), particularly in P. rhodesiae 88A6, which did not have any production of the compound in the other media (24.86 ppbv). Both P. chlororaphis 14B11 and P. protegens Darke had levels of DMDS >1ppbv when grown on M9MM+L-methionine, but to a lower level than

88A6 (1.53 and 3.43 ppbv respectively). Two additional organosulfur compounds increased on

+ L-methionine containing media were methyl thiocyanate (m/z 74.006, C2H4NS ) and S-methyl

+ thioacetate (m/z 91.021, C3H7OS ). P. chlororaphis 14B11 and P. protegens Darke were higher producers of methyl thiocyanate than P. rhodesiae 88A6, which may be related to the inability of this strain to produce hydrogen cyanide, another cyanogenic compound. P. rhodesiae 88A6 on

M9MM+ L-methionine was the only treatment to produce S-methyl thioacetate >1ppbv. As reference, the organosulfur compounds produced by bacteria when grown on LB are included, although the analysis was performed in a previous study (Chapter 2, Figure 2.9). The compound

125

+ m/z 77.042 (C3H9S ), quantified in LB in Chapter 2 (Figure 2.9) is left out of Figure 3.9 because no treatments in this chapter produced quantities >1 ppbv (all replicates).

3.4.4 Correlation of F. oxysporum inhibition with volatile production

Of the 26 VOCs that were present at >1ppbv and significantly different between the treatments, 15 compounds were correlated with inhibition (Table 3.1). Eight of the correlated compounds were organosulfur compounds or associated compound fragments. Pearson’s

Correlation Coefficient’s were also calculated for C. elegans rating (treatments on

M9MM±amino acids only), and no volatiles were significantly correlated with inhibition of the nematodes.

3.4.5 Presence of genes involved in methanethiol and hydrogen cyanide production

The three pseudomonads had different combinations of genes present for methanethiol production (Table 3.2). Each strain contained genes for three aminotransferases (BcAT, ArAT, and MetAT) that are involved in the transamination of methionine to α-keto-γ-(methylthio) butyric acid, which is then converted to methanethiol (Figure 3.1; Yvon & Rijnen, 2001). Every strain also contained at least one gene (MeGL, CBL, or CGL) involved in the direct conversion of methionine to methanethiol: P. rhodesiae 88A6 (MeGL and CBL) and P. protegens Darke

(MeGL) and P. chlororaphis 14B11 (CGL). The sequence of CGL in the P. chlororaphis 14B11 annotation most closely aligned to PLP-dependent transferase or cystathionine-gamma synthase in the blastp results. While P. rhodesiae 88A6 contained the annotation for CBL, it only matched

<65% with two of the reference sequences. The methanethiol is chemically converted to compounds including DMDS and dimethyl trisulfide (Yvon & Rijnen, 2001). The sequence for

126 the enzyme involved in conversion of methanethiol to DMS, MddA, was not present in any of the bacterial genomes. P. protegens Darke and P. chlororaphis 14B11 both had the entire HCN cluster (HcnABC) while P. rhodesiae 88A6 did not have any of the genes.

3.4.6 F. oxysporum 289 inhibition by DMS and DMDS

Of the quantities we tested, DMS was not fully inhibitory to F. oxysporum 289. Growth was reduced by over 25% at 688.26ppm (100µl) and over 92% at 2064.78ppm (300µl) when compared to both the water and blank controls. F. oxysporum exposed to 6.88ppm (1µl) and

68.83ppm (10µl) DMS had comparable growth to the controls. DMDS was fully inhibitory to F. oxysporum 289 at quantities 86.23ppm (10µl) and higher. DMDS was observed to be fungistatic, rather than fungicidal. One week after the DMDS was removed from the fungal plates

(Experiment 1), at least one plate from each inhibitory concentration had visible growth beyond the plug, however measurements were not taken for average mycelial area.

3.5 Discussion

In many biological systems, there is evidence for priming, the increase of specific activities though the selective input of substrate material(s). The “priming effect” of soil refers changes in the rate of soil organic matter mineralization though the input of organic and/or mineral carbon and nitrogen sources, which in turn can stimulate microbial activity (Kuzyakov et al, 2000). Due to priming effects from roots in the rhizosphere, microbial activity can be higher there than in bulk soil (Kuzyakov & Blagodatskaya, 2015). In addition, plants can be induced for defense against plant pathogens though the addition or presence of beneficial bacteria or specific compounds (Compant et al, 2005; Huang et al, 2012). While bacteria are capable of producing

127 many secondary metabolites, production of specific compounds can depend on the nutritional composition of the microorganism’s food source. When grown on different media compositions, bacteria produce metabolites that vary in both diversity and quantity. Volatile emission and bioactivity of Lysobacter spp. were different when grown on potato dextrose agar and nutrient agar, two media with different sugar and protein contents (Lazazzara et al, 2017). The amino acid composition and concentration in growth medium can influence the production of antibiotics and volatiles generated by bacteria as well as microbial activity (Aharonowitz &

Demain, 1978; Aly, 2009; Castric, 1977; Garbeva et al, 2014b). Our study focused on the priming of Pseudomonas and soil microbiome though manipulation of amino acids in the media, specifically glycine and methionine, two precursors to volatile compounds known for control potential against phytopathogens. We determined addition of specific amino acids to a low nutrient growth medium greatly impacted the bioactivity, quantity, and diversity of volatile organic compounds produced by three Pseudomonas strains.

The priming effect was seen with L-methionine. Addition of L-methionine to minimal medium increased the production and bioactivity of VOCs to the greatest extent. The effects of methionine were seen on both agar-based (F. oxysporum and C. elegans) and soil-based (F. oxysporum only) matrices (Figures 3.2, 3.3, 3.4). The topsoil in vitro volatile inhibition assays with P. rhodesiae 88A6 demonstrated the potential of priming both inoculated bacteria and background soil microbial populations with L-methionine to produce VOCs inhibitory to F. oxysporum. The soil priming effect may be seen here because the amount of available amino acids in the soil represents a small portion of dissolved organic nitrogen (Jones et al, 2004; Yu et al, 2002). Through addition of L-methionine into the environment, native soil microbes were able to produce sufficient levels of VOCs for fungal growth inhibition. Presumably this priming

128 effect could be seen with additional secondary metabolites through the addition of other precursor compounds (e.g. glycine for hydrogen cyanide production).

The addition of glycine to minimal media was less pronounced. By adding its precursor, we expected to see large increases in hydrogen cyanide production (Figure 3.1). While the

+ addition of glycine to the media increased average H2CN production to varying extents in both

P. chlororaphis 14B11 and P. protegens Darke, the amounts were not restored to the quantities produced when bacteria were grown on LB (Figure 3.8). However, the increase in cyanide content by 14B11 on M9MM+glycine was similar in magnitude to the difference in cyanide production seen in P. aeruginosa on complete medium±glycine by Castric (1977). The addition of glycine did not significantly increase the ability of the bacteria to inhibit mycelial growth of F. oxysporum 289 as compared to the bacteria grown on minimal medium (Figure 3.2).

Alternatively, addition of glycine to the culture medium restored the full inhibitory activity of P. chlororaphis 14B11 and P. protegens Darke VOCs against C. elegans (Figure 3.3).

When grown on minimal medium+L-methionine, P. rhodesiae 88A6, the strain with most enhanced activity against F. oxysporum, produced more organosulfur compounds than the other bacteria and controls (Figures 3.7, 3.9, Supplemental Table S3.2). Because this strain had a markedly larger increase in organosulfur compound production than the other bacteria on minimal medium containing L-methionine, we investigated possible genetic differences among the bacteria in regard to organosulfur biosynthesis. There are multiple routes bacteria can use to produce methanethiol (precursor to other organosulfur compounds) (Figure 3.1). Three enzymes involved in the direct conversion of methionine to methanethiol are methionine gamma-lyase

(MeGL), cystathionine beta-lyase (CBL), and cystathionine gamma-lyase (CGL). While each enzyme can produce methanethiol from methionine, the substrate specificity varies between the

129 enzymes. MeGL (derived from Brevibacterium linens BL2) demonstrated higher activity on L- methionine than other sulfur-containing amino acid L-cysteine and no activity on L- cystathionine, while CGL (derived from subsp. cremoris SK11) and CBL

(derived from L. lactis subsp. cremoris B78) had inverse specificities (activity of L- cystathionine>L-cysteine>L-methionine) (Alting et al, 1995; Bruinenberg et al, 1997; Dias &

Weimer 1998b). Cell extracts of P. aeruginosa PAO1 and P. putida S-313 had varied levels of

MeGL, CBL, and CGL activity when tested on multiple organosulfur substrates, which suggests activity may be bacteria specific in addition to substrate specific (Vermeij & Kertesz, 1999). Of the two strains that contain the gene for MeGL, the amount of methanethiol produced by P. rhodesiae 88A6 was over one log-fold higher than P. protegens Darke on methionine containing growth media, indicating enzyme activity may vary between the strains (Figure 3.9). P. chlororaphis 14B11, which only has the gene for GCL, also produced approximately one log- fold less methanethiol than P. rhodesiae 88A6, possibly because the activity of the enzyme is less than that of MegL on L-methionine. Due to the blastp results of the CGL sequence, it is also possible P. chlororaphis 14B11 does not have the CGL gene, and methanethiol is produced via the aminotransferase route (Figure 3.1). It is possible the presence of proteins in the bacteria genomes may be different if the number of sequences used in the queries were larger.

The volatile compounds that were most significantly associated with fungal inhibition were organosulfur compounds and multiple CnHn- and CnHnOn- containing fragments (Table

3.1). These associations were expected, as the most effective treatments for inhibiting F. oxysporum 289 were bacteria grown on methionine-containing media. We were particularly

+ + + interested in m/z 94.998, 78.967, and 49.011 (respectively C2H7S2 , CH3S2 , and CH5S ), putatively identified as DMDS and its associated fragments (Perraud et al, 2016). Multiple

130 pseudomonads capable of biocontrol against plant pathogens produce DMDS (De Vrieze et al,

2015; Guevara-Avendaño et al, 2019; Ossowicki et al, 2017; Zhou et al, 2014). P. rhodesiae

88A6 on L-methionine-containing medium both produced higher levels of DMDS and its associated fragments than all other treatments, and inhibited F. oxysporum 289 to the greatest extent. These results indicate the potential for DMDS to contribute to the increased activity of the bacterium when grown on methionine (Figures 3.2 and 3.8).

DMDS is used commercially in the control of plant diseases. Due to the Montreal

Protocol the fumigant methyl bromide (MBr) is being phased out worldwide, and consequently additional chemicals including DMDS have been registered though the US Environmental

Protection Agency on multiple cropping systems as alternatives to MBr (UNEP, 2019; USEPA,

2012). Paladin® (Arkema, Pennsylvania, USA), a soil fumigant with DMDS as its active ingredient, is registered as a nematicide, fungicide, and herbicide of many fruit, vegetable, and tree crops (Arkema, 2016). In field trials, treatment of soil with Paladin® or Paladin®:chloropicrin before planting led to decreased pathogen population levels and severity and increased crop yield

(Keinath et al, 2012; Leocata et al, 2014). Field and greenhouse trials with DMDS as a soil fumigant saw reduced disease expression and pathogen populations (caused by F. oxysporum) in infested soil as compared to untreated controls additionally, when applied as a soil drench,

DMDS can induce systemic resistance against foliar pathogens (Gómez-Tenorio et al, 2015;

Gómez-Tenorio et al, 2018; Huang et al, 2012). Additional assays have investigated the potential of DMDS to inhibit soil pathogens in a more controlled, in vitro environment. In indirect volatile exposure assays fungi, oomycetes and bacteria were inhibited to varying degrees in the presence of DMDS (Briard et al, 2016; De Vrieze et al, 2015; Guevara-Avendaño et al, 2019; Lo Cantore et al, 2015; Ossowicki et al, 2017; Zhou et al 2014). We found that the inhibition of F.

131 oxysporum 289 with DMDS was dose dependent, and at low concentrations the compound was not inhibitory (Table 3.3). Other studies support this observation, as the activity of DMDS was increased when exposed to higher levels of the compound (De Vrieze et al, 2015; Lo Cantore et al, 2015; Zhou et al, 2014). In biocontrol systems, DMDS has the potential to serve a dual purpose. In addition to directly antagonizing the pathogen, DMDS can also aid in plant growth promotion. On sulfur-free media, exposure to DMDS significantly increased Nicotiana attenuata phenotypes including lateral root density, leaf surface area, and chlorophyll concentration

(Meldau et al, 2013). In contrast to the aforementioned examples, DMDS also has the potential to promote microorganism growth under the right conditions. The addition of DMDS to a closed system significantly stimulated the growth of Aspergillus fumigatus grown on sulfur-deficient medium in vitro (Briard et al, 2016).

It is unlikely that every volatile correlated with F. oxysporum 289 contributed equally to the inhibition of the fungus. For example, dimethyl sulfide and its associated fragment (m/z

+ + 63.026 and 46.995, respectively C2H7S and CH3S ), produced by P. rhodesiae 88A6 at over 100 ppbv, is an organosulfur compound that can be produced from methanethiol in soils by many bacteria (Carrión et al; 2015; Carrión et al, 2017). In contrast to the DMDS activity, DMS was less active against F. oxysporum 289, not fully inhibiting the fungus at any tested concentration

(Table 3.3). In addition, when Briard et al (2016) exposed DMS to Aspergillus fumigatus grown on minimal medium±sulfur, growth of the fungus was enhanced, rather than inhibited (Briard et al, 2016). Mass fragments of DMDS and DMS also represent methanethiol, the precursor to

+ + DMDS and other organosulfur compounds (m/z 49.011 and 46.995, CH5S and CH3S respectively). Lo Cantore et al (2015) demonstrated methanethiol can significantly inhibit the growth of non-pathogenic spp.at high levels of exposure, although unlike DMDS

132 methanethiol did not fully inhibit the fungi at any concentration. The biocontrol potential of

+ + methyl thiocyanate (m/z 74.006, C2H4NS ) and S-methyl thioacetate (m/z 91.021, C2H7S2 ), two additional compounds correlated with inhibition of F. oxysporum 289, is discussed in greater detail in Chapter 2. Both compounds could have contributed to inhibition of F. oxysporum, however were present in P. rhodesiae 88A6 on M9MM+L-methionine at lower amounts than

DMDS and its associated fragments; additionally, P. chlororaphis 14B11 grown on M9MM+L- methionine produced the highest level of S-methyl thiocyanate but caused the same degree of inhibition to F. oxysporum 289 as 14B11 grown on M9MM. As mentioned in Chapter 2, further studies of the VOC profile of the Pseudomonas strains on minimal medium could be performed over a longer period to more accurately correlate individual VOCs with microorganism inhibition.

3.6 Conclusions and Future Directions

This study demonstrated the potential to prime Pseudomonas for production of select volatile compounds though manipulation of the culture medium. Supplementation of M9 minimal medium with L-methionine increased organosulfur compound production by multiple log-fold.

The extent of increase of microorganism inhibition with addition of L-methionine varied by bacterium, possibly due to the presence and expression of MeGL, CBL, CGL, and aminotransferases. Of the three bacteria investigated in this study, P. rhodesiae 88A6 had the largest increase in VOC production and biocontrol activity upon addition of L-methionine to the culture medium. The results found here can be broadly applied to other nutrient poor zones such as the rhizosphere, in which specific compounds of interest can be selected for though nutrient manipulation of the environment. We have identified some future directions to be taken with the

133 project: 1) establish the potential of bacteria priming for VOC production in a larger, more applied setting. We conducted our priming experiments in small scale in vitro experiments, and work should be done to investigate whether the phenomena observed here can occur at the greenhouse or field scale; and 2) further investigate the effect of priming the soil with amino acids. Addition of L-methionine alone to topsoil was sufficient to decrease F. oxysporum growth through production of antagonistic volatiles, and work should be done to investigate how amino acid supplementation to soil changes the microbial community of the soil. Future research will also need to be performed to identify amino acid turnover in the system. The half-life of amino acids in soils has been shown to occur in stages: 20-25% of the inputs have a short half-life estimated in a matter of hours, while the remining 75-80% have a half-life of approximately a month, although results vary soil by soil (Jones et al, 2004; Jones & Kielland, 2012). To establish the maximal priming effect with amino acids, we need to determine how long the inputs can be utilized by soil microorganisms before being transformed and broken down.

We acknowledge Drs. Cosimo Taiti and Diego Comparini (LINV, Sesto Fiorentino, Tuscany-Italy) for their assistance in performing and analyzing the data from the PTR-ToF-MS experiments,

Edwin Daniel Navarro Monserrat with help with the in vitro assays, and The Translational Plant

Sciences Graduate Program for funding the PTR-ToF-MS experiments.

134

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A

B

Figure 3.1. Pathways of (A) hydrogen cyanide (HCN) and (B) organosulfur compounds biosynthesis. A) HCN is produced from glycine in Pseudomonas. This conversion requires the presence of the hcnABC gene cluster, which encodes hydrogen cyanide synthase(Laville et al 1998; figure adapted from Gross and Loper 2009); B) Methionine is converted to methanethiol (MeSH) via the transamination (multiple AtAses) or elimination routes (enzymes MeGL, CBL, or CGL), which is subsequently converted to additional sulfur compounds (figure adapted from Carrión et al 2015, Dias and Weimer 1998a, Ganesan and Weimer 2017, Liu et al 2008, and Yvon and Rijnen 2001). Organosulfur compounds biosynthesis is complicated, and the pathway presented here is simplified. Greater detail can be found in the sources the figure was adapted from.

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Figure 3.2. Indirect volatile exposure inhibition of F. oxysporum 289 by Pseudomonas spp. grown on minimal medium with and without supplementation of amino acids. Bacteria were growth on M9 minimal medium (M9MM), M9MM supplemented with 250mM glycine (+glycine), M9MM supplemented with 250mM L-methionine (+L-methionine). Inhibition of the fungus by Pseudomonas was assessed after a week of indirect exposure. Fusarium was exposed to the volatiles produced by each bacterium in a closed system. Values presented are percentage of the total petri plate area. Each treatment was tested in two independent assays, and the results of both assays were combined. n= 7 or 8. Data shown are mean± standard error. Significance between all treatments was determined using ANOVA followed by a post-hoc Tukey test (α=0.05). Treatments with the same letter are not significantly different from one another.

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Figure 3.3. Indirect volatile exposure inhibition of C. elegans by Pseudomonas spp. grown on LB or minimal medium with and without supplementation of amino acids. Bacteria were grown on either LB, M9 minimal medium (M9MM), or M9MM supplemented with 250mM glycine or 250mM L-methionine. Inhibition of the nematodes by Pseudomonas volatiles was assessed after a week of indirect exposure in a sealed system. Inhibition was rated on a scale 1-4, where 0= 0 living/moving nematodes; 1=1-20 nematodes; 2=21-100 nematodes; 3=101-200 nematodes; and 4=200+ nematodes. Each treatment was tested in two independent assays and the results were combined. n=9-11. Data shown are mean±standard error. Significance between the bacteria treatments and corresponding blank media controls was determined using the Kruskal-Wallis non-parametric test followed by the post-hoc Dunn multiple comparison test. *p<0.05, **p<0.01, ***p<0.001.

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Figure 3.4. Indirect volatile exposure inhibition of F. oxysporum 289 by P. rhodesiae 88A6 grown on topsoil supplemented with L-methionine. Bacteria were diluted in M9 minimal medium±250mM L- methionine and added to autoclaved topsoil. Inhibition of the fungus was assessed after a 10-day indirect exposure period. Values presented are the percentage of the petri plate area. Each treatment was tested in three independent assays and the results combined. n=12 for each treatment. Data shown are mean±standard error. Significance between all treatments was determined using ANOVA followed by a post-hoc Tukey test (α=0.05). Treatments with the same letter are not significantly different from one another.

