Abstract

AbstractGarlic mustard [Alliaria petiolata (M. Bieb.) Cavara & Grande] is a biennial invasive plant commonly found in the northeastern and midwestern United