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m/z 27.02328.01830.04631.01833.03339.02341.03943.01843.05445.03346.99547.04949.01151.01 53.03955.05457.03357.07 59.04961.02862.99 63.02663.94565.03969.07 73.06574.00675.04478.96783.04983.08691.02191.05893.99794.99896.998/96.995129.091153.127 M9MM Control M9MM+G M9MM+M M9MM P. chlororaphis 14B11 M9MM+G M9MM+M M9MM P. rhodesiae 88A6 M9MM+G M9MM+M M9MM P. protegens Darke M9MM+G M9MM+M

log(n+1) Scale 0 4

Figure 3.5 Heat map showing the average intensities (ppbv) of the volatile profile of Pseudomonas spp. strains grown on media with different amino acid compositions. Bacteria were growth on M9 minimal medium (M9MM), M9MM supplemented with glycine (M9MM+G), M9MM supplemented with L-methionine (M9MM+M). Compounds at quantities >1 ppbv in all replicates of at least one bacterium or the control (38 total) are included. The bacteria are organized by species. n=3 for each treatment. Average values are displayed. Before averaging treatments, the log(n+1) transformation was performed on the data set. This transformation was taken to better visualize differences due to the high range in abundance among compounds.

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Figure 3.6. Principal component analysis (PCA) score plot of Pseudomonas spp. grown on minimal media with and without supplementation of amino acids. Bacteria (P. chlororaphis 14B11, P. rhodesiae 88A6, P. protegens Darke) were grown on M9 minimal medium (M9MM), M9MM supplemented with glycine (+Glycine, +G), M9MM supplemented with L-methionine (+Methionine, +M). A) Each treatment is designated with a letter and colored according the growth medium; B) each treatment is colored according to the amount of F. oxysporum 289 growth. The first two Eigenvalues account for 75.9% of the variability within the data set. 26 compounds that were >1ppbv and significantly different among the treatments were used to generate the PCA (ANOVA; α=0.05). Data were log(n+1) transformed and mean centered before subjecting to PCA. Each replicate for every treatment is shown as a point. n= 3 for each treatment.

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Figure 3.7. Cyanide and sulfur-containing VOCs compared to the total amount of volatile organic compounds produced by each treatment. All compounds >1ppbv in at least one treatment are included. Bacteria were growth on M9 minimal medium (M9MM), M9MM supplemented with glycine (+G), M9MM supplemented with L-methionine (+M). (A) is the quantity of VOCs in each category as ppbv; (B) is each category of VOC as a percentage of total VOCs produced by each treatment. average±standard deviation is shown. n=3.

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+ Figure 3.8. Hydrogen cyanide (CH2N , m/z 28.018) produced by Pseudomonas spp. strains grown on media with different amino acid compositions. Bacteria were growth on M9 minimal medium (M9MM), M9MM supplemented with glycine (+G), or M9MM supplemented with 250mM L-methionine (+M). Organosulfur compounds produced by the controls and bacteria growth on LB are also included for comparison. N=3 for each treatment. Average±standard deviations are shown.

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Figure 3.9. Organosulfur compounds produced by Pseudomonas spp. strains grown on media with different amino acid compositions. Bacteria were growth on M9 minimal medium (M9MM), M9MM supplemented with glycine (+G), or M9MM supplemented with methionine (+M) Organosulfur compounds produced by the controls and bacteria growth on LB from Chapter 2 are also included for comparison. n=3 for each treatment except for the LB control (n=6). Average±standard deviations are + shown in Table S3.1. Putative chemical formula and identity of the masses are m/z 46.995 (CH3S ); m/z + + 49.011 (CH5S , methanethiol/DMDS fragment); m/z 62.990 (CH3OS , DMS/methanethiol fragment); m/z + + + 63.026 (C2H7S , DMS); m/z 74.006 (C2H4NS , methyl thiocyanate); m/z 78.967 (CH3S2 , DMDS fragment); + + m/z 91.021 (C3H7OS , S-methyl thioacetate); m/z 91.058 (C4H11S , S-compound fragment); m/z 94.998 + + + (C2H7S2 , DMDS); m/z 96.995 or 96.998 (CH5O3S or C4H3NS , S-compound fragment) .

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Table 3.1. Pearson’s correlation coefficients for VOCs correlated with F. oxysporum 289 inhibition. Negative correlation coefficients correspond with inhibition of the fungus. Fungal areas (% plate area) were used in these comparisons. A compound was considered correlated with a negative coefficient value and p<0.05.

Pearson's Correlation m/z Chemical Formulaa Tentative ID P-value Coefficient + 43.018 C2H3O Fragment (ester) -0.778 0.003 + 46.995 CH3S DMS/MT Fragment -0.819 0.001 + 49.011 CH5S MT/DMDS Fragment -0.810f 0.001 51.010 Unknown -- -0.815 0.001 + 53.039 C4H5 Alkylic Fragment -0.735 0.006 Acetic Acid/Fragment 61.028 C H O + -0.786 0.002 2 5 2 (ester) + 62.990 CH3OS S-compound fragment -0.789 0.002 + 63.026 C2H7S Dimethyl Sulfide (DMS) -0.779 0.003 63.945 Unknown -- -0.836 0.001 Alkylic Fragment 65.039 C H + -0.780 0.003 5 5 (Ethanol) + 78.967 CH3S2 DMDS Fragment -0.834 0.001 + 91.021 C3H7OS S-methyl thioacetate -0.797 0.002 + 91.058 C4H11S S-compound fragment -0.793 0.002 93.997 Unknown -- -0.800 0.002 Dimethyl Disulfide 94.998 C H S + -0.833 0.001 2 7 2 (DMDS) achemical formula determined based on m/z.

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Table 3.2. Genome search for the presence of genes coding for enzymes involved in methanethiol and hydrogen cyanide biosynthesis. Methanethiol is the intermediary metabolite between methionine and other organosulfur compounds such as DMS and DMDS. The annotated genomes were searched for enzymes involved in the elimination route: methionine gamma-lyase, MeGL (EC 4.4.1.11); cystathionine beta-lyase, CBL (EC 4.4.1.8); cystathionine gamma-lyase, GCL (EC 4.4.1.1); and transamination route: branched-chain amino acid aminotransferase, BcAT (EC 2.6.1.42); aromatic-amino-acid aminotransferase, ArAT (EC 2.6.1.57); methionine aminotransferase, MetAT (EC 2.6.1.88); hydrogen cyanide synthase, HcnABC (1.4.99.5). Protein sequences used in tblastn for MeGL, CBL, CGL, and HcnABC are found in Supplemental Table 2.1.

Bacteria MeGL CBL CGL BcAT ArAT MetAT HcnA HcnB HcnC P. chlororaphis 14B11 Xab X X X X X X P. rhodesiae 88A6 X X X X X P. protegens Darke X X X X X X X aThe blastp results of the protein sequence from the annotated file were similar to PLP-dependent transferase or cystathionine-gamma synthase bThe protein sequence for CGL (P. aeruginosa PAO1) was identical to multiple sequences of cystathionine gamma-synthase. This was the only RefSeq Pseudomonas CGL sequence available.

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Table 3.3. Inhibition of F. oxysporum 289 by DMDS and DMS. A) is inhibition due to DMDS and B) is inhibition due to DMS. Individual chemicals were added to filter paper saturated with water and exposed to the fungus in indirect exposure assays. NG indicates no growth beyond the fungal plug. With the exception of 2064.78ppm DMS, each treatment was tested in two independent experiments and the results combined. n=3 or 6.

A 8.62 43.12 86.23 431.17 862.35 Blank H O DMDS 2 ppm ppm ppm ppm ppm Average % Plate Area 71.49 71.68 70.48 5.03 NG NG NG Standard Deviation % 2.86 5.42 5.55 1.89 ------Plate Area

B 6.88 68.83 688.26 2064.78 Blank H O DMS 2 ppm ppm ppm ppm Average % Plate Area 57.91 57.41 57.25 57.80 43.20 4.23 Standard Deviation % 13.38 14.76 13.53 11.54 18.75 5.29 Plate Area

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Supplemental Table S3.1. Protein sequences used in tblastn search for presence of organosulfur compound and hydrogen cyanide synthesis genes in three Pseudomonas strains. The complete genomes of P. chlororaphis 14B11 (NZ_MOAN01000000), P. rhodesiae 88A6 (NZ_MOBA01000000), and P. protegens Darke (NZ_MOAX01000000) were searched against the protein sequences. The gene was considered present in the genome if at least one reference sequence has a match with % identity ≥65%. Sequences obtained from: https://www.ncbi.nlm.nih.gov/protein

NCBI Reference Sequence Number/ Organism Name GenBank Accession Number Methionine Gamma Lyase (MeGL) (E.C. 4.4.1.11) MULTISPECIES Pseudomonas WP_003442381.1 MULTISPECIES Pseudomonas WP_122711835.1 WP_034138419.1 Pf-5 AAY92781.1 Pseudomonas protegens CHA0 VAV69833.1 Cystathionine Beta-Lyase (CBL) (4.4.1.8) MULTISPECIES Bacillus WP_003228854.1 MULTISPECIES Pseudomonas WP_053121572.1 MULTISPECIES Pseudomonas WP_169962785.1 Pseudomonas fluorescens WP_012723472.1 Pseudomonas fluorescens WP_046035455.1 Pseudomonas syringae WP_017683912.1 Cystathionine Gamma-Lyase (CGL) (EC 4.4.1.8)

Pseudomonas aeruginosa PAO1 NP_249091.1a Mycobacteroides abscessus WP_005111723.1 MeSH-dependent DMS A (MddA) Pseudomonas deceptionesis AJE75769.1 Methionine Aminotransferase (MetAT) (EC 2.6.1.88) MULTISPECIES: pyridoxal phosphate-dependent aminotransferase [Pseudomonas] (methionine WP_003106648.1 aminotransferase; validated) Hydrogen Cyanide Synthase A (HcnA) MULTISPECIES Pseudomonas WP_072396115.1 Pseudomonas protegens AAC38594.1 Pseudomonas fluorescens F113 AEV62378.1 Hydrogen Cyanide Synthase B (HcnB) MULTISPECIES Pseudomonas WP_011060874.1 MULTISPECIES Pseudomonas WP_041073373.1 Pseudomonas fluorescens F113 AEV62379.1 Hydrogen Cyanide Synthase C (HcnC) MULTISPECIES: Pseudomonas WP_058637820.1 Pseudomonas protegens AAC38596.1 Pseudomonas fluorescens F113 AEV62380.1 aThe protein sequence for CGL (P. aeruginosa PAO1) was identical to multiple sequences of cystathionine gamma-synthase. This was the only RefSeq Pseudomonas CGL sequence available.

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Supplemental Table S3.2. Organosulfur compounds produced by Pseudomonas spp. on M9 minimal medium±amino acids. A) is the average and B) is the standard deviation of 3 biological replicates/treatment. M9 minimal medium was supplemented with 500mM glycine (+G) or 250mM L-methionine (+M).

A Average Organosulfur Compounds

46.995 49.011 62.990 63.026 74.006 78.967 91.021 91.058 94.998 96.995/96.998 Treatment + + + + + + + + + [CH3S+] [CH5S ] [CH3OS ] [C2H7S ] [C2H4NS ] [CH3S2 ] [C3H7OS ] [C4H11S ] [C2H7S2 ] [CH5O3S / C4H3NS]

M9MM 0.00 0.00 0.00 0.00 0.00 0.49 0.00 0.35 0.00 2.00

Control +G 1.12 0.00 0.00 0.00 0.00 1.11 0.00 0.40 0.11 1.83

+M 0.67 0.00 0.00 0.00 0.00 1.36 0.00 0.46 0.09 1.76

M9MM 4.02 7.61 0.00 0.00 2.56 7.27 0.00 0.49 0.49 0.00 P. chlororaphis +G 2.83 0.93 0.00 0.00 4.33 5.12 0.00 0.35 0.44 0.00 14B11 +M 114.70 618.15 0.46 0.23 69.51 21.38 0.78 0.50 1.53 0.10

M9MM 1.64 2.36 0.00 0.15 0.32 0.00 0.00 0.44 0.00 0.00 P. rhodesiae +G 4.59 15.67 0.44 7.38 0.45 0.98 0.00 0.26 0.00 0.00 88A6 +M 824.69 6454.92 10.69 176.65 6.39 353.04 26.58 5.41 24.86 1.78

M9MM 0.48 0.00 0.00 0.00 1.01 1.04 0.00 0.59 0.11 0.00 P. protegens +G 1.60 1.90 0.00 0.00 0.66 1.95 0.00 0.42 0.14 0.00 Darke +M 77.49 429.78 0.20 0.00 21.71 50.08 0.91 0.44 3.43 0.21

(Table S3.2 continued).

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(Table S3.2 continued).

B Standard Deviation Organosulfur Compounds

46.995 49.011 62.990 63.026 74.006 78.967 91.021 91.058 94.998 96.995/96.998 Treatment + [CH3S+] [CH5S+] [CH3OS+] [C2H7S+] [C2H4NS+] [CH3S2+] [C3H7OS+] [C4H11S+] [C2H7S2+] [CH5O3S / C4H3NS]

M9MM 0.00 0.00 0.00 0.00 0.00 0.85 0.00 0.11 0.00 0.21

Control +G 0.73 0.00 0.00 0.00 0.00 1.42 0.00 0.15 0.18 0.16

+M 0.32 0.00 0.00 0.00 0.00 0.80 0.00 0.16 0.15 0.25

M9MM 3.57 2.79 0.00 0.00 2.51 9.30 0.00 0.18 0.59 0.00 P. chlororaphis +G 1.66 0.50 0.00 0.00 2.19 4.53 0.00 0.33 0.38 0.00 14B11 +M 28.29 279.73 0.13 0.21 36.16 14.99 0.23 0.04 1.15 0.17

M9MM 0.50 4.09 0.00 0.26 0.05 0.00 0.00 0.07 0.00 0.00 P. rhodesiae +G 4.56 20.00 0.38 6.40 0.23 0.59 0.00 0.23 0.00 0.00 88A6 +M 275.83 2499.24 4.22 73.79 3.00 109.18 7.42 1.51 5.72 0.40

M9MM 0.30 0.00 0.00 0.00 0.31 1.80 0.00 0.25 0.19 0.00 P. protegens +G 1.18 3.29 0.00 0.00 0.14 2.80 0.00 0.01 0.24 0.00 Darke +M 10.50 34.53 0.17 0.00 12.36 7.15 0.04 0.08 0.88 0.18

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Chapter 4 Evaluation of Bacteria Treatments as Biocontrol Agents of Soybean Cyst Nematode in

Microplot and Greenhouse Trials.

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4.1 Abstract

Soybean Cyst Nematode (SCN) is an obligate plant parasite that is annually responsible for billions (USD) in economic loss. Due to the nematode’s economic relevance, paired with the fact there is no single method of managing this plant pathogen, it is vital to search for new methods of control. We investigated the biocontrol potential of eight bacteria (from the genera

Pseudomonas, Bacillus, and Pantoea) to act as nematode control agents and plant growth promoters in greenhouse and microplot studies. Three microplot studies were performed to test the bacteria against SCN. Bacteria were applied as single strains or in consortia, and as seed treatments or soil drench. Nematodes were tested at high and low inoculation loads. Results from the microplot studies were inconsistent. Select treatments demonstrated control potential and soybean yield increase in at least one experiment. Of the eight bacteria treatments that were tested in all three microplot trials, however, none were consistently effective. Two greenhouse trials demonstrated no difference in nematode reduction or plant growth promotion between the controls and bacteria treatments. This study demonstrated the potential of select treatments but identified the need to perform further investigation in the varied efficacy of the bacteria. While the results from individual studies may be promising, the ideal target for SCN control will need to show consistent results through multiple experiments in both nematode control and soybean yield increase.

4.2 Introduction

Soybean is an important, widely grown commodity crop in North America. In 2019, over

76 million acres of soybean were planted in the United States, with 4.3 million acres planted in

Ohio (USDA-NASS, n.d c.). Phytopathogens can cause devastating yield loss within this system.

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Between 2010-2014, plant disease caused over $21 billion USD in economic damage

(corresponding to loss of over two billion bushels) across 28 US soybean-producing states and

Ontario, Canada. Soybean cyst nematode (SCN, Heterodera glycines) was the most destructive phytopathogen to soybean crops in this period, resulting in an estimated loss of over half a billion bushels (Allen et al, 2017). SCN is a widespread plant parasite, found across the soybean growing region of the United States (Tylka & Marett 2017; USDA-NASS, n.d b). As of 2017, 71 out of 88 counties in Ohio have recorded incidence of SCN (SCN in Ohio, n.d.). Yield loss due to SCN (and other phytopathogens) can be gathered in multiple ways including field surveys, research plots, and cultivar trial performance ratings (Allen et al 2017). While variation occurs between sites and cultivars, soybean yield can be substantially lower in fields infested with SCN as compared to fields with no nematodes present; in infested soil yields vary depending on use of

SCN-susceptible or -resistant cultivars and high or low nematode pressure (Chen et al, 2001;

McCarville et al, 2017; Rupe et al, 1997; Wang et al, 2003; Wheeler et al, 1997). In Ohio between 2003-2005 soybean cyst nematode was the second ranked phytopathogen responsible for yield loss, behind only the oomycete Phytophthora sojae, causal agent of Phytophthora root and stem rot (Wrather & Koenning, 2006).

Due to its high economic impact and widespread prevalence, it is imperative to control

SCN. Currently, multiple control strategies are used, although none can minimize nematode damage. Effective control strategies in place for the disease do not reduce SCN populations by

100%, however they can substantially lower populations in the soil. We discuss widely used methods here; however, additional do exist to control the nematodes. Multiple chemical nematicides are sold on the market, however in field trials they have varied efficacy and are generally not recommended in lieu of other management strategies (Ahmed et al, 2018; Frye,

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2009; Niblack & Tylka, n.d; Staton & Seamon 2018, Yabwalo et al, 2019). One of the most commonly used methods of SCN control is planting SCN-resistant soybean cultivars.

Commercially grown SCN-resistant varieties are developed through breeding programs in which the resistance genes in nematode resistant lines are combined with lines of soybean with more desirable traits including higher yield. Most commercial varieties of soybean advertised as SCN- resistant have resistance derived from cultivar PI 88788. Relatively few commercially available

SCN-resistant varieties of soybean have resistance derived from sources other than PI 88788

(Tylka & Mullaney, 2019). In Ohio SCN populations from multiple counties were able grow on

PI 88788 at levels ≥10% as compared to a susceptible check, indicating host compatibility with the resistant cultivar (Niblack et al, 2002; Therese Miller & Christopher Taylor, unpublished).

Due to nematode populations growing on soybean lines with resistance from PI 88788, it is imperative to breed new lines with other sources of resistance and use additional SCN control strategies.

Another control strategy for SCN is the use of crop rotation. Soybean rotation with non- host crops can both decrease nematode populations and increase soybean yield following the rotation (Niblack & Tylka n.d.; Niblack, 2005; Porter et al, 2001; Rupe et al, 1997). Successful crop rotation strategies can also involve use of soybean resistant cultivars in combination with non-host plants (Niblack, 2005; Rupe et al, 1997). Unfortunately, because the beneficial effects of the rotation can be lost after successive soybean planting, additional nematode control strategies are needed (Porter et al, 2001).

One final method that is increasingly studied to manage SCN is biological control.

Multiple bacteria and fungi have been investigated as control agents of the nematodes (Aly,

2009; Chen & Liu, 2005; Kloepper et al, 1992; Tian et al, 2000; Timper & Riggs, 1998). As

158 control agents, microorganisms employ multiple modes of action against target pathogens including direct antagonism, secreted antibiotics, and volatile compound production (Köhl et al,

2019). Chapters 2 and 3 of this work explore some of these modes of action as they relate to inhibition of the fungus Fusarium oxysporum and free-living nematode Caenorhabditis elegans by Pseudomonas spp. and Pantoea agglomerans strains. Multiple bacteria-based bioproducts are currently registered with the United States Environmental Protection Agency and commercially sold to control SCN (including Poncho®/VoTiVO®, BASF; Clariva®, Syngenta Corporation;

Aveo® EZ, Valent Biosciences; BioST®, Albaugh). The products are formulated as either living microorganisms (Poncho®/VOTiVO®, Clariva®, and Aveo® EZ) or heat-killed cells (BioST®).

These products have varied effectiveness in controlling SCN populations and increasing yield compared to the control (Ahmed et al, 2018; Bissonnette et al, 2018; Musil et al, 2015; Staton &

Seamon 2018; Tylka, 2019; Yabwalo et al, 2019), and continued research is needed to develop additional products. The focus of this chapter is the investigation of Pseudomonas, Bacillus, and

Pantoea strains as biological control agents of SCN. This study is of importance due to the aforementioned limitations of other methods of SCN control. Previous studies done by the

Taylor Laboratory investigated the use of Pseudomonas to control SCN in greenhouse trials, and this study builds upon those trials, testing the bacteria in controlled microplot field experiments

(Figure 4.1) (Aly, 2009; Xiao-Yuan Tao & Christopher Taylor, unpublished). The aim of this chapter is twofold: to determine whether 1) bacterial treatments can control SCN in greenhouse and microplot trials, and 2) if the treatments result in increased yield in microplot trials.

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4.3 Materials and Methods

Microplot and greenhouse trials were conducted in collaboration with 3Bar Biologics

Inc., an agricultural biologicals company based in Columbus, OH.

4.3.1 Plant material

The SCN-susceptible soybean cultivar ‘Kottman’ was used in all microplot and greenhouse assays. Additional susceptible soybean cultivars ‘Hutcheson’ and ‘Lee’ were used in nematode propagation. All seed was obtained from Anne Dorrance (Department of Plant

Pathology, The Ohio State University, Wooster, OH).

4.3.2 Nematode inoculum preparation-microplots

The SCN population used was a HG-type (Heterodera glycines-type) 1, 2, 5, 7 from

Wood County, OH. HG-typing was previously performed by the Taylor Laboratory according to the protocol described by Niblack et al (2002). Populations of the nematodes were maintained in the greenhouse on SCN-susceptible soybean cultivars. The soybean plants were maintained in an approximately 1:1 all-purpose sand:Turface® mixture supplemented with Osmocote® (14:14:14

NPK) (all-purpose sand: 2.5-50lb bags all-purpose sand, 1.25 cubic feet; Turface®: 1-50lb bag,

1.35 cubic feet; Osmocote®: either 150 cubic centimeters or 1% of the total volume of the sand:turface). Inoculum was prepared one to two days prior to nematode inoculation. In brief, the root system of an infested plant was placed in a bin filled with tap water, mixed, and poured over a pair of nested sieves (#30 sieve over a #60 or #80 sieve, mesh sizes respectively 600, 250, and

180 microns). The cysts were collected in the #60 (or #80) sieve. An individual plant system was rinsed until most cysts were harvested. Cysts were washed from the sieve into tap water and ground using a modified drill press with a rubber stopper attachment through an additional set of

160 sieves (rubber stopper ground into #100 (mesh size 149 microns) sieve, where eggs passed through a #230 (mesh size 63 microns) sieve before final collection in a #500 sieve (mesh size

25 microns). Eggs were washed from the sieve and stored in the cold room before use. In the

2017 microplot trial, 75,000 SCN eggs were added to each microplot. In the 2018 trials, two nematode inoculum loads were prepared: 50,000 and 5,000 eggs/plot. In each experiment the eggs were aliquoted into 50ml tubes filled with tap water.

4.3.3 Bacteria preparation-microplots

Bacteria strains representing Pseudomonas spp., Bacillus sp., and Pantoea agglomerans were used in the microplot trials. Bacteria were collected previously by the Taylor laboratory

(Aly, 2009). Strains used in the microplot trials were selected based on activity in previous in vitro and greenhouse assays. (Figure 4.1). The bacteria used in this chapter are found in Table

4.1. Bacteria were applied in four possible ways: seed treatment, soil drench prepared with overnight culture, a combined seed treatment+drench (overnight culture), and mock bioreactors

(similar to the 3Bar Biologics Inc. bacterial delivery system). In the three microplot experiments each treatment had 20 replicates and organized in a randomized complete block design using

ARM software (Gylling Data Management, Inc, SD). Bacteria were grown overnight

(~200RPM, 28-30°C) in Tryptic Soy Broth (TSB) before dilution to OD600 1-1.2 and preparation of treatments. Bacteria were tested individually and in consortia. The two consortia we worked with were designated as PS4: MBSA-3BB1, 38D7, 38D4, and 39A2; and PS5: MBSA-3BB1,

Wood1B, 88A6, 36G2, and 38D4. PS4 is composed of bacteria from three species

(Pseudomonas brassicacearum, P. frederiksbergensis, and Pantoea agglomerans). PS5 is composed of bacteria from five species (P. brassicacearum, P. fluorescens, P. rhodesiae,

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Pantoea agglomerans, and Bacillus sp.) Specific treatment information for the 2017 and 2018 microplot trials can be found in Tables 2 and 3. Clean TSB (no bacteria) was used as a negative control.

Seed treatments used in the microplots were prepared by adding 8ml of bacteria culture or TSB per 250 seeds. The TSB-treated seed was used as a negative control. The seeds were mixed to allow the bacteria suspension to coat each seed. The seeds were air dried before planting. If seeds were not used the same day as treatment preparation, they were stored overnight in a cold room.

In 2017, drench treatments were prepared by adding bacteria culture (30, 60, 120, or

150ml depending on treatment) to 12 liters of deionized water and 500ml of suspension was added to a plot (Table 4.2). Likewise, in 2018, drench treatments were prepared by adding bacteria culture (30,60,120, or 150ml depending on treatment) to 6 liters of deionized water, and

250ml was added to a plot (Table 4.3). Bacteria were diluted to the same concentration (OD600 1-

1.2) regardless of the volume of bacteria added to the treatment. In the 2018 trials, mock bioreactors were also prepared as drench treatments. The two consortia and TSB (controls) were the only bioreactor treatments prepared. Except for the bacteria cultures and growth medium, material for the bioreactors was provided by the company. Bacteria or TSB were added at a rate of 0.1ml/gram autoclaved ground soybean. The bacteria in the bioreactors was not diluted to a specific concentration, rather overnight culture was used. The soybeans were mixed well to evenly coat the bacteria and allowed to dry for 20 minutes in the laminar flow hood. Six grams of the ground soybean+bacteria were added to 2 liters of water in jugs. The water and jugs were not sterile. The mixture was closed, shaken, and sat at ambient temperature for 3 days, after which 30ml of culture from the bioreactors were added to 6 liters of deionized water (Table 4.3).

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4.3.4 Microplot setup and yield measurements

Trials were conducted at Snyder Farm (OARDC-OSU) in Wooster, OH. Microplots consisting of PVC pipe (10-inch diameter X 12-inch deep) were set up in rows of 60, with each plot spaced approximately two feet apart. In this setup, individual plots were kept separate from each other with minimum possibility of crossover between the plots (Figure 4.2). In the 2018 trial, the two nematode inoculum levels (50,000 and 5,000 eggs) were tested side by side in two separate experiments, rather than combining all plots into one large experiment. At the beginning of each field season, soil from the previous year was removed and fresh topsoil (Rock Shop,

Wooster, OH) was added to fill the plots. Seed was planted in the microplots in mid-June. In every microplot experiment 10 soybeans were planted; seedlings were thinned to approximately five to seven plants/plot prior to the inoculation of bacteria drench treatments. In rare instances, a plot was overlooked and had more than five to seven plants. Bacteria were added on either the day of planting as a seed treatment or as a drench treatment approximately three weeks after planting. In both years, all seed was planted on the same day. Two to three days after bacteria were applied as a drench, SCN eggs were added to the soil. Four to five holes (approximately three to five inches deep) were made in the microplots and then eggs were added by gently shaking the tubes to resuspend eggs and pouring into the holes. Regular plot maintenance was done as needed through the summer with watering and weeding by hand. The herbicide

Roundup® (Bayer) was also applied to control the weeds, with careful avoidance of the soybeans in the microplots. Approximately four months after nematode inoculation, the plants were harvested for yield, and soil samples were taken for determination of nematode infestation in the plots. At this time with a few exceptions all microplots had complete senescence of plants. Soil samples were taken with probes to an approximate 12-inch depth, however the depth of each

163 core varied. Multiple cores were taken from each plot, collected in one gallon bags, and homogenized by mixing by hand. Soil samples were stored in a cold room until further processing.

Soybeans were stored in a barn at Snyder Farm until threshing using a Wintersteiger LD350

(Wintersteiger Inc, Salt Lake City, UT) laboratory threshing machine. Threshed beans were further stored until yield measurements were taken.

4.3.5 Determination of SCN infestation of microplots

Nematodes were extracted from the homogenized soil using a four-funnel elutriator

(University of Georgia Instrument Shop, Georgia), which allows for collection of SCN cysts though washing with water and airflow. One hundred cubic centimeters (cc) of homogenized soil was used from each microplot. During a 5-minute run time, the cysts passed through a #30 sieve and were collected on a #60 or #80 sieve. Cysts were collected in 50ml tubes and store in the cold room until grinding to collect eggs. Cysts from the microplots were ground as described above, until no cysts remained in the uppermost sieve. Collected eggs were then stained using acid fuschin (1L solution: 3.5g acid fuschin, 250ml acetic acid, 750ml distilled H2O) by adding the eggs and the stain (between 1-1.5ml) to a 250ml glass beaker and bringing it to a boil in the microwave. Like the cysts, stained eggs were collected in 50ml tubes and stored in the cold room until further processing. The stained eggs were brought to a final volume of 200ml using tap water, after which two aliquots were taken for determination of eggs in a sample. A dissecting microscope was used to count the number of eggs in an aliquot. Only eggs, not hatched SCN juveniles nor empty eggshells were used to determine the number of nematodes in each sample.

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4.3.6 SCN greenhouse assay

In 2018 SCN greenhouse assays were performed to complement the microplot trials.

Bacteria and SCN juveniles were prepared similarly to how inoculum was prepared for the microplot trials. The same SCN population was use in both the microplot and greenhouse trials

Only bacteria drench treatments were tested in the greenhouse assays. Seed was sterilized with chlorine gas, germinated, and planted in a conetainer (107ml volume) filled with the all-purpose sand:Turface® mixture supplemented with Osmocote® (14:14:14 NPK) and planted in. Drench treatments were applied to approximately two and a half-week-old plants. Bacteria overnight culture (~200RPM, 28-30°C) was diluted to OD600 1-1.2 and further diluted 1:100 in ddH2O.

Twenty milliliters of bacterial suspension was added to each plant. Throughout the assay additional fertilizer (20:20:20 NPK) was added as needed. All treatments except for 36G2 and ddH2O were tested in two independent greenhouse assays. Three days after adding the bacteria

4,000 nematode eggs were added to each cone. Plants were organized in a randomized design.

Cysts were harvested from each plant four and a half weeks after nematode inoculation, which allowed for the inoculated juveniles to undergo one lifecycle. Cysts were collected as described above, with the four-funnel elutriator. Upon conclusion of the experiment, the number of cysts were counted, and root dry weight recorded. Root systems were dried at ambient temperature for approximately one month before weighing.

4.3.7 Data analysis

The microplot data was analyzed using a linear mixed model with the GLIMMIX procedure in SAS (SAS Institute, Cary, NC, USA), using block as a random effect and treatment as fixed effect. Before analysis, egg values were subject to a natural log (ln) transformation to

165 normalize data. Least square means for each treatment (eggs/100cc soil and soybean yield/plot) were determined, and differences between the treatments were analyzed. Correlation plots were constructed comparing yield and number of eggs. Differences between soybean yield in 2018

(50,000 eggs vs 5,000) eggs was determined with a t-test in SPSS (α=0.05). Due to the huge variation of values within the data we did not remove any outliers in any of the data set, however some treatments did have them.

Each greenhouse assay was analyzed separately and subject to ANOVA (α=0.05) to identify differences between the treatments. Box and whisker plots were generated to show the median and quartiles of each experiment. The greenhouse data was analyzed using SPSS.

4.4 Results

Microplot trials were performed in 2017 and 2018 to determine the effect bacteria inoculants have on soybean cyst nematode control and soybean yield increase. Few treatments in both studies had significance in either of these factors at the α=0.05 level. No bacteria were significantly different (lower SCN eggs/100cc soil and increased yield) compared to all negative controls across the three experiments. P-values are included in the comparison of every treatment with the TSB (Tryptic Soy Broth) negative control treatments (two controls in 2017 and three controls in 2018). Due to the wide range of p-values in our comparisons and the arbitrary nature of p-values, we were interested in those treatments with p≤0.2 as compared to the controls. This higher p-value cutoff allowed us to best visualize possible differences between the treatments.

Specific significance levels are detailed in the results of each microplot experiment.

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4.4.1 2017 microplot study

Summaries for the 2017 microplot study (75,000-egg load) are found in Tables 4.4 and

4.6. Average eggs/100cc soil ranged from 107916 (36G2-D) to 156737 (PS4-Full-D) and soybean yield/microplot (g) ranged from 151.3 (88A6-S) to 179.2 (88A6-MBSA-3BB1-D). This study had two controls, drench (D) and seed (S) treatment, which comparisons were made against (TSB-D and TSB-S). The control values were not significantly different from each other

(Table 4.6). In general, bacteria were not effective against SCN or as plant growth promoters in the 2017 microplot study. Five treatments had significantly fewer eggs/100cc than the TSB-S control: PS5-Full-D and Wood1B-D at p≤0.2; PS4 -1/4-D at p≤0.1; and 36G2-D and PS5-S at p≤0.05. Two treatments, 36G2-D and PS5-S had significantly fewer eggs/100cc soil than the

TSB-D control (p≤0.1). There no treatments with significantly higher yield compared to TSB-D.

Six bacterial treatments had significantly higher yield than TSB-S: 38D4-D, 88A6-D, and PS4-

ST (p≤0.2); and 36G2-D, MBSA-3BB1-D, and 88A6-MBSA-3BB1-D (p≤0.1). There was no correlation between eggs/100cc soil and soybean yield (Figure 4.3A), which shows some microplots had high egg counts and high yield, and others had high egg counts and low yield.

Only one treatment, 36G2-D, was effective in both reducing eggs/100cc soil (compared to both controls) and increasing yield (compared to just TSB-S). One commercial product,

Poncho®/VOTiVO® was tested in this trial, and neither eggs/100cc soil nor yield were significantly different from the controls.

4.4.2 2018 microplot study

Bacteria were ineffective against SCN or as plant growth promoters in the 2018 microplot study (50,000 and 5,000-egg load). Three controls were used for the comparisons

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(TSB-D, TSB-Bioreactor-D, and TSB-S). Unlike the other controls which were free from contamination after overnight growth, the TSB-Bioreactor had substantial microbe growth after the incubation period of 4 days (data not shown). The controls in both 2018 experiments had significant differences from each other in both eggs/100cc soil and soybean yield (Tables 4.7 and

4.8)

Experiment 1 (50,000-egg load)

Summaries for 2018 Experiment 1 (50,000-egg load) can be found in Tables 4.5A and

4.7. At the higher egg load, final egg counts ranged from 107650 (TSB-Bioreactor-D) to 139990 eggs/100cc soil (TSB-D). There was no significant reduction in in eggs/100cc soil between bacteria and any of the control treatments. The bioreactor control treatment (TSB-Bioreactor-D), which had the lowest end-of-season egg counts, had three treatments with significantly higher eggs/100cc soil (p≤0.2). Soybean yield (grams/microplot) ranged from 143.6g (PS4-Bioreactor-

D) to 179g (MBSA-3BB1-S). Multiple bacteria treatments caused an increase in soybean yield as compared to both TSB-D and TSB-S. The drench and seed treatment controls both had significantly lower yield (p<0.1) than the bioreactor control. There were multiple bacterial treatments which had significantly higher yield compared to both TSB-D and TSB-S: Wood3-D

(p≤0.2); PS5-S (TSB-D p≤0.1 and TSB-S p≤0.1); MBSA-3BB1-S (p<0.05); and PS4-D+S

(p≤0.2). PS5-Bioreactor-D also had significantly higher yield than TSB-S only (p≤0.2). No treatments had significantly higher yield than TSB-Bioreactor-D, however multiple treatments had significantly lower yield. MBSA-3BB1-S and PS5-S were the only treatments with higher soybean yields than TSB-Bioreactor-D. There was no correlation between eggs/100cc soil and soybean yield in 2018 Experiment 1 (Figure 4.3B).

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Experiment 2 (5,000 Egg Load)

Summaries for 2018 Experiment 2 can be found in Tables 4.5B and 4.8. At the reduced load of 5,000 egg/plot treatment average values for eggs/100cc soil ranged from 69680 (PS4-

Bioreactor-D) to 101080 (PS5-D+S). There were no significant reductions in eggs/100cc soil between by any treatments. Soybean yield averages ranged from 241.7g (TSB-Bioreactor-D) to

269.3g (TSB-S). The bioreactor control had significantly lower yield than the drench and seed treatment controls. No bacterial treatment had significantly higher yield than TSB-D or TSB-S, however multiple treatments caused significantly higher yield than the TSB-Bioreactor D (PS5-

Bioreactor-D, PS4-Bioreactor-D, and PS4-D (p≤0.2)). The other controls, TSB-D (p≤0.2) and

TSB-S (p≤0.1), had yields which were also significantly higher than the TSB-Bioreactor-D treatment. There was no correlation between eggs/100cc soil and soybean yield per microplot in

2018 Experiment 2 (Figure 43.C).

In the 2018 microplot experiments each treatment, regardless of significance compared to the control, had substantially higher yields in the lower-nematode inoculation experiment. When the yield data from each 2018 experiment was combined and compared (50,000 vs 5,000 eggs inoculated), the yield from the low nematode pressure experiment was significantly higher than the high nematode pressure experiment (p<.001) (Figure 4.4). This comparison was not made between the number of eggs at the end of the season because different individuals counted the

50,000 and 5,000 eggs inoculated experiments, which may have led to differences due to human error.

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4.4.3 SCN greenhouse assays

The data from each greenhouse assay is presented separately in box and whisker plots

(Figure 4.5). These plots demonstrate the large variation in an individual treatment to inhibit development of SCN cysts. The treatments were not significantly different from the TSB control in both greenhouse assays (Greenhouse Assay #1: cysts/plant and root weight p-values respectively 0.944 and 0.053; Greenhouse Assay #2: cysts/plant and root weight p-values respectively 0.591 and 0.765). While not shown, the data expressed as cysts/gram root (dry weight) was also not significantly different across any of the treatments in both greenhouse assays. The results from the greenhouse assays did not match the results from previous experiments conducted by Xiao-Yuan Tao (Figure 4.1, Christopher Taylor Laboratory, unpublished) or Aly (2009), which indicate the bacteria may be similarly varied in their ability to control SCN in the greenhouse as that observed in the microplot studies.

4.4 Discussion

Management of SCN is important. According to the University of Wisconsin Extension

(n.d.), an egg density of 1-500eggs/cc soil can result in 0-30% yield loss, while higher densities can experience increased degrees of loss. At any egg density nematodes will reproduce on the soybean though the season, but a higher initial density is detrimental to yield. At high enough nematode levels, yield will even be reduced on SCN-resistant varieties (UW Extension, n.d.).

When all data from our two 2018 microplot experiments (50,000- and 5,000-eggs inoculated/plot) were combined, yield from the lower egg load was significantly higher. Despite high nematode populations at the end of the season, we saw that the initial egg population had an impact on overall plant yield (Figure 4.4, Table 4.5).

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In the past decade multiple products have been developed and tested as biocontrol agents of soybean cyst nematode. Two of the products currently marketed as bio-nematicides of SCN are Poncho®/VOTiVO® (BASF) and Clariva® (Syngenta), both of which have demonstrated varied efficacy in SCN egg reduction and plant growth promotion in field trials. There are inconsistencies in the ability of both nematicides to control SCN to any extent. Nematode control with the products has ranged from significant to ineffective, in which the nematicides may even result in higher SCN populations compared to the controls. Yield in trials with the nematicides is similarly varied (Bissonnette et al, 2018; Ahmed et al, 2018; Musil et al, 2015; Staton &

Seamon, 2018; Yabwalo et al, 2019). Selection of soybean cultivar may play a role in bioproduct efficacy. While overall yield was lower between the susceptible and resistant cultivars, the magnitude of yield increase was greater in Clariva® treated SCN-susceptible seed than treated

SCN-resistant seed as compared to their respective controls (Yabwalo et al, 2019).

Limited information on the efficacy of the nematicides Aveo® and BioST® against SCN is available. In two years of small-scale field trials, Aveo® significantly increased soybean yield in 2018, but not in 2017, and did not significantly control nematode populations in either year

(Tylka, 2019). In studies with other nematode species, including Rotylenchulus reniformus

(reniform nematode) and Meloidodgyne incognita (root knot nematode, RKN), control of nematodes and plant growth promotion with the nematicides were similarly varied. An RKN study on soybean showed Aveo® EZ Nematicide to significantly decrease root galling but did not have an effect on yield (Faske et al, 2019). In many cases, both decreases in nematode infection severity or population and increases in plant yield, if present at all, were not significant (Emerson et al, 2019; Lawaju et al, 2019; Rondon et al, 2019). Dyer et al (2017a and 2017b) identified the beneficial activity of BioST® as dose dependent. The varied efficacy of these four bio-

171 nematicides has demonstrated the necessity to continue screening for additional microbes of interest with use as control agents of SCN. Our study investigated the potential for bacteria representative of three genera (Pseudomonas, Pantoea, and Bacillus) as control agents of SCN in a microplot setting. With the exception of Wood1B (Bacillus sp.), bacteria were screened by previous members of the Taylor Laboratory in in vitro and greenhouse experiments. The strains used in our microplot assays were selected based on efficacy in greenhouse trials. Five of the strains of the selected for the studies presented here significantly reduced the fecundity of soybean cyst nematode in preliminary greenhouse assays. These bacteria were varied in their ability to control the hatch rate of SCN eggs, which implies different modes of action for each bacterium in controlling nematode reduction on the plant (Figure 4.1).

Similar to many of the commercial product studies (described in the preceding paragraphs), efficacy of the Pseudomonas treatments was varied between the three microplot experiments. The two most promising treatments in the 2017 trial (36G2-D and PS5-S) had significantly lower end of season egg density than both controls, however, neither treatment had significantly higher soybean yield than both controls. The commercial product,

Poncho®/VOTiVO® , had no significant difference in SCN egg density compared to either control, and at p<0.2 yield was significantly lower compared to the TSB-D control. This lack of beneficial effect from Poncho®/VOTiVO® treated seed for both SCN inhibition and yield increase was similar to the results of Musil et al (2015).

The 2018 trials built off the 2017 trial, and we tested some of the more promising treatments seen in either nematode control or plant yield increase: 36G2-D, MBSA-3BB1-D, and the PS5 treatments. Due to interest in the consortia we also tested PS4 again. Efficacy of the treatments was varied between the 2018 experiments. Of the treatments that were tested in both

172 the 2017 and 2018 microplot trials, there was no clear pattern between the three microplot experiments to what the best treatments were. Bioactivity was varied among the experiments in regard to both SCN end-of-season counts and yield increase. For example, 36G2-D was significant in the 2017 trial in both SCN inhibition and yield increase but was not effective in either of the 2018 trials. In multiple-year small-scale field studies (small plot and strips) investigating the efficacy of Clariva®, Bissonnette et al (2018) saw similar inconsistencies with

SCN reproduction and yield; Clariva® significantly inhibited nematode reproduction in only the small plots in one year (all test sites combined/year), and significantly increased yield in only the strip plots in one year (all test sites combined/year). Select trial sites had significant differences, but when the data from all test sites was combined the overall impact was not significant

(Bissonnette et al, 2018). Across our three microplot experiments the seed treatment and drench controls were not statistically different, however the bioreactor-drench control varied from the other controls in the 2018 trials, which makes data comparison difficult. On the day of the bacteria drench, the bioreactor control had substantial microbial growth, while the other controls used clean tryptic soy broth, which could have affected the nematodes and yield. In an ideal scenario, the controls would all be statistically equivalent.

The evidence for the role of Pseudomonas in SCN control is varied. Pseudomonas naturally occurring in suppressive soil has been linked with SCN control in growth chamber assays. (Hamid et al, 2017; Hussain et al, 2018). Alternatively, Hu et al (2017) found

Pseudomonas was enriched in cysts collected from a suppressive soil fumigated with the biocide formaldehyde as compared to non-treated suppressive soil. Egg density was also higher in the formaldehyde treated soil, which implies that Pseudomonas enrichment was not associated with nematode control (Hu et al 2017).There are multiple reasons to consider why the bacteria

173 treatments did not consistently work well as biocontrol agents of SCN or plant growth promoters of inoculated soybean in either the greenhouse or microplots. If the bacteria we added could not colonize well, they might neither form a physical barrier to the root, nor reproduce efficiently and produce toxic secondary metabolites that could directly affect the nematode. Kloepper et al

(1992) identified bacteria isolated from the rhizosphere of multiple plant species that had bioactivity against SCN. Most of our bacteria were not originally isolated from the roots or rhizosphere of plants and may not be efficient colonizers of the system (Table 4.1). We did not monitor specific environmental conditions of our experiments; perhaps external factors including temperature and soil water content affected the activity and colonizing potential of the of the bacteria. In short-term assays, when bacteria were added as seed treatments or root dips, the upper portion of root systems were better colonized by pseudomonads (Bowers & Parke, 1993;

Davies & Whitbread, 1989; Schmidt et al, 2004). Bowers & Parke (1993) and Davies &

Whitbread (1989) saw that addition of water to the system from the top allowed the bacteria to travel and colonize farther down the root. It is possible bacteria in our system were unable to effectively travel down the length of the soybean root, and subsequently only a limited portion of the root was colonized and primed for protection against the nematodes. Additionally, while proteobacteria including Pseudomonas can survive in soil and colonize root systems, and act against pathogens at wide ranges of temperatures, multiple assays have shown optimal temperature for the bacteria can depend on the isolate (typically between 10 and 30°C, parameters included air and/or soil temperature measurements) (Bowers & Parke, 1993; Davies

& Whitbread, 1989; Pillay & Nowak, 1997; Schmidt et al, 2004; Seong et al, 1991). The soil temperatures may have been suboptimal for bacterial for colonization. However according to data obtained from the Ohio State College of Food, Agriculture, and Environmental Sciences

174 weather station in Wayne County, Ohio, the average air and soil (4” depth) temperature from

June 13-July 15, 2017 ranged respectively from 15.7°C (June 27) to 26°C (June 17), and 19.8°C

(June 27) to 24.7°C (June 17); from June 11 to July 15, 2018 average air temperatures ranged from 18.4°C (June 11) to 27.6°C (June 18), and soil temperatures from 20°C (June 12) to 26°C

(July 2, 4, and 5) (https://www.oardc.ohio-state.edu/weather1/). The beginning date in each year is the day seed were planted, and July 15 is 12 days after the soil drenches were applied. In each case, the average minimum and maximum for both air and soil temperature were in the aforementioned range of optimal bacteria colonization, although it is possible our strains were more sensitive to higher temperature. The temperature ranges in the soil were in a range appropriate for SCN egg hatching, and it is possible that if the bacteria could not colonize the soybean efficiently and the nematodes had a high hatch rate, limited nematode control would occur (Tefft et al, 1982). More specific assays may need to be done with the most promising strains to establish their colonizing potential in the soil and root systems. The variation between our greenhouse assays and those performed previously by member of the Taylor Lab may be due to differences including selection of bacteria growth medium, soybean cultivar, seasonal timing of experiments, temperature of the greenhouse, and nematode population used (Figure 4.1 and

Aly, 2009). However, for a biocontrol agent, factors such as these should have limited effects on its overall activity for it to be considered effective.

The number of nematodes in the system could also play a factor in biocontrol and plant growth promoting activity. In our low nematode-load experiment, when comparing the controls to other treatments, the TSB drench and seed treatments had higher yields. One possible explanation for this is microbiome alteration. While very dilute, the addition of TSB to the microplots could have provided a boost for plant growth promoting rhizobacteria already present

175 in the topsoil. Bacteria inoculants can alter the soil microbiome, and if beneficial microbes were already present in the soil they could have been outcompeted by our inoculants, which could lead to less of an effect in the treatment plots (Schmidt et al 2014; Deng et al, 2019). We do not have an explanation why this effect was not seen in similar experiments with higher nematode pressure. In both the greenhouse and microplot experiments it is also possible not enough replicates were used. Due to the high variation in the treatments, more replicates could help reduce experimental noise.

4.5 Conclusions and Future Directions

While the treatments were not consistent between the microplot trials, further exploration can be taken with some of the more promising treatments. Multiple drench and seed treatment had significantly lower SCN egg densities or increased soybean yield as compared to the controls in at least one of the three experiments at the p<0.2, 0.1, and 0.05 levels. We are particularly interested in optimizing the treatments with significant yield increase. It is possible these two measures of control are not linked, and it is important to focus on the economically relevant measure. If a treatment reduces nematode reproduction without increasing yield compared to the controls, it is not an economical management strategy. We only tested 20 replicates/treatment, however due to the wide variation in both egg count and soybean yield, more replicates should be used in the future for each treatment. Because SCN is a field pathogen, future work should go into optimizing the bacteria for use in the microplots and field trials, rather than optimization in the greenhouse setting. Due to the inconsistent results of the controls in the 2018 50,000- and

5,000-egg load experiments, which were set up at the same time using the same materials, additional studies should go into determining the role nematode pressure has on the effectiveness

176 of biocontrol treatments and the possible role spiking the soil with nutrients can have on biocontrol potential.

We acknowledge Wanderson Bucker Moraes (The Ohio State Department of Plant Pathology) for his help with the statistical analysis for the microplot data and Leslie Taylor, Therese Miller, and Edwin Daniel Navarro Monserrat for their assistance in processing and counting the nematodes.

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Figure 4.1. SCN hatch rate and fecundity assay for a collection of Pseudomonas spp. strains. The preliminary data presented here was collected by Xiao-Yuan Tao (Chris Taylor Laboratory) and is the basis of the studies done in this chapter. A) shows the relative hatch rate for H. glycines eggs exposed to bacteria culture as compared to the water control (CK). GI-GIV indicates grouping based on hatch activity; B) shows the relative control of SCN in greenhouse assays as compared to the LB control (CK). In these assays bacteria were cultured in LB medium, and SCN-susceptible Glycine max ‘Hutcheson’ and H. glycines population Wood (HG 1,2,57) were used. Statistical significance was determined with the non- parametric Wilcoxon signed-rank test (* p<0.05; **p<0.01).

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A

B C

Figure 4.2 Microplot setup. Trials were held at Snyder Farm (OARDC, Wooster OH). A) shows the experimental setup at the beginning of the season, B) plot in the middle of the season, and C) plots before soybean harvest. Plots were spaced out so that there was minimal risk of cross contamination between each plot.

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2017 (75,000 eggs) 300

250

200

150

100 Soybean Weight (g)

50 y = -0.0001x + 182.3 R² = 0.0229 0 0 50000 100000 150000 200000 250000 300000 350000 400000 Eggs/100cc soil

2018 (50,000 eggs) 350

300

250

200

150

Soybean Weight (g) 100

50 y = 5E-05x + 155.35 R² = 0.0025 0 0 50000 100000 150000 200000 250000 300000 350000 400000 Eggs/100cc soil

Figure 4.3. Correlation between eggs/100 cubic-centimeters soil and soybean yield in microplot trials. Data for A) 2017 and B, C) 2018 field experiments. The data from every microplot was plotted and a linear trendline was established based on y=mx+b. (Figure 4.3 Continued)

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Figure 4.3 (continued).

2018 (5,000 eggs) 450

400

350

300

250

200 Soybean (g) 150

100

50 y = -0.0003x + 286.31 R² = 0.1014 0 0 50000 100000 150000 200000 250000 300000 350000 400000 Eggs/100cc soil

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Figure 4.4. Yield comparison between egg load in 2018 microplot study. Data from all treatments were combined (n=300 (50,000 eggs) and 293 (5,000 eggs)) and compared with a 2-sample T-test (***p<0.001). Mean±standard error shown.

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Figure 4.5. Box and whisker plots of SCN greenhouse assays. The Pseudomonas tested in the field were also tested in greenhouse assays. – represents the median. All treatments except for H2O and 36G2 were tested in two independent greenhouse assays; these treatments were tested once. The results from each assay are shown separately with A) Greenhouse Assay #1 and B) Greenhouse Assay #2. n=10 for each treatment. ANOVA was performed on each data and no treatments were significantly different (Experiment 1 and 2 ANOVA p-value >0.20). (Figure 4.5 continued)

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Figure 4.5 (continued).

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Table 4.1. Bacteria strains used in microplot and greenhouse experiments.

Strain Species Source Wood3 Pseudomonas brassicacearum Ohio soil (corn rhizosphere) 38D7-1 Pseudomonas frederiksbergensis Wyoming soil 39A2 Pseudomonas frederiksbergensis Wyoming soil 38D4 Pseudomonas brassicacearum Wyoming soil 36G2 Pseudomonas fluorescens Wyoming soil 88A6 Pseudomonas rhodesiae Missouri soil Wood1B Bacillus sp. Unknown MBSA-3BB1 Pantoea Agglomerans Unknown

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Table 4.2. Bacteria treatments used in 2017 microplot study. Bacteria were tested in the microplots as control agents of the Soybean Cyst Nematode. PS4: Pantoea agglomerans MBSA-3BB1, P. brassicacearum 38D4, P. brassicacearum 38D7, P. frederiksbergensis 39A2; PS5: Pantoea agglomerans MBSA-3BB1, Bacillus sp. Wood1B, P. brassicacearum 38D4, P. fluorescens 36G2, P. rhodesiae 88A6. DI= deionized water.

2017 Microplot Study Treatment Treatment Type Preparation of Bacteria Treatment

MBSA-3BB1-D Drench 30ml in 12L DI water

38D4-D Drench 30ml in 12L DI water 36G2 -D Drench 30ml in 12L DI water 88A6-D Drench 30ml in 12L DI water Wood1B-D Drench 30ml in 12L DI water Wood3-D Drench 30ml in 12L DI water 38D7-D Drench 30ml in 12L DI water 39A2-D Drench 30ml in 12L DI water PS4-1/4-D Drench 30ml (7.5ml of each bacteria) in 12L DI water PS4-Full-D Drench 120ml (30ml of each bacteria) in 12L DI water PS5-1/5-D Drench 30ml (6ml of each bacteria) in 12L DI water PS5-Full-D Drench 150ml (30ml of each bacteria) in 12L DI water

88A6+MBSA-3BB1-D Drench 60ml (30ml of each bacteria) in 12L DI water

TSB-D Drench 30ml TSB in 12L DI water

MBSA-3BB1-S Seed Treatment 8ml/250 seed 88A6-S Seed Treatment 8ml/250 seed Wood3-S Seed Treatment 8ml/250 seed PS4-S Seed Treatment 8ml (2ml of each bacterium)/250 seed PS5-S Seed Treatment 8ml (1.6 ml of each bacterium)/250 seed TSB-S Seed Treatment 8ml/250 seed Poncho®/ VOTiVO® Seed Treatment 0.26mg/seed

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Table 4.3. Bacteria treatments used in 2018 microplot study. Bacteria were tested in the microplots as control agents of the Soybean Cyst Nematode. PS4: Pantoea agglomerans MBSA-3BB1, P. brassicacearum 38D4, P. brassicacearum 38D7, P. frederiksbergensis 39A2; PS5: Pantoea agglomerans MBSA-3BB1, Bacillus sp. Wood1B, P. brassicacearum 38D4, P. fluorescens 36G2, P. rhodesiae 88A6. DI= deionized water.

2018 Microplot Studya Treatment Treatment Type Preparation of Bacteria Treatment PS5-D Drench 150ml (30ml of each bacterium) in 6L DI water PS4-D Drench 120ml (30ml of each bacterium) in 6L DI water MBSA-3BB1-D Drench 30ml in 6L DI water Wood3-D Drench 30ml in 6L DI water 36G2-D Drench 30ml in 6L DI water TSB-D Drench 30ml in 6L DI water PS5-Bioreactor-D Drench 30ml in 6L DI water PS4-Bioreactor-D Drench 30ml in 6L DI water TSB-Bioreactor-D Drench 30ml in 6L DI water PS5-S Seed Treatment 8ml (1.6 ml of each bacterium)/250 seed PS4-S Seed Treatment 8ml (2ml of each bacterium)/250 seed MBSA-3BB1-S Seed Treatment 8ml/250 seed TSB-S Seed Treatment 8ml/250 seed Drench+ 8ml (1.6 ml of each bacterium)/250 seed + PS5-S+D Seed Treatment 150ml (30ml of each bacterium) in 6L DI water Drench+ 8ml (2ml of each bacterium)/250 seed + PS4-S+D Seed Treatment 120ml (30ml of each bacterium) in 6L DI water aTreatments are the same for both nematode inoculum loads (50,000 eggs/plot and 5,000 eggs/plot)

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Table 4.4. 2017 microplot summary. Eggs/100cc soil and soybean weight (g) in microplots inoculated with 75,000 SCN eggs. Egg/100cc soil data were log transformed and analyzed using a linear mixed model with T-grouping for least square means (α=0.05). Soybean weights were not transformed and subjected to the same analysis. Treatments with the same letter are not significantly different. n=18- 20/treatment. Shading is done according to treatment type. D indicates drench treatments and S indicates seed treatments.

Eggs/100cc Soil Soybean Yield (g)

Standard Standard Treatment Average Average Error Error TSB-D 145663 15353 171.3 7.6 36G2-D 107916 9509 178.1 8.8 38D4-D 129895 8301 175.0 8.4 38D7-D 142240 9718 167.6 10.0 39A2-D 136820 11564 165.3 6.7 88A6-D 143222 13504 176.3 12.2 MBSA-3BB1-D 133160 11422 179.1 7.7 Wood1B-D 127060 10807 165.6 9.9 Wood3-D 126160 8931 164.5 8.8 88A6+MBSA-3BB1-D 134860 11407 179.2 8.6 PS4-1/4-D 126620 13477 164.2 10.5 PS4-Full-D 156737 14698 164.8 8.6 PS5-1/5-D 146400 14170 164.6 7.0 PS5-Full-D 127520 11020 166.5 7.6 TSB-S 147940 10876 158.8 6.1 88A6-S 141979 12935 151.3 9.8 MBSA-3BB1-S 134380 10449 168.2 8.4 Wood3-S 144460 11927 168.1 7.1 PS4-S 140820 16312 174.6 7.2 PS5-S 110240 9440 163.7 9.6 Poncho®/ VOTiVO® 144840 11890 153.0 9.3

192

Table 4.5. 2018 microplot summary. Eggs/100cc soil and soybean weight (g) in microplots inoculated with A) 50,000 and B) 5,000 SCN eggs. Egg/100cc soil data were log transformed and analyzed using a linear mixed model with T-grouping for least square means (α=0.05). Soybean weights were not transformed and subjected to the same analysis. Treatments with the same letter are not significantly different. n=17-20/treatment. Shading is done according to treatment type. D indicates drench treatments and S indicates seed treatments.

A Eggs/100cc soil Soybean Yield (g)

Standard Standard Treatment ID Average Average Error Error TSB-D 139990 19180 147.1 13.3 PS5-D 121190 12336 162.7 12.3 PS4-D 116440 10447 158.8 10.7 MBSA-3BB1-D 118730 12026 157.6 12.0 Wood3-D 134980 14488 169.1 13.1 36G2-D 130550 15749 162.6 13.5 TSB-Bioreactor-D 107650 12254 173.8 15.2 PS5-Bioreactor-D 114090 12158 164.8 11.9 PS4-Bioreactor-D 116480 12215 143.6 11.1 TSB-S 117630 12415 144.6 10.0 PS5-S 124980 10638 176.2 14.1 PS4-S 111830 12145 144.3 12.3 MBSA-3BB1S 112800 6936 179.0 10.0 PS5-D+S 125090 13514 162.3 11.2 PS4-D+S 136960 16924 169.3 11.0

(Table 4.5 continued)

193

Table 4.5 (continued).

B Eggs/100cc soil Soybean Yield (g)

Standard Standard Treatment ID Average Average Error Error TSB-D 84940 10501 267.3 17.1 PS5-D 94118 12138 257.2 18.2 PS4-D 73200 11699 265.9 16.3 MBSA-3BB1-D 92880 11546 254.7 15.4 Wood3-D 72042 10675 258.2 12.1 36G2-D 83920 19138 252.3 15.5 TSB-Bioreactor-D 92842 15097 241.7 11.7 P5S-Bioreactor-D 87280 10752 268.1 12.2 PS4-Bioreactor-D 69680 8721 266.2 7.8 TSB-S 92042 12994 269.3 11.3 PS5-S 75880 10648 254.2 10.8 PS4-S 92460 13667 242.8 11.8 MBSA-3BB1-S 93720 11598 260.5 12.3 PS5-D+S 101080 18099 255.2 12.5 PS4-D+S 99916 15330 259.1 14.1

194

Table 4.6. Statistical differences between 2017 SCN microplot treatments-75,000 egg inoculum. A) shows differences between eggs/100cc soil and B) soybean yield. The egg values were ln transformed before subject to analysis. Least square (LS) means were determined for each treatment Comparisons include differences between the calculated LS means (D), standard error of the LS means(DSE), 95% confidence intervals surrounding D (CIL and CIU), and significance between the treatments (P). Significant differences at p<0.2 are in red, p<0.1 in green, and p<0.05 in blue. Shading is done according to treatment type. D indicates drench treatments and S indicates seed treatments.

A TSB-D TSB-S

Treatment D DSE CIL CIU P D DSE CIL CIU P MBSA-3BB1-D -0.05 0.13 -0.29 0.20 0.710 -0.12 0.12 -0.37 0.12 0.321 38D4-D -0.04 0.13 -0.29 0.21 0.773 -0.11 0.13 -0.36 0.13 0.368 36G2-D -0.24 0.13 -0.49 0.01 0.060 -0.32 0.13 -0.56 -0.07 0.012 88A6-D 0.03 0.13 -0.22 0.29 0.788 -0.04 0.13 -0.29 0.21 0.743 Wood1B-D -0.09 0.13 -0.34 0.16 0.472 -0.17 0.12 -0.41 0.08 0.179 Wood3-D -0.07 0.13 -0.32 0.18 0.585 -0.15 0.12 -0.39 0.10 0.242 38D7-D 0.05 0.13 -0.20 0.30 0.693 -0.03 0.12 -0.27 0.22 0.828 39A2-D -0.03 0.13 -0.27 0.22 0.828 -0.10 0.12 -0.35 0.14 0.403 PS4 -1/4-D -0.15 0.13 -0.40 0.10 0.234 -0.23 0.12 -0.47 0.02 0.069 PS4-Full-D 0.10 0.13 -0.15 0.35 0.417 0.03 0.13 -0.22 0.27 0.830 PS5-1/5-D 0.04 0.13 -0.21 0.28 0.779 -0.04 0.12 -0.28 0.20 0.739 PS5-Full-D -0.09 0.13 -0.33 0.16 0.484 -0.16 0.12 -0.41 0.08 0.185 88A6+MBSA-3BB1-D -0.03 0.13 -0.28 0.22 0.802 -0.11 0.12 -0.35 0.14 0.383 TSB-D * * * * * -0.08 0.13 -0.32 0.17 0.543 MBSA-3BB1-S -0.02 0.13 -0.23 0.27 0.872 -0.10 0.12 -0.34 0.15 0.435 88A6-S 0.01 0.13 -0.26 0.24 0.947 -0.07 0.13 -0.31 0.18 0.588 Wood3-S 0.04 0.13 -0.29 0.21 0.742 -0.04 0.12 -0.28 0.21 0.777 PS4-S -0.02 0.13 -0.23 0.27 0.871 -0.10 0.12 -0.34 0.15 0.434 PS5-S -0.24 0.13 -0.01 0.48 0.061 -0.31 0.12 -0.56 -0.07 0.012 TSB-S 0.08 0.13 -0.32 0.17 0.543 * * * * * Poncho®/ VOTiVO® 0.03 0.13 -0.28 0.21 0.785 -0.04 0.12 -0.20 0.29 0.734

(Table 4.6 continued)

195

Table 4.6 (continued).

B TSB-D TSB-S

Treatment D DSE CIL CIU P D DSE CIL CIU P MBSA-3BB1-D 7.86 11.57 -14.90 30.62 0.498 20.25 11.42 -2.20 42.71 0.077 38D4-D 4.49 11.73 -18.57 27.55 0.702 16.89 11.57 -5.87 39.65 0.145 36G2-D 6.78 11.73 -16.28 29.84 0.564 19.17 11.57 -3.58 41.93 0.098 88A6-D 4.66 11.90 -18.73 28.05 0.695 17.06 11.74 -6.03 40.15 0.147 Wood1B-D -5.56 11.57 -28.32 17.20 0.631 6.84 11.42 -15.62 29.29 0.550 Wood3-D -6.71 11.57 -29.47 16.05 0.563 5.69 11.42 -16.77 28.14 0.619 38D7-D -3.59 11.57 -26.34 19.17 0.757 8.81 11.42 -13.64 31.26 0.441 39A2-D -5.94 11.57 -28.70 16.82 0.608 6.46 11.42 -16.00 28.91 0.572 PS4-1/4-D -7.03 11.57 -29.79 15.73 0.544 5.36 11.42 -17.09 27.82 0.639 PS4-Full-D -6.48 11.73 -29.54 16.58 0.581 5.91 11.57 -16.85 28.67 0.610 PS5-1/5-D -6.60 11.57 -29.36 16.15 0.569 5.79 11.42 -16.66 28.25 0.612 PS5_Full-D -4.72 11.57 -27.48 18.04 0.684 7.68 11.42 -14.78 30.13 0.502 88A6+MBSA-3BB1-D 7.95 11.57 -14.81 30.70 0.493 20.34 11.42 -2.11 42.80 0.076 TSB-D * * * * * 12.40 11.57 -10.36 35.15 0.285 MBSA-3BB1-S -2.99 11.57 -19.77 25.74 0.797 9.41 11.42 -13.04 31.86 0.410 88A6-S -20.21 11.73 -2.85 43.27 0.086 -7.81 11.57 -30.57 14.94 0.500 Wood3-S -3.06 11.57 -19.70 25.82 0.792 9.34 11.42 -13.12 31.79 0.414 PS4-ST 3.44 11.57 -26.20 19.31 0.766 15.84 11.42 -6.61 38.29 0.166 PS5-ST -7.53 11.57 -15.23 30.29 0.516 4.87 11.42 -17.59 27.32 0.670 TSB-S -12.40 11.57 -10.36 35.15 0.285 * * * * * Poncho®/ VOTiVO® -18.25 11.57 -4.51 41.00 0.116 -5.85 11.42 -16.60 28.30 0.609

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Table 4.7. Statistical differences between 2018 SCN microplot treatments-50,000 egg inoculum. A) shows differences between eggs/100cc soil and B) soybean yield. The egg values were ln transformed before subject to analysis. Least square (LS) means were determined for each treatment. Comparisons include differences between the calculated LS means (D), standard error of the LS means (DSE), 95% confidence intervals surrounding D (CIL and CIU), and significance between the treatments (P). Significant differences at p<0.2 are in red, p<0.1 in green, and p<0.05 in blue. Shading is done according to treatment types. D indicates drench treatments and S indicates seed treatments.

A TSB-D TSB-Bioreactor-D TSB-S

Treatment D DSE CIL CIU P D DSE CIL CIU P D DSE CIL CIU P PS5-D -0.06 0.14 -0.33 0.21 0.649 0.12 0.14 -0.15 0.39 0.390 0.05 0.14 -0.22 0.32 0.700 PS4-D -0.07 0.14 -0.34 0.20 0.616 0.11 0.14 -0.16 0.38 0.416 0.05 0.14 -0.22 0.32 0.735 MBSA-3BB1-D -0.08 0.14 -0.35 0.19 0.579 0.11 0.14 -0.17 0.38 0.446 0.04 0.14 -0.23 0.31 0.775 Wood3-D 0.04 0.14 -0.23 0.32 0.745 0.23 0.14 -0.04 0.50 0.102 0.16 0.14 -0.11 0.43 0.244 36G2-D -0.02 0.14 -0.29 0.25 0.899 0.16 0.14 -0.11 0.44 0.235 0.10 0.14 -0.17 0.37 0.476 TSB-D * * * * * 0.18 0.14 -0.09 0.45 0.189 0.12 0.14 -0.16 0.39 0.401 PS5-Bioreactor-D -0.11 0.14 -0.16 0.39 0.407 0.07 0.14 -0.20 0.34 0.627 0.00 0.14 -0.27 0.27 0.991 PS4-Bioreactor-D -0.09 0.14 -0.18 0.37 0.497 0.09 0.14 -0.18 0.36 0.525 0.02 0.14 -0.25 0.29 0.873 TSB-Bioreactor-D -0.18 0.14 -0.09 0.45 0.189 * * * * * -0.07 0.14 -0.34 0.21 0.635 PS5-S 0.00 0.14 -0.27 0.27 0.983 0.18 0.14 -0.45 0.09 0.196 0.11 0.14 -0.16 0.38 0.413 PS4-S -0.16 0.14 -0.11 0.44 0.235 0.02 0.14 -0.29 0.25 0.899 -0.05 0.14 -0.32 0.22 0.728 MBSA-3BB1-S -0.07 0.14 -0.20 0.34 0.614 0.11 0.14 -0.38 0.16 0.417 0.05 0.14 -0.23 0.32 0.736 TSB-S -0.12 0.14 -0.16 0.39 0.401 0.07 0.14 -0.34 0.21 0.635 * * * * * PS5-D+S -0.03 0.14 -0.24 0.30 0.832 0.15 0.14 -0.42 0.12 0.270 0.09 0.14 -0.36 0.18 0.530 PS4-D+S 0.02 0.14 -0.29 0.25 0.883 0.20 0.14 -0.47 0.07 0.144 0.14 0.14 -0.41 0.14 0.324

(Table 4.7 continued)

197

Table 4.7 (continued).

B TSB-D TSB-Bioreactor-D TSB-S

Treatment D DSE CIL CIU P D DSE CIL CIU P D DSE CIL CIU P PS5-D 15.59 15.19 -14.33 45.50 0.306 -11.08 15.19 -40.99 18.84 0.467 18.09 15.19 -11.83 48.00 0.235 PS4-D 11.67 15.19 -18.25 41.58 0.443 -15.00 15.19 -44.91 14.92 0.325 14.17 15.19 -15.75 44.08 0.352 MBSA-3BB1-D 10.44 15.19 -19.47 40.35 0.493 -16.22 15.19 -46.14 13.69 0.287 12.94 15.19 -16.97 42.85 0.395 Wood3-D 22.02 15.19 -7.90 51.93 0.149 -4.65 15.19 -34.56 25.27 0.760 24.52 15.19 -5.40 54.43 0.108 36G2-D 15.53 15.19 -14.38 45.44 0.308 -11.13 15.19 -41.05 18.78 0.464 18.03 15.19 -11.88 47.94 0.236 TSB-D * * * * * -26.66 15.19 -56.58 3.25 0.080 2.50 15.19 -27.41 32.41 0.870 PS5-Bioreactor D 17.65 15.19 -47.57 12.26 0.246 -9.01 15.19 -38.93 20.90 0.554 20.15 15.19 -9.76 50.06 0.186 PS4_Bioreactor-D -3.52 15.19 -26.40 33.43 0.817 -30.18 15.19 -60.10 -0.27 0.048 -1.02 15.19 -30.93 28.89 0.947 TSB-Bioreactor-D 26.66 15.19 -56.58 3.25 0.080 * * * * * 29.16 15.19 -0.75 59.08 0.056 PS5-S 29.05 15.19 -58.96 0.87 0.057 2.38 15.19 -32.30 27.53 0.876 31.55 15.19 1.63 61.46 0.039 PS4-S -2.81 15.19 -27.10 32.72 0.853 -29.47 15.19 -0.44 59.39 0.053 -0.31 15.19 -30.23 29.60 0.984 MBSA-3BB1-S 31.91 15.19 -61.82 -1.99 0.037 5.24 15.19 -35.16 24.67 0.730 34.41 15.19 4.49 64.32 0.024 TSB-S -2.50 15.19 -27.41 32.41 0.870 -29.16 15.19 -0.75 59.08 0.056 * * * * * PS5-D+S 15.22 15.19 -45.13 14.69 0.317 -11.44 15.19 -18.47 41.36 0.452 17.72 15.19 -47.63 12.20 0.245 PS4-D+S 22.23 15.19 -52.14 7.69 0.145 -4.44 15.19 -25.48 34.35 0.770 24.72 15.19 -54.64 5.19 0.105

198

Table 4.8. Statistical differences between 2018 SCN microplot treatments-5,000 egg inoculum. A) shows differences between eggs/100cc soil and B) soybean yield. The egg values were ln-transformed before subject to analysis. Least square (LS) means were determined for each treatment. Comparisons include differences between the calculated LS means (D), standard error of the LS means (DSE), 95% confidence intervals surrounding D (CIL and CIU), and significance between the treatments (P). Significant differences at p<0.2 are in red, p<0.1 in green, and p<0.05 in blue. Shading is done according to treatment types. D indicates drench treatments and S indicates seed treatments.

A TSB-D TSB-Bioreactor-D TSB-S

Treatment D DSE CIL CIU P D DSE CIL CIU P D DSE CIL CIU P PS5-D 0.09 0.26 -0.41 0.60 0.715 0.10 0.26 -0.41 0.61 0.704 0.08 0.26 -0.43 0.60 0.745 PS4-D -0.26 0.25 -0.75 0.23 0.304 -0.25 0.25 -0.75 0.25 0.320 -0.27 0.25 -0.77 0.23 0.293 MBSA-3BB1-D 0.05 0.25 -0.43 0.54 0.830 0.06 0.25 -0.43 0.55 0.816 0.04 0.25 -0.45 0.54 0.861 Wood3-D -0.21 0.25 -0.70 0.28 0.402 -0.20 0.25 -0.70 0.29 0.420 -0.22 0.25 -0.72 0.28 0.388 36G2-D -0.25 0.25 -0.73 0.24 0.316 -0.24 0.25 -0.74 0.25 0.332 -0.26 0.25 -0.75 0.24 0.305 TSB-D * * * * * 0.01 0.25 -0.49 0.50 0.984 -0.01 0.25 -0.50 0.48 0.970 PS5-Bioreactor-D -0.01 0.25 -0.48 0.49 0.981 0.00 0.25 -0.49 0.49 0.997 -0.02 0.25 -0.51 0.48 0.951 PS4-Bioreactor-D -0.23 0.25 -0.26 0.71 0.362 -0.22 0.25 -0.71 0.27 0.379 -0.23 0.25 -0.73 0.26 0.349 TSB-Bioreactor-D -0.01 0.25 -0.49 0.50 0.984 * * * * * -0.01 0.25 -0.51 0.48 0.955 PS5-S -0.25 0.25 -0.23 0.74 0.307 -0.25 0.25 -0.24 0.74 0.323 -0.26 0.25 -0.75 0.23 0.296 PS4-S -0.03 0.25 -0.46 0.52 0.900 -0.03 0.25 -0.47 0.52 0.918 -0.04 0.25 -0.53 0.45 0.872 MBSA-3BB1-S 0.05 0.25 -0.54 0.43 0.824 0.06 0.25 -0.55 0.43 0.811 0.05 0.25 -0.45 0.54 0.855 TSB-S 0.01 0.25 -0.50 0.48 0.970 0.01 0.25 -0.51 0.48 0.955 * * * * * PS5-D+S -0.02 0.25 -0.46 0.51 0.924 -0.02 0.25 -0.47 0.51 0.941 -0.03 0.25 -0.46 0.53 0.895 PS4-D+S 0.00 0.25 -0.49 0.49 0.996 0.01 0.25 -0.51 0.49 0.980 -0.01 0.25 -0.49 0.51 0.975

(Table 4.8 continued)

199

Table 4.8 (continued).

B TSBD TSB-Bioreactor-D TSB-S

Treatment D DSE CIL CIU P D DSE CIL CIU P D DSE CIL CIU P PS5-D -8.40 16.85 -41.57 24.78 0.619 17.02 17.07 -16.59 50.62 0.320 -10.55 17.07 -44.16 23.05 0.537 PS4-D -1.19 16.34 -33.36 30.97 0.942 24.22 16.56 -8.39 56.82 0.145 -3.35 16.53 -35.90 29.20 0.840 MBSA-3BB1-D -12.62 16.11 -44.35 19.10 0.434 12.79 16.34 -19.38 44.96 0.434 -14.78 16.34 -46.95 17.39 0.367 Wood3-D -7.69 16.33 -39.86 24.47 0.638 17.72 16.56 -14.88 50.32 0.285 -9.85 16.56 -42.45 22.76 0.553 36G2-D -14.95 16.11 -46.68 16.78 0.354 10.46 16.34 -21.71 42.63 0.522 -17.11 16.34 -49.27 15.06 0.296 TSB-D * * * * * 25.41 16.34 -6.75 57.58 0.121 -2.16 16.34 -34.32 30.01 0.895 PS5-Bioreactor-D 0.83 16.11 -32.55 30.90 0.959 26.24 16.34 -5.93 58.41 0.109 -1.33 16.34 -33.50 30.84 0.935 PS4-Bioreactor -D -1.08 16.11 -30.64 32.81 0.947 24.33 16.34 -7.84 56.50 0.138 -3.24 16.34 -35.41 28.93 0.843 TSB-Bioreactor-D -25.41 16.34 -6.75 57.58 0.121 * * * * * -27.57 16.56 -60.17 5.04 0.097 PS5-S -13.13 16.11 -18.59 44.86 0.416 12.28 16.34 -44.45 19.89 0.453 -15.29 16.34 -47.46 16.88 0.350 PS4-S -24.46 16.11 -7.27 56.19 0.130 0.95 16.34 -33.12 31.21 0.954 -26.62 16.34 -58.78 5.55 0.104 MBSA-3BB1-S -6.83 16.11 -24.90 38.55 0.672 18.59 16.34 -50.75 13.58 0.256 -8.98 16.34 -41.15 23.18 0.583 TSB-S 2.16 16.34 -34.32 30.01 0.895 27.57 16.56 -60.17 5.04 0.097 * * * * * PS5-D+S -12.04 16.11 -19.69 43.76 0.456 13.38 16.34 -45.54 18.79 0.414 -14.19 16.34 -17.97 46.36 0.386 PS4-D+S -7.96 16.34 -24.21 40.12 0.627 17.46 16.53 -50.01 15.09 0.292 -10.11 16.56 -22.49 42.72 0.542

200

Chapter 5:

Market Research on the Development of a Platform for Streamlined University-Industry

Collaboration in the Field of Microorganisms and Natural Products

201

5.1 Key Takeaways

1. Industry research expenditures are important sources of university income

2. There is no uniform method to identifying collaborators in university-industry

relationships

3. Companies utilize university resources for both goods (licensing of patentable and non-

patentable material) and research services

4. MO-NP@OSU proposes a matchmaking platform to facilitate the creation of university-

industry collaborations, particularly in the research fields of microorganisms and natural

products.

5.2 Introduction and Project Rationale

Success of a research institution can be determined by a variety of factors, including funding spent on research, faculty quality, and technology transfer or commercialization of research (McDevitt et al 2014; Rouse et al, 2018). Some primary categories of research funding into universities are federal and state grant dollars, non-profit funding, and funds from private industry. In 2018, institutions of higher education received 42.0 and 4.7 billion dollars (USD) respectively from the federal government and private businesses (Gibbons 2019). According to the AUTM STATT (Statistics Access for Technology Transfer) database, The Ohio State

University (OSU) had the 6th highest total research and development (R&D) expenditures, but the highest industry R&D expenditures, of the universities in the Big Ten Academic Conference in 2017 (Figure 5.1). Commercialization revenue of universities in the Big Ten varies widely. In

2017, the ratio of gross licensing income:total research expenditures at The Ohio State

University was 0.375, ranked 12/14 of the schools in the Big 10, and 123rd of over 180 universities with reported data to AUTM (Figure 5.2, Table 5.1) (AUTM STATT Database, n.d).

202

Due to the low level of licensing income generated at Ohio State compared to the other Big Ten universities, measures should be taken to increase this “return on research expenditure investment.” In addition, due to projected federal budget declines, OSU may need obtain an even greater amount of industry research expenditures to maintain, or increase, total research expenditures.

Both the United States Department of Agriculture (USDA) and the National Science

Foundation (NSF), two governmental organizations that fund projects in microbial and/or national products sciences, may experience substantial reduction (-8.4 and -7.2%1 respectively in their discretionary budgets in Fiscal Year 2021 (OMB, 2020). From FY2016 to FY2021, the amount of money requested for these organizations has was generally lower than the actual budget from the previous year; however, the enacted budgets were always higher than the requested budget (Table 5.2). Despite this, there is no guarantee that funding opportunities will increase for either agency. The Directorate for Biological Sciences of the National Science

Foundation (NSF-BIO), which provides over 65% of the federal funding for research in the life sciences at the academic institutions, funded almost 200 fewer research grant proposals in 2019 than in 2018 (NSF, 2019a; NSF, 2020). The Agriculture and Food Research Initiative (AFRI), the grant-funding leg of the USDA, was authorized to have an annual budget of up to $700 million in the 2018 Farm Bill (2018-2023). However, the actual AFRI budget for 2019 and 2020 was only $415 million (actual) and $425 million (enacted), respectively. Six-hundred million

(USD) was requested for AFRI in FY2021 but the true amount spent on agriculture research may differ than this requested amount ( USDA, 2020; USDA-NIFA, n.d.).

1 1 % change annual budget calculation: [(FY2-FY1)/FY1]*100

203

The budgets of NSF and USDA notwithstanding, the trend of federal government funding

R&D expenditures in higher education has changed over the past decade. Individual governmental agency expenditures (including Department of Energy, Department of Health and

Human Services, NSF, and USDA) may have risen over this period, however the federal government contribution to federal funding has decreased proportionally though the years. The proportion of federal (all agencies):total R&D expenditures was 62.5% in FY2011 and fell to

52.9% in FY2018. Over this period, the proportion of private industry:total expenditures increased from 4.9 to 5.9% (Gibbons, 2019). Industry research expenditures at OSU were 31%

($45.3 million) higher in 2017 than 2012 while federal research expenditures were 1.1% ($5.3 million) lower; 2017 saw the highest level of industry research expenditures at the university since 2007 (AUTM STATT Database, n.d.). Our team formed to investigate the increased potential of industry R&D expenditures in higher education, especially as federal expenditures decline. In 2019 we proposed the idea to create a platform to better connect industry and academia, which could ultimately generate revenue for the university, and went through an intensive market research program to fully craft a business model. Due to our areas of expertise, we chose to specifically focus on industry-academia connections within the research areas of microorganisms and natural products. Through the rest of this work, the team will be referred to as MO-NP@OSU (Microorganisms and Natural Products of Ohio State

University).

Since 2011 the National Science Foundation Innovation Corps (I-CORPS) training program has trained over 1300 teams of science and engineering researchers across the country to determine the commercial potential for their research (NSF, 2019b). Rather than introducing technology to the market and then learning if there is a customer base, the intent of I-CORPS is

204 to conduct market research before the product or idea hits the market. In 2015 the state of Ohio, funded by the Ohio Department of Education, created its own state-funded program (I-

CORPS@Ohio), modeled after the NSF I-CORPS). Since its inception, dozens of science and engineering teams have participated in the I-CORPS@Ohio program to test specific market hypotheses about a developed technology (Modlich, 2018).

Our project was initially based around the concept of unpatentable microorganisms.

Multiple United States Supreme Court rulings over the past century have focused on the patentability of microorganisms and DNA. Funk Brothers Seed Co. v. Kalo Inoculant Co. (1948) ruled that “works of nature,” which includes combinations of naturally occurring microorganisms, are not patentable. More recently in Association for Molecular Pathology v.

Myriad Genetics, Inc (2013), the United States Supreme Court held the ruling that “a naturally occurring DNA segment is a product of nature and not patent eligible merely because it has been isolated.” While microorganisms are not patentable, companies can still license them to develop a patentable product. At the offset of our I-CORPS@Ohio project we hypothesized that there is a need for an Ohio State University spin-off to license unpatentable microorganisms and natural products from the university and sub-license these organisms out to interested companies though better advertising (Figure 5.3). Through participating in interviews, we generated the additional hypothesis that there is a need to connect companies to academic researchers for collaboration on specific projects. We spent the entirety of the I-CORPS@Ohio program testing, validating or invalidating, and recrafting these hypotheses, and generating new hypotheses, which ultimately led to the creation of our final business model.

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5.3 Methodology

This project was conducted as part of the I-CORPS@Ohio entrepreneurship training program from April to August of 2019. In this program, teams performed market research for a business idea, and over the course of the training period continuously revised and updated the business concept based on the information gathered.

The MO-NP@OSU team was comprised of four graduate students from The Ohio State

University Department of Plant Pathology (Rebecca Kimmelfield, Ram Khadka, Daowen Huo, and Edwin Navarro), and five mentors from Ohio State and industry (Christopher Taylor, Shauna

Brummet, Jay Dahlman, Subbu Kumarappan, and Bruce Caldwell). The students conducted all interviews, generally in groups of two or three. Interviews typically lasted between 30 and 60 minutes and consisted of open-ended questions. Multiple questionnaires were created and used, depending on the interviewee segment. Approximately 100 interviews were conducted with individuals representing many fields including university faculty, industry, technology commercialization office or technology transfer office (TCO) officers, and university administration. The team also interviewed multiple organizations that operate similarly to the project we are proposing to help determine the logistical feasibility of the project. The similar organizations included university centers, nonprofit organizations, and for-profit companies.

Interview questions for faculty, industry, and TCO are found in Table 5.3. We did not have set questions for the organizations we interviewed that were similar to the entity we are proposing and university offices outside of TCO; rather we asked individuals from these segments to describe their organization and factors including successes, and difficulties in operation. Some of the TCO officer interviews were also conducted in this conversational format, without use of the standard questions.

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Similar to the evolution of the business concept, the questions evolved over the course of the interviews as the team determined what information was necessary to gather. Each broad question had additional sub-questions that could be asked if needed. Not every question was asked, as the answers tended to dictate the course of the interview. In this way, information could be gathered without asking in a leading or probing manner. In faculty, company, and some TCO interviews in order to prevent bias as much as possible, the I-CORPS project was not fully described until the conclusion of the interview, after which there was an additional period for the interviewee to provide feedback. In interviews with university administration, including some

TCO, and organizations similar in structure to the proposed MO-NP@OSU the I-CORPS project was explained before we asked questions, so the usefulness of the feedback was maximized. The interpretation of these questions is considered qualitative in nature.

The I-CORPS@Ohio process was largely focused on creation of the business model canvas (BMC, Figure 5.4) (Osterwalder & Pigneur, 2010). Information from the interviews was collated, and went into hypothesis generation, validation, or invalidation, on the BMC’s nine categories: Key Partners, Key Activities, Key Resources, Value Proposition, Customer

Relationships, Channels, Customer Segments, Cost Structure, and Revenue Streams. Each of these factors must be considered when making plants to start a business. The final iteration of the

BMC was used to develop our final business model.

5.4 Results and Discussion

In its current form, MO-NP@OSU is a proposed business-business that serves as a database where companies can find university-based goods and services related to microorganisms and natural products. University-industry (U-I) collaborations provide tangible

207 benefits to universities (including research funding, licensing income, opportunities for faculty and students) and companies (including research and development, access to knowledge, licensing of material), but we learned there is no single way of forming these connections

(Edmonson et al, 2012; Glenna et al, 2007; Lacy et al, 2014; Rybnicek & Königsgruber 2019).

MO-NP@OSU serves to simplify the industry search process for finding academic partnerships.

Over the course of the I-CORPS@Ohio project period, multiple iterations of the BMC were created (Figure 5.4). Initially we had three categories to test: value propositions (long term microbe storage, facilitating research between academia-industry, identifying university partners for companies, and alleviating the TCO workload), key partners (university administration); and customer segments (MO/NP companies, TCO officers, and professors at universities). The interviews conducted helped validate/invalidate the initial series of hypotheses. For the terms of the BMC, every item filled in (as a customer segment, key partner, revenue stream, etc.) was considered a business hypothesis (Osterwalder et al, 2014). The interviews we conducted helped dictate whether the business hypotheses were an integral part of the business model.

5.4.1 Interview summary

Interviews were conducted with individuals from 28 companies (worldwide) and 30 faculty from around the state of Ohio. Eight companies had two interviews (multiple individuals spoken with), and the remaining 20 had one interview from the company. Every company was entirely or partially focused on bioproducts using microorganism and/or natural products. The size of the companies ranged from 2-10 to over 10,000 employees. Of the companies we interviewed, 16 were small (0-100 employees), six were medium (101-1000 employees), and six were large (>1000 employees). Of the faculty interviewed, 18 were from the OSU College of

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Food, Agriculture, and Environmental Sciences, seven were from OSU Arts and Sciences, one was from the OSU College of Pharmacy, and four were from other research institutions across

Ohio.

There are multiple ways in which companies and universities collaborate, and there is no one way of identifying these collaborators. Companies were varied in their utilization of resources from universities. Companies sought out: research collaborations, contract research, field trials, and microbe/natural product licensing. Information regarding how companies utilize resources at universities/other external institutions regarding microorganisms and natural products can be found in Tables 5.4 and 5.5. Over ten strategies were mentioned by companies regarding how collaborators were identified. While we will not mention every method of how collaborators are identified, multiple strategies are described here. We have information on how collaborators were identified and/or formed for 20 of the 28 companies. Some common strategies include previous knowledge based on the company or personal network of the individuals interviewed (12), searching the literature (9), and networking at conferences (11). Additional strategies include companies working with 3rd parties (including IN-Part and the Biological

Products Industry Alliance), through TCO solicitations, website or TCO reaching out (5) use of a scientific advisory board (2). Some companies indicated that specific individuals were hired for the purpose of identifying collaborators. Collaborations were formed both by the company reaching out to universities and other collaborators, and collaborators reaching out to the company. The information presented in Tables 5.4 and 5.5 may not be complete, as it is based solely off the interviews we performed, and company operations may vary division to division.

Of the faculty interviewed 26 out of 30 have worked with companies in some capacity during their careers as faculty members at their institutions. Faculty both worked as research

209 partners with existing companies and began companies as entrepreneurs. One additional faculty member worked with industry as a graduate student. Of the faculty who have interacted with industry in any capacity, we have information on how collaborations were formed for 22 of them. The three most common ways for professors to form industry collaborations are though the company directly reaching out (13 professors), professional network/prior connections of the professor (6) or networking at conferences (6). An additional method used by some faculty in identifying industry collaborators is utilizing university offices and centers (for example, the

Industry Liaison Office at Ohio State University and the Ohio Bioproducts Innovation Center)

(2).

While many of the companies and faculty interviewed engage in successful university- industry (U-I) collaborations, there is room for improvement. Lacy et al (2014) and Glenna et al

(2007) identified multiple disadvantages to U-I collaborations perceived by university scientists and administrators and the industry community including conflicts of interest, restriction of communication, and inhibition of material transfer. Of the faculty we interviewed, problems with industry collaborators included difficulty in identifying and forming collaborations and a lack of company interest in acquiring technology. Multiple companies we interviewed expressed the potential for U-I partnerships to be improved by increasing the visibility and accessibility of university resources. Issues with universities include administrative hurdles, overvaluation and ownership of university material and research, and a disconnect in understanding project processes, and timelines. In order for U-I collaborations to have the most success, both players must demonstrate flexibility, honesty and clarity (Rybnicek & Königsgruber, 2019). These areas of improvement are challenging to incorporate into the model but must be considered to have sustained long-term partnerships between universities and industry. The information regarding

210 improvements in U-I relationships may not be complete as we interviewed a small subset of individuals, and opinions may differ from person-to-person, company-to-company, or within multiple divisions at a company.

A majority of the professors were interested in commercializing their research and were in various stages of the process including: submitted patents, interest in licensing out to interested parties, and optimizing research projects. Two faculty members started companies with their previous research. Of the faculty interviewed, 19 have worked with the Technology

Commercialization Office (TCO) in some capacity, either at their current or previous institution.

Multiple professors who indicated interest in commercialization of research had limited to no interaction with TCO. Multiple professors from Ohio State indicated that relationships with TCO have improved in recent years as the office has become more responsive and easier to work with.

We interviewed TCO officers from universities around the United States, university administrators at Ohio State, and for-profit and non-profit entities that have similar business models to the one that we are proposing. Similar business models included entities that: licensed out university generated/owned material, advertised university owned intellectual property, and facilitated connections between universities and industries. We are unable to quantify these interviews; however, we have qualitatively included points of interest from each category of interview (TCO, administrator, and similar business models) in Table 5.6. Multiple interviews offered advice and feedback on starting simple (one university to begin, focusing on either licensing microbes/natural products or facilitating research partnerships) and the importance of sufficient revenue streams. Multiple interviews brought up the point that standardizing licensing agreements and research contracts, could be a good idea but ultimately difficult to achieve. Of

211 the entities similar to what MO-NP@OSU is proposing, there was variation in whether the university or private industry was the customer base.

5.4.2 Business model canvas and business model: Hypotheses validation

The BMC was updated weekly, and three iterations are presented here; one from the early, middle, and end part of the interview process. The interviews performed each week were used to update the canvas. The final BMC was used to create our business model (Figures 5.4,

5.5). MO-NP@OSU, in its current iteration, is a proposed web platform to connect industry and academia for the purposes of developing research relationships and advertisement of non- patentable intellectual property (microorganisms and natural products). Companies developing products with microorganisms and/or natural products are the customers, and university personnel (faculty, offices of commercialization and research) are key partners. As it stands, the model is a work in progress. We used the information gathered from the interviews to test specific hypotheses, and additional information gathered may result in a modification of the model.

Iteration #1: Tested Business Hypotheses • Key Partners: university administration (including TCO) • Value Propositions: long term microbe storage; facilitating research between academia- industry; identifying university partners for companies; alleviating TCO workload • Customer Segments: Companies (Start-up and Large R&D), TCO officers, professors at universities working with MOs/NPs Insight Gained/Invalidated Hypotheses • Faculty, TCO are not customers; they are integral for the business model to succeed but are key players • Companies of different sizes have different needs and wants, and are distinct customer segments

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Iterations #2 and 3: The final BMC consists of all hypotheses that were not invalidated in BMC #2. Tested Business Hypotheses: • Key Partners: university administration (TCO); professors at member universities • Key activities: curate database of professors and associated expertise; curate list of MO/NPs with commercial relevance; build platform (website) for companies to access; license/option microbes of interest • Key Resources: venture capital funding; federal funding (if non-profit) • Value Propositions: long term storage of microbes off site from primary research; facilitating research partnership between academia-industry; faster time to get products to market; identifying academia-partners to conduct contract research for companies; alleviating responsibility of TCO to manage/forge relationships; identifying well characterized MOs/NPs • Customer Relationships: GET: attending conferences and tradeshows, free trial memberships for companies; KEEP: continuously updating information of interest for companies; GROW: satisfied customers and word of mouth • Channels: sub-licensing microorganisms and processes from partners; website with MO/NP information • Customer Segments: Product discovery and development divisions of companies (start- up, small, medium, and large) • Cost Structure: licensing microbes from partner universities; salaries (microbiologist, data scientist, contracts associate, in-house counsel) • Revenue Streams: Companies licensing microbes from MO-NP@OSU, membership fees, commission made on collaborations

Insight Gained/Invalidated Hypotheses: • Licensing is expensive and tied to university expectations • MO-NP@OSU needs to differentiate itself from the current market of science and technology matchmakers (see interview notes in Table 5.5) • Invalidated: o Licensing of MO/NPs from universities o Sublicensing of MO/NPs to companies o Long term storage of microbes o Facilitating projects/licenses will not alleviate TCO/TTO officer’s workload. ▪ TCO will still have to work with MO-NP@OSU

5.5 Conclusions and Future Directions

Through the I-CORPS@Ohio process we interviewed individuals from multiple categories including industry, academia-faculty researchers, academia-university administration, and entities similar to what MO-NP@OSU is proposing. Every company we interviewed

213 interacts with universities or other external organizations via licensing or research collaborations, and 27 of the 30 of the faculty interviewed have collaborated with industry in some capacity. We learned there is no uniform way of establishing university-industry collaborations. We built a model using the information gained for the interviews which proposes to more efficiently connect industry with academic collaborators. Future steps involve validating the model though quantitative interviews with academia and industry. Additional hypotheses to validate include revenue streams and the type of organization (for-profit, non-profit, or university center) and the possibility of establishing standard licensing/research contracts. Our team intends for MO-

NP@OSU to start at Ohio State University, and eventually expand to be a multi-institutional platform where companies doing work on microbe and natural products can find sufficient collaborators to fill their needs.

The data presented here results from a market research project performed in 2019 though I-

CORPS@Ohio. Four students from the department of Plant Pathology and Translational Plant

Sciences Graduate Program participated equally in the collection of the data. RBK led the team and analyzed the collated data. We acknowledge I-CORPS@Ohio for funding this project.

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References

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Figure 5.1. Total research expenditures versus industry research expenditures. Data represents university expenditure and income data from 2017, as reported to the AUTM STATT database (autm.net). To ease readability of the figure, specifically in viewing Ohio State, the axes were scaled so that institutions with the highest values were left out. The red dots represent The Ohio State University, yellow dots represent other schools in the Big 10, and black dots are other schools included in the STATT database.

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Figure 5.2. Research expenditures versus gross licensing income. Data represents university expenditure and income data from 2017, as reported to the AUTM STATT database (autm.net). To ease readability of the figure, specifically in viewing Ohio State, the axes were scaled so that institutions with the highest values were left out. The red dots represent The Ohio State University, yellow dots represent other schools in the Big 10, and black dots are other schools included in the STATT database.

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Figure 5.3. Business model initially proposed by MO-NP@OSU. The company would focus on licensing microorganisms and natural products from Ohio State University. All university transactions would take place though the TCO, and companies would work exclusively though MO- NP@OSU. TCO: technology commercialization office; R/L: royalties and licensing; IP: licensable intellectual property; Green dots indicate faculty members interested in working with this model and red dots indicated faculty not interested. The I-CORPS@Ohio process was spent testing and reformulating this model though interviews with faculty, TCO, industry, and other entities.

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A

Figure 5.4. Business model canvas (BMC) for I-CORPS@Ohio Project. A) reflects the earliest iteration of the canvas. The first set of interviews were performed with the idea of filling out the additional categories; B) reflects a middle iteration of the BMC, after updating with information from more interviews; C) reflects the final iteration of the BMC as of July 2019. This includes hypotheses that were invalidated due to the results of the interviews. The canvas was updated weekly on the Launchpad Central program (launchpadcentral.com) to reflect insights gained from interviews.

(Figure 5.4 continued).

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(Figure 5.4 continued). B

(Figure 5.4 continued).

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(Figure 5.4 continued). C

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Figure 5.5. Proposed business model for MO-NP@OSU. This model was developed using the data from the I-CORPS@Ohio interviews collected in 2019.

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Table 5.1. Ratio of gross licensing income to total research expenditures for Big Ten universities in 2017. Data obtained from AUTM STATT database. The GLI/TRE gives an indicator of return on investment of research expenditures.

Total Research Gross Licensing Expenditures (TRE) Income (GLI) Ratio Institution (millions of dollars, (millions of dollars, [GLI/TRE] USD) USD) Northwestern University 563.56 246.74 43.78 Rutgers (The State University of New 627.42 29.43 4.69 Jersey) University of Illinois Chicago Urbana 1036.78 31.14 3.00 University of Minnesota 948.35 22.94 2.42 University of Wisconsin- 1193.41 20.01 1.68 Madison/WARF Indiana University (IOC) 474.42 6.70 1.41 University of Michigan 1482.85 14.65 0.99 Purdue Research Foundation 662.51 5.13 0.77 Michigan State University 694.92 4.60 0.66 University of Nebraska 458.96 2.32 0.50 University of Iowa Research 451.24 1.83 0.41 Foundation The Ohio State University 864.33 3.24 0.37 University System of Maryland 1085.08 2.43 0.22 Penn State University 862.87 1.18 0.14

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Table 5.2. Federal budget information for the National Science Foundation and US Department of Agriculture from FY2016-FY2021. Budget information includes the amount allocated in the previous fiscal year (FY) to the federal organization (amounts are actual, enacted, or estimated by the Federal Government) and the requested budget for the coming fiscal year. Budget information was obtained from the United States Office of Management and Budget federal budget documents for FYs 2016-2021 (https://www.govinfo.gov/app/collection/BUDGET/).

Budget (billions of dollars, USD) %Change Actual/Enacted/Estimated Requested [(FY2-FY1)/FY1]*100 2015 (actual) 2016 7.3 7.7 5.48 2016 (enacted) 2017 7.5 7.6 1.3 2017 (enacted) 2018 National Science 7.5 6.7 -10.7 Foundation 2018 (estimated) 2019 7.4 5.3 -28.4 2019 (actual) 2020 8.1 7.1 -12.3 2020 (enacted) 2021 8.3 7.7 -7.2 2015 (actual) 2016 24.9 23.5 -5.6 2016 (enacted) 2017 25.2 23.4 -7.1 2017 (enacted) 2018 Department of 22.7 18 -20.7 Agriculture 2018 (estimated) 2019 22.5 19 -15.6 2019 (actual) 2020 24.4 20.8 -14.8 2020 (enacted) 2021 23.8 21.8 -8.4

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Table 5.3. Questions asked in I-CORPS@Ohio interviews. Broad questions are in bold. Not every question or sub-question was asked. Question asking was guided by the flow of the interview. This is a representative example of the questions, as they were modified over the course of the interview period as we received feedback from interviewees and mentors.

Interview Questions Segment 1. Can you give a brief overview/description of the research projects you are involved in? 1.1. What are your daily tasks as a faculty member at this institution and which of these tasks would you say consumes most of your time? 2. What is the driving motivation behind your research? 2.1. Do you think about how your microbes/natural products could be commercialized? 2.2. Do you share your microbes/natural products with other groups within/outside of the university? Please expand on these collaborations. 3. Do have any prior experience working with industry? Please describe the interactions. 3.1. If yes: how did you form the relationship with the companies? Academic (faculty) 3.2. Is there room to improve academic-industry relationships? How would your lab group benefit from improved relationships? 4. Are you aware of the TCO, and what the steps towards commercializing your university-owned research entail? How have you heard about TCO? 4.1. Have you felt that TCO was accessible to your lab? 4.2. Have you ever been involved in the licensing or commercialization of a product/organism developed in your lab? Why/why not? 4.2.1. If yes: what is the experience with TCO? Did you face any obstacles working with TCO? 4.2.2. If yes: do you have any suggestions to make the TCO process better 4.3. If interested in commercializing your microbes, would you feel comfortable working with a conduit that would connect academia to TCO to industry? 1. What type of work does your company focus on? How important is discovery within the company? What is your product discovery process? How do you feel about the discovery process? What could be better about it? 1.1. What competitive advantage do your microbes have? [this may be more applicable for companies that have their own discovery processes] 2. What limitations do you identify in new product development? 3. What are you looking for? Are you working on developing new microbes or natural products? Industry 3.1. Are you looking for microbes or services, or both? 3.2. If you work with microbes/natural products, how have you identified material to work on for your products and experiments? 3.3. Has your company had previous experience working with academia? 3.4. What are the processes and challenges you have experienced to obtain the microbes or natural products? 3.5. How have you formed your connections? 3.6. How have your experiences with TCO/TTO at universities been during the commercialization process?

(Table 5.3 Continued).

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(Table 5.3 Continued).

4. How can Universities make microbes more accessible to you? 4.1. What would you like to see in terms of information the university can make accessible to you? 4.2. How can university-industry relationships be improved? What would you like Industry to see? 4.3. Is there a disconnect between academia and industry? How can this gap be lessened? 4.4. What does a better relationship look like? 1. Can you give an overall overview of how TCO facilitates the translation of advanced research done at the university into the commercial realm? 1.1. What does your job entail? 1.2. What has been the experience of handling this process when it relates to agriculture? 1.3. What part of the process is most challenging? 1.4. Is there a typical relationship between faculty and TCO? 2. Do you find the office prioritizing some projects (products?) over others? 2.1. If so, how do you rank them? Does this lead to some products not getting the required attention? 3. How do TCO licensing professionals fill potential gaps in their scientific knowledge Technology when working on product details? Does the TCO work with any 3rd party Commercialization organizations to help facilitate product commercialization? Office 3.1. If yes, please describe what these relationships entail 3.2. If no, could you see this set-up being helpful in managing the workload? 4. How are your experiences working with agriculture company and faculties/researcher working in agriculture microorganisms and natural products? 5. Do you think the blanket licensing of microorganisms and natural products is feasible? 6. Is TCO at your university involved in any multi institutional arrangements? 6.1. Standardization of contracts/licenses 6.2. Commercial vs research projects 6.3. Efforts to market research done at the university? 6.4. Has your TCO worked with 3rd parties to facilitate licensing agreements? Is this possible?

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Table 5.4. Industry collaborations with universities and/or private research contract companies. Many of the companies we interviewed work with external parties in some capacity. The extent of the outsourcing varied from company to company. If collaborations were not mentioned as being currently done with universities, answers may include the nature of collaborations a company would like in the future.

Industry Collaborations Companies Outsourcing: Laboratory Research/Unspecified Collaborations Small/Startups (16 total) 13 Medium (6 total) 3 Large (6 total) 4 Companies Outsourcing: Field/Product Trials Small/Startups (16 total) 8 Medium (6 total) 3 Large (6 total) 1 Companies Outsourcing: Scientific Advisory Board/Consulting from Universities Small/Startups (16 total) 3 Medium (6 total) 0 Large (6 total) 0

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Table 5.5. Company sourcing for microorganisms and natural products. For our purposes, in-house discovery includes microbes that are publicly available, and do not need to be licensed from external sources. We do not have the microbe/NP sourcing information for one of the small/startup companies and information is incomplete for one of the medium companies.

Microbe/NP Microbe/NP Discovery: External Discovery: In House Open to All/ All/ Company Size Some Some outsourcing in Majority Majority the future Small/Startups (16 Total) 8 2 5 3 2 Medium (6 Total) 2 1 2 4 0 Large (6 Total) 2 1 3 2 0

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Table 5.6. Responses from technology commercialization officers, other university administration, and similar organization interview segments. In addition to the TCO, we interviewed individuals from offices at Ohio State including the Office of Sponsored Programs (OSP), the Industry Liaison Office (ILO), and the Corporate Engagement Office (CEO). We were unable to quantify the responses in these interviews and have instead included some qualitative points of interest and suggestions from each of these groups.

Interview Segment Points of Interest TCO (ten interviews • Projects within TCO are prioritized and marketed on the basis of from seven multiple factors including of likelihood of licensing/patenting, universities) marketability and funding within office • TCOs work with 3rd party organizations to market university IP; multiple TC officers mentioned working with a 3rd party on a case-by- case basis, dependent on individual ability to market technology • Standard licensing agreements across universities could be useful [for an institution serving multiple universities] but would be difficult and require a lot of effort to achieve. One TC officer felt standard licensing agreements are a gimmick • Licensing of microbes from universities could be done with exclusive or non-exclusive licensing, or optioning of the technology. Each type of licensing comes at a different price point. Licensing costs are not uniform across each microbe, and each university may have their own conditions. OSU Administration • MO-NP@OSU would not conflict with OSU policy (CEO) (nine individuals • MO-NP@OSU could help university stay up to date on general interest from seven levels of companies; many faculty do not work with companies due to interviews restrictive guidelines; faculty do not want to work with 3rd parties representing five regarding company relationships (ILO) offices) • MO-NP@OSU could work with the office to help establish research collaborations; Standard contracts across companies and universities for research projects may be difficult to achieve (OSP) Similar • Companies may not want to pay for a matchmaking service if a free Organizations (two alternative exists; the goals of the organization change with changes in stock centers from funding by grant proposals—MO-NP@OSU would have to consider this OSU, one university possibility; standard contracts across universities will be difficult to consortium, three achieve (non-profit) non-profits, six • Companies pay membership to join, influence what projects are companies) funded at university; companies have one point of contact rather than multiple faculty (university consortium) • Reduced federal funding is a challenge in keeping centers open; material used for research, not commercial purposes (stock centers) • MO-NP@OSU could occupy niches tangential to multiple, existing companies; important to determine demand in a niche market (companies)

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Chapter 6

Perspectives

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This work examined the concept and practice of biocontrol along multiple points of the basic science-applied science continuum, and each study helped paint a picture of the importance in selecting the proper biocontrol agent. To look at the field as broadly as possible, we start at

Chapter 5, in which university-industry collaboration were examined. In the realm of microorganisms and natural products product development, companies often collaborate with universities as research partners and license un-patentable microorganisms and natural products to further run though their pipelines and potentially develop into a product. Thus, the work that university researchers do on biocontrol, from basic laboratory science to field trials with promising microorganisms, has relevancy in the university-industry framework. Anecdotally, in multiple interviews conducted with individuals involved in research and development at companies developing bioproducts, we learned that the more information on a specific microorganism the better; when companies look to license material, they seek as much information about it as possible. The platform we proposed as a result of the I-CORPS@Ohio project is a more streamlined process to distribute this information and connect industry with faculty members. The projects investigated in Chapters 2 through 4 of this dissertation coincide with the industry thought of “the more information the better,” as a collection of Pseudomonas sp. and Pantoea agglomerans strains were investigated for biocontrol potential against several microorganisms (Fusarium oxysporum, Caenorhabditis elegans, and Heterodera Glycines, soybean cyst nematode) in a diverse series of assays.

The primary focus of Chapters 2 and 3 was to investigate modes of action of

Pseudomonas against other microorganisms. More specifically, we were interested in the role of volatile organic compounds (VOCs) in contributing to the biocontrol potential of pseudomonads.

Of the collection we screened against F. oxysporum and C. elegans in Chapter 2, a majority

232 produced VOCs that inhibited the growth and activity of selected microorganisms. We quantified the volatiles produced by the collection of bacteria using proton transfer reaction time-of-flight mass-spectrometry, an analytical tool that to the best of our knowledge has not previously been used to quantify the VOCs of Pseudomonas strains. The VOC profiling showed 39 compounds produced at quantities >1ppbv; some of which were correlated with Pseudomonas bioactivity.

Hydrogen cyanide (HCN) is an important contributor to Pseudomonas bioactivity both the fungus and nematode, however additional organosulfur compounds were also correlated with fungal mycelial growth reduction. While the results from this assay were promising, from a more practical perspective a concern arises: are the VOCs produced by bacteria on nutrient-rich agar representative of compounds produced in the rhizosphere, a less nutrient-rich environment?

The question brought up in Chapter 2 was the focus of the experiments in Chapter 3, in which three Pseudomonas strains were selected for further investigation. One method used to enhance microbial activity in the soil is though priming, the adding of material to enhance the activity of microorganisms and or/soil processes (Kuzyakov et al 2000). We investigated the volatile profile and antagonistic behavior of the bacteria on minimal medium with or without supplementation with glycine or L-methionine. These amino acids are the precursors to HCN and organosulfur compounds, two categories of compounds associated with inhibiting growth of F. oxysporum (Chapter 2), and we hypothesized priming the medium with them would enhance the control capabilities of the bacteria. Results from the amino acid-priming study showed that within our system, the addition of methionine had a substantial effect on the VOC profile and control potential of two of the pseudomonads, however the individual effects varied by strain. To address another question of applicability—the priming effect in vitro in agar-based media is not truly representative of the soil—we tested our most bioactive strain from the priming

233 experiments in soil supplemented with methionine. In a small-scale closed system, methionine was able to both prime the inoculated Pseudomonas and native microorganisms in the soil to produce VOCs inhibitory to F. oxysporum. While it seems promising as a tool to enhance microorganism activity, further experiments must be performed a larger scale, on a variety of soil types, in both open and closed systems, to determine whether priming for VOCs can be an effective tool in microorganism control. Priming Pseudomonas for non-VOCs secondary metabolites can also be considered and investigated, especially because in an open soil setting it is unlikely any beneficial bacteria’s sole mode of action is volatile. Under the right circumstances, priming for antibiotics—volatile and not—could be effective tools to use in pathogen control. For bacteria with good VOC activity, it is also important to consider that the field may not be the optimal environment for activity, and future directions could explore the use of bacteria in controlled agriculture environments.

While not related to VOCs, Chapter 4 of this work investigated the potential of bacteria to control soybean cyst nematode (SCN) in small-scale microplot trials. These experiments were more applied than the VOC assays; multiple bioproducts are currently sold to control SCN, however the beneficial effects of the products are often varied. The purpose of this study was to search for additional candidates capable of reducing the impact of SCN on soybeans, with the long-term goal that promising single strains or consortia could be licensed. The results from the microplot trials yielded inconsistent results from trial to trial. While some treatments were only tested in one or two trials, eight bacteria treatments were tested in all microplot trials. Of these treatments, none were consistently significant in reducing SCN populations or increasing soybean yield across the trials. In the future, our most promising candidates can be optimized in an attempt to see more consistent results. Due to the nature and complexity of the system (plant,

234 pathogen, and biocontrol agent), consistently significant results may be unattainable, however a consistently positive effect is better than no effect. Because inconsistency has been reported for multiple commercial bionematicides, future trials should include more commercial products as points of comparison, as the ideal candidate is comparable, or better, than the products currently on the market.

The results from this dissertation’s Chapters 2, 3, and 4 leave room for future scientific inquiries and exploration regarding the ideal biocontrol niche for these bacteria. As more studies are done into determining the role of the bacteria used in this work, a more comprehensive picture of the Pseudomonas and Pantoea strains will arise. Information from studies like the ones presented her can be made available to companies, thus furthering university-industry collaboration and moving research from more basic to applied.

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Appendix A1 Volatile Organic Compounds Quantified in the Headspace of Pseudomonas spp. and Pantoea agglomerans

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The information presented in this appendix is from the volatile organic compound (VOC) profiling in Chapters 2 and 3 of this dissertation. While a majority of the VOCs were present in both data sets, compounds quantified in only one chapter are specifically marked. Compounds were included in the table if they were present at levels <1ppbv in every replicate of at least one bacterium or control. In both Chapters 2 and 3, additional compounds were quantified, but left out of the table because they were close to the limit of detection (<1ppbv).

Chapter 2 m/z that were not significantly different (ANOVA α=0.05) between the treatments and controls: 33.033, 69.070, 75.044, 81.070, 83.086, 153.127.

Chapter 3 m/z that were not significantly different (ANOVA α=0.05) between the treatments and controls: 31.018, 39.023, 41.039, 43.054, 55.054, 57.033, 69.070, 75.044, 83.049, 83.086,

129.091, 153.127.

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Table A1.1. Compounds identified with PTR-ToF-MS analysis. Compounds listed are at abundances >1ppbv in at least one treatment. The papers listed in both the PTR-ToF-MS and Pseudomonas citations columns are meant to be representative, rather than exhaustive. In some instances, multiple putative identities are given. Citations are only included if they provided identification of the compound included here; in some instances, a compound was measured with no putative identification given, or an alternative compound identity was given that did not fit for our system.

A) VOCs present in Chapter 2 and Chapter 3 Data

Protonated Theoretical Experimental Tentative PTR-ToF-MS/ Compound Chemical Mass Pseudomonas VOCs Citationsg Mass (m/z)a Identificationd PTR-MS Citationse Formulab (m/z)c

+ 1 27.023 C2H3 27.023 Alkyl fragment

Bean et al 2012; Ossowicki et al 2 28.020 CH N+ 28.018 Hydrogen cyanide Moussa et al 2016 2 2017

+ 3 30.045 C2H6 30.046 Alkyl fragment

Infantino et al 2017; Vita et 4 31.020 CH O+ 31.018 Formaldehyde Thorn et al 2011 3 al 2015

Buhr et al 2002; Infantino et + 5 33.033 CH5O 33.033 Methanol al 2017; Khomenko et al Bean et al 2012 2017; Vita et al 2015

Infantino et al 2017; 6 39.022 C H + 39.023 Isoprene fragment 3 3 Maleknia et al 2007

(Table A1.1 Continued).

263

(Table A1.1 Continued).

Protonated Theoretical Experimental Tentative PTR-ToF-MS/ Compound Chemical Mass Pseudomonas VOCs Citationsg Mass (m/z)a Identificationd PTR-MS Citationse Formulab (m/z)c Alkyl fragment (alcohol, ester, Buhr et al 2002; Gueneron et 7 41.040 C H + 41.039 3 5 aldehyde, al 2015 hydrocarbon) Acetyl fragment Buhr et al 2002; Maleknia et 8 43.020 C H O+ 43.018 2 3 (ester) al 2007 Alkyl fragment Buhr et al 2002; Gueneron et 9 43.055 C H + 43.054 (alcohol, ester, 3 7 al 2015 hydrocarbon) Infantino et al 2017; + 10 45.033 C2H5O 45.033 Acetaldehyde Maleknia et al 2007; Perraud et al 2016; Vita et al 2015 DMS fragment or + f 11 46.995 CH3S 46.995 methanethiol Mochalski et al 2014 fragment Buhr et al 2002; Infantino et al 2017; Maleknia et al 2007; 12 47.050 C H O+ 47.049 Ethanol Thorn et al 2011, Zhu et al 2010 2 7 Perraud et al 2016; Vita et al 2015 Khomenko et al 2017; Methanethiol: Methanethiol or 13 49.011 CH S+ 49.011 Papurello et al 2015; Perraud Lo Cantore et al 2015; Thorn et al 5 DMDS fragment et al 2016; Vita et al 2015 2011

14 51.010 Unknown XXX Unidentified fragment

+ 15 53.040 C4H5 53.039 Alkyl fragment

(Table A1.1 Continued).

264

(Table A1.1 Continued).

Protonated Theoretical Experimental Tentative PTR-ToF-MS/ Compound Chemical Mass Pseudomonas VOCs Citationsg Mass (m/z)a Identificationd PTR-MS Citationse Formulab (m/z)c

Alkyl fragment + 16 55.055 C4H7 55.054 (aldehyde, Buhr et al 2002 cis-3-hexen-1-ol)

Acetyl fragment 17 57.033 C H O+ 57.033 Buhr et al 2002 3 5 (ester)

Butyl fragment Buhr et al 2002; Gueneron et 18 57.070 C H + 57.070 4 9 (alcohol, hydrocarbon) al 2015; Maleknia et al 2007

Buhr et al 2002; Infantino et al 2017; Khomenko et al + 19 59.049 C3H7O 59.049 Acetone or Propanal 2017; Maleknia et al 2007; Acetone: Zhu et al 2010 Perraud et al 2016; Vita et al 2015 Buhr et al 2002; Infantino et Acetic acid or ester al 2017; Khomenko et al Acetic Acid: Bean et al 2012, Zhu 20 61.028 C H O + 61.028 2 5 2 fragments 2017; Perraud et al 2016; et al 2010 Vita et al 2015 Dimethyl sulfide Papurello et al 2015;Perraud Bean et al 2012; Ossowicki et al 21 63.027 C H S+ 63.026 2 7 (DMS) et al 2016; Vita et al 2015 2017; Alkyl Fragment Buhr et al 2002; 22 65.040 C H + 65.039 5 5 (Ethanol, methanol) Maleknia et al 2007 Buhr et al 2002;Infantino et Isoprene or alkyl al 2017; Maleknia et al 2007; 23 69.070 C H + 69.070 Isoprene: Thorn et al 2011 5 9 fragment (aldehyde) Perraud et al 2016; Vita et al 2015

(Table A1.1 Continued).

265

(Table A1.1 Continued).

Protonated Theoretical Experimental Tentative PTR-ToF-MS/ Compound Chemical Mass Pseudomonas VOCs Citationsg Mass (m/z)a Identificationd PTR-MS Citationse Formulab (m/z)c Buhr et al 2002; Infantino et al 2017; Khomenko et al 24 73.063 C H O+ 73.065 2-Butanone or butanal Butanone: Bean et al 2012 4 9 2017; Perraud et al 2016; Vita et al 2015 Bean et al 2012; Ossowicki et al 25 74.010 C H NS+ 74.006 Methyl thiocyanate 2 4 2017; Methyl Acetate or Buhr et al 2002; Infantino et Propionic Acid or al 2017; Khomenko et al 26 75.045 C H O + 75.044 3 7 2 other fragments (e.g.- 2017; Perraud et al 2016; acid, formate, acetate) Vita et al 2015

+ 27 78.990 CH3S2 78.967 DMDS Fragment Perraud et al 2016

Alkyl fragment (Cis-3- Buhr et al 2002, Infantino et 28 83.088 C H + 83.086 6 11 hexen-1-ol or hexanal) al 2017, Perraud et al 2016 Bean et al 2012; Ossowicki et al 29 91.025 C H OS+ 91.021 S-methyl thioacetate Khomenko et al 2017 3 7 2017;

Dimethyl disulfide Lo Cantore et al 2015; Ossowicki 30 95.001 C H S + 94.998 2 7 2 (DMDS) Perraud et al 2016 et al 2017; Thorn et al 2011

Terpenoid-like 31 compound 153.120 C H O+ 153.127 Vita et al 2015 10 17 (e.g. camphor, fenchone or carveol)

(Table A1.1 Continued).

266

(Table A1.1 Continued).

B) VOCs Present only in Chapter 2 (Determination of the volatile compounds produced by Pseudomonas strains and establishing their role in biocontrol.)

Protonated Theoretical Experimental Tentative PTR-ToF-MS/ Compound Chemical Mass Pseudomonas VOCs Citationsg Mass (m/z)a Identificationd PTR-MS Citationse Formulab (m/z)c

+ 1 67.058 C5H7 67.054 Alkyl Fragment

Methyl vinyl ketone or Infantino et al 2017; 2 71.052 C H O+ 71.049 4 7 butenal Khomekno et al 2017;

Alkyl fragment Buhr et al 2002; Gueneron et 3 71.090 C H + 71.086 5 11 (alcohol, hydrocarbon) al 2015

S- compound 4 77.043 C H S+ 77.042 Papurello et al 2015 3 9 fragment

+ 5 79.050 C6H7 79.054 Alkyl Fragment

Alkyl fragments Maleknia et al 2007; Perraud 6 81.070 C H + 81.070 (monoterpene 6 9 et al 2016; Vita et al 2015 fragments)

(Table A1.1 Continued).

267

(Table A1.1 Continued).

2-pentanone or Buhr et al 2002; Infantino et Pentanone: Bean et al 2012 Zhu 7 87.080 C H O+ 87.080 pentanal or al 2017; Khomenko et al 5 11 et al 2010 methylbutanal 2017; Vita et al 2015

h + 8 97.030 C5H5O2 97.028 Furfural Vita et al 2015

C) VOCs Present only in Chapter 3 (Identifying the potential to prime Pseudomonas spp. for volatile organic compound production though manipulation of the culture medium.)

Protonated Theoretical Experimental Tentative PTR-ToF-MS/ Compound Chemical Mass Pseudomonas VOCs Citationsg Mass (m/z)a Identificationd PTR-MS Citationse Formulab (m/z)c

+ 1 62.989 CH3OS 62.990 S-compound fragment

2 63.945 Unknown

Vita et al 2015 3 83.049 C H O+ 83.049 Methylfuran 5 7

+ 4 91.060 C4H11S 91.058 S-compound fragment Papurello et al 2015

(Table A1.1 Continued).

268

(Table A1.1 Continued).

5 93.997 Unknown

+ C4H3NS or 96.998 or 6 97.0000 + S-compound fragment CH5O3S 96.995

i 7 129.09 C7H13O2 129.091 2,3 Heptanedione Garbeva et al 2014b aExperimental Mass to Charge Ratio measured during analysis with PTR-ToF-MS. Experimental masses for A) and B) are from Chapter 2 data, and masses for C) is from Chapter 3 data. bProtonated chemical formula determined based on experimental m/z. ctheoretical mass to charge ratio determined with the Barrow Group (University of Warwick) m/z calculator. dtentative compound identification given, based on whether the compound has been previously quantified and/or associated with Pseudomonas and identified with PTR-ToF-MS or PTR-MS. epreviously identified and/or quantified with PTR-ToF-MS, PTR-MS, or other mass spectrometry analysis systems (listed below). For papers that used PTR-MS to identify fragmentation patterns of alcohols, aldehydes, ketones, and hydrocarbons, only indicate the presence of a specific compound if all mass fragments from the selected compound were present. While it is unlikely that our bacteria produced the specific compounds presented in Gueneron et al (2015), fragmentation patterns were similar between multiple alkanes and alkenes, and we decided the fragmentation patterns could match a general “hydrocarbon” designation. If possible, we matched the chemical formulas presented for each compound with our determined chemical formula. fselective reagent ionization time-of-flight mass spectrometry (SRI-TOF-MS) (Mochalski et al 2014) gpreviously viewed in the volatilome of Pseudomonas. hquantified only in the LB-control of Chapter 2 iquantified in Collimonas pratensis volatilome (Garbeva et al 2014b)

269

References

Bean, H. D., Dimandja, J. M. D., & Hill, J. E. (2012). Bacterial volatile discovery using solid phase microextraction and comprehensive two-dimensional gas chromatography-time-of- flight mass spectrometry. Journal of Chromatography B, 901, 41–46. https://doi.org/10.1016/j.jchromb.2012.05.038 Buhr, K., Van Ruth, S., & Delahunty, C. (2002). Analysis of volatile flavour compounds by Proton transfer reaction-mass spectrometry: Fragmentation patterns and discrimination between isobaric and isomeric compounds. International Journal of Mass Spectrometry, 221(1), 1–7. https://doi.org/10.1016/S1387-3806(02)00896-5 Garbeva, P., Hordijk, C., Gerards, S., & de Boer, W. (2014b). Volatiles produced by the mycophagous soil bacterium Collimonas. FEMS Microbiology Ecology, 87(3), 639–649. https://doi.org/10.1111/1574-6941.12252 Gueneron, M., Erickson, M. H., Vanderschelden, G. S., & Jobson, B. T. (2015). PTR-MS fragmentation patterns of gasoline hydrocarbons. International Journal of Mass Spectrometry, 379, 97–109. https://doi.org/10.1016/j.ijms.2015.01.001 Infantino, A., Costa, C., Aragona, M., Reverberi, M., Taiti, C., & Mancuso, S. (2017). Identification of different Fusarium spp. through mVOCS profiling by means of proton- transfer-reaction time-of-flight (PTR-TOF-MS) analysis. Journal of Plant Pathology, 99(3), 663–669. https://doi.org/10.4454/jpp.v99i3.3953 Khomenko, I., Stefanini, I., Cappellin, L., Cappelletti, V., Franceschi, P., Cavalieri, D., … Biasioli, F. (2017). Non-invasive real time monitoring of yeast volatilome by PTR-ToF-MS. Metabolomics, 13(10), 1–13. https://doi.org/10.1007/s11306-017-1259-y Lo Cantore, P., Giorgio, A., & Iacobellis, N. S. (2015). Bioactivity of volatile organic compounds produced by Pseudomonas tolaasii. Frontiers in Microbiology, 6(1082). https://doi.org/10.3389/fmicb.2015.01082 Maleknia, S. D., Bell, T. L., & Adams, M. A. (2007). PTR-MS analysis of reference and plant- emitted volatile organic compounds. International Journal of Mass Spectrometry, 262(3), 203–210. https://doi.org/10.1016/j.ijms.2006.11.010 Mochalski, P., Unterkofler, K., Španěl, P., Smith, D., & Amann, A. (2014). Product ion distributions for the reactions of NO+ with some physiologically significant volatile organosulfur and organoselenium compounds obtained using a selective reagent ionization time-of-flight mass spectrometer. Rapid Communications in Mass Spectrometry, 28(15), 1683–1690. https://doi.org/10.1002/rcm.6947 Moussa, S. G., Leithead, A., Li, S. M., Chan, T. W., Wentzell, J. J. B., Stroud, C., … Liggio, J. (2016). Emissions of hydrogen cyanide from on-road gasoline and diesel vehicles. Atmospheric Environment, 131, 185–195. https://doi.org/10.1016/j.atmosenv.2016.01.050 Ossowicki, A., Jafra, S., & Garbeva, P. (2017). The antimicrobial volatile power of the rhizospheric isolate Pseudomonas donghuensis P482. PLoS ONE, 12(3), 1–13. https://doi.org/10.1371/journal.pone.0174362 Papurello, D., Tognana, L., Lanzini, A., Smeacetto, F., Santarelli, M., Belcari, I., … Biasioli, F. (2015). Proton transfer reaction mass spectrometry technique for the monitoring of volatile sulfur compounds in a fuel cell quality clean-up system. Fuel Processing Technology, 130, 136–146. https://doi.org/10.1016/j.fuproc.2014.09.041 Perraud, V., Meinardi, S., Blake, D. R., & Finlayson-Pitts, B. J. (2016). Challenges associated with the sampling and analysis of organosulfur compounds in air using real-time PTR-ToF-

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MS and offline GC-FID. Atmospheric Measurement Techniques, 9(3), 1325–1340. https://doi.org/10.5194/amt-9-1325-2016 Thorn, R. M. S., Reynolds, D. M., & Greenman, J. (2011). Multivariate analysis of bacterial volatile compound profiles for discrimination between selected species and strains in vitro. Journal of Microbiological Methods, 84(2), 258–264. https://doi.org/10.1016/j.mimet.2010.12.001 Vita, F., Taiti, C., Pompeiano, A., Bazihizina, N., Lucarotti, V., Mancuso, S., & Alpi, A. (2015). Volatile organic compounds in truffle (Tuber magnatum Pico): Comparison of samples from different regions of Italy and from different seasons. Scientific Reports, 5, 12629. https://doi.org/10.1038/srep12629 Zhu, J., Bean, H. D., Kuo, Y. M., & Hill, J. E. (2010). Fast detection of volatile organic compounds from bacterial cultures by secondary electrospray ionization-mass spectrometry. Journal of Clinical Microbiology, 48(12), 4426–4431. https://doi.org/10.1128/JCM.00392-10

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Appendix A2:

Root Exudate Profile of 10-day Old Glycine max ‘Lee’ Seedlings

272

The information and data presented below is unpublished data by Timothy Frey, Rebecca

Kimmelfield, & Christopher Taylor. RK and TF contributed equally to the conception, implementation, and analysis of the experiment presented here.

A2.1 Materials and Methods

A2.1.1 Plant material

Soybean (Glycine max ‘Lee’), was used in the root exudate collection experiments. Lee, a

SCN-susceptible cultivar of soybean was used because it was commonly used in other experiments done in the Taylor laboratory. Soybean seeds were sterilized for 6 hours-overnight using chlorine gas (approximately 10ml 37% HCl added to approximately 200ml bleach) in a vacuum-sealed chamber. Sterile seeds were imbibed in sterile ddH2O overnight before experimental setup.

A2.1.2 Experimental setup and quantification: Root exudates

All material used was either wiped with 70% ethanol or autoclaved to ensure the materials used were as sterile as possible. Experimental setup occurred in the laminar flow hood to ensure clean conditions. Imbibed seedlings were placed in plastic funnels containing 50ml

Quikrete play-sand and covered with another 30ml sand. The sand was saturated with 35ml ¼

Murashige and Skoog (MS) medium. The funnels contained filter paper and wire mesh to keep the sand from leaking out of the funnels. Funnels were placed in acrylic boxes (Nalgene®) that were approximately 39cm x 28cm x 28cm in size. Each box could fit two tube racks, and ten funnels were placed on the racks. There were two blank funnels (sand only) in every box. A cartoon of experimental setup can be seen in Figure A.1 The boxes were sealed with micropore

273 tape (3M®) and placed in a growth chamber at 25°C for two weeks at 16h:8h day:night. After a two-week growth period, when seedlings were approximately 10 days old (2nd or 3rd trifoliate beginning to open) root exudates were harvested from the systems. Plants and controls were washed two times with sterile ddH2O (35ml/wash). Multiple washes were done to harvest as many exudates as possible. The sand of one biological replicate was washed three times due to low volume collected from the first wash. Sand from the plant samples and blanks were spread on Luria-Bertani agar plates to check for sterility. Washes were stored at 4°C, and samples that did not have contaminants present in the sand were used for analysis. We stored clean samples at

4°C under the assumption that no-minimal turnover of the amino acids would occur in a clean system. The harvested exudates were filtered with a .22µM filter, frozen, and lyophilized before being sent for analysis at the Targeted Metabolomics Laboratory (TML, The Ohio State

University, Columbus, OH). At the TML freeze dried samples were resuspended and amino acids were analyzed using Liquid-Chromatography Tandem Mass-Spectrometry (LC-MS/MS) according to the methodology previously described in Cocuron et al (2014). Compounds were quantified relative to the amounts quantified in an external amino acid standard (Table A2.1).

A2.2 Results

Twenty-four amino acids were quantified using LC-MS/MS. The distribution of amino acids produced by Glycine max ‘Lee’ root exudates were varied. Average values ranged from

105pmol/ml (cysteine) to 356,095pmol/ml (asparagine). Due to large variation of total quantity of exudates between the biological replicates, we prefer to represent each individual amino acid as a proportion of the total measured amino acids produced by an individual plant (Tables A2.2 and A.3). The most abundant amino acid was asparagine (41.67% of the total profile). Four

274 additional compounds (alanine, glutamine, proline, and valine) each represented between 6-8% of the total profile. Eight compounds (citrulline, cysteine, hydroxyproline, lysine, methionine, ornithine, tryptophan, and tyrosine) were present in very low amounts, and each represented <1% of the total profile (combined, just over 2% of the total profile). The amino acids <1% can be considered negligible contributions to the overall root exudate profile. The amino acids at the lowest amounts (<0.5%) can be considered negligible to the overall profile. We did not remove any compounds on the basis of low signal to noise.

Glycine and methionine, two amino acids of interest in Chapter 3 of this work, represented respectively 3.07 and 0.11% of the total amino acids profile of 10-day old soybean seedlings.

References Cocuron, J. C., Anderson, B., Boyd, A., & Alonso, A. P. (2014). Targeted metabolomics of Physaria fendleri, an industrial crop producing hydroxy fatty acids. Plant and Cell Physiology, 55(3), 620–633. https://doi.org/10.1093/pcp/pcu011

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Figure A2.1. Setup of Root Exudate Experiment. Seedlings were grown in sterilized funnels filled with sterile sand saturated with ¼ MS Medium. Seedlings were kept in acrylic boxes that were sealed with micropore tape (3M®). Each box could hold up to 10 funnels. There were two blanks (no plant) in every box.

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Table A2.1. Amino acid external standard. Amino acids in the external standard were injected at a known quantity. Quantity of metabolites in the root exudates were calculated according to the quantity of amino acid in the standard. Concentrations obtained from Jean-Christophe Cocuron (2014) of the Targeted Metabolomics Laboratory at Ohio State University.

Expected Retention 1X Concentration Time Metabolite 100X Concentration (uM) (uM) (min) Arginine 25 0.25 3.25 Citrulline 25 0.25 3.25 GABA 25 0.25 1.27 Histidine 25 0.25 2.18 Isoleucine 25 0.25 2.24 Leucine 25 0.25 2.04 Methionine 25 0.25 3.00 Hydroxyproline 25 0.25 1.73 Proline 25 0.25 1.75 Serine 25 0.25 1.47 Threonine 25 0.25 1.53 Tryptophan 25 0.25 5.19 Tyrosine 25 0.25 3.57 Valine 25 0.25 1.75 Alanine 125 1.25 1.46 Asparagine 125 1.25 1.77 Aspartate 125 1.25 2.06 Cysteine 125 1.25 1.79 Glutamate 125 1.25 2.36 Glutamine 125 1.25 2.00 Glycine 125 1.25 1.41 Ornithine 125 1.25 1.14 Phenylalanine 125 1.25 3.53 Lysine 125 1.25 1.18

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Table A2.2. Amount of 24 amino acids in root exudates of Glycine max 'Lee' seedlings. Values are expressed as pmol/ml. Either 1 or 10µl of resuspended root exudates were injected into the LC-MS/MS. Seedlings were grown under sterile conditions for two weeks before harvest of the root exudates. n=4.

AVERAGE pmol/ml STDEV pmol/ml Alanine 24930.19 12290.39 Arginine 15658.05 13127.96 Asparagine 356095.68 373925.78 Aspartic Acid 7506.23 3439.03 Citrulline 636.41 662.52 Cysteine 105.34 19.39 GABA 12972.21 10996.25 Glutamate 7365.56 4132.41 Glutamine 29890.54 25329.66 Glycine 9824.02 5174.52 Histidine 8500.05 8080.35 Hydroxyproline 761.57 502.40 Isoleucine 12458.96 8874.83 Leucine 8567.62 5047.45 Lysine 4330.00 4034.24 Methionine 725.56 938.06 Ornithine 168.80 150.64 Phenylalanine 29030.40 29764.27 Proline 30917.92 25703.68 Serine 15730.97 15165.30 Threonine 16138.81 14233.81 Tryptophan 769.89 838.60 Tyrosine 2052.80 1001.62 Valine 27063.49 18781.03

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Table A2.3. Proportion of 24 amino acids in root exudates of Glycine max 'Lee' seedlings. Seedlings were grown under sterile conditions for two weeks before harvest of the root exudates. Compounds in red are present at amounts <1% of the total amino acids. Compounds <0.5% can be considered negligible contributions to the overall root exudate profile. n=4. AVERAGE % Total Amino Acid STDEV % Total Amino Acid Alanine 7.92 5.86 Arginine 2.90 0.71 Asparagine 41.67 24.47 Aspartic Acid 2.48 2.35 Citrulline 0.08 0.03 Cysteine 0.04 0.04 GABA 2.46 1.09 Glutamate 1.94 1.15 Glutamine 6.26 2.77 Glycine 3.07 2.25 Histidine 1.59 0.54 Hydroxyproline 0.18 0.09 Isoleucine 2.74 1.14 Leucine 2.14 1.13 Lysine 0.85 0.37 Methionine 0.11 0.06 Ornithine 0.03 0.01 Phenylalanine 4.92 1.36 Proline 6.37 2.32 Serine 2.63 0.58 Threonine 2.89 0.58 Tryptophan 0.14 0.07 Tyrosine 0.59 0.40 Valine 6.00 2.51

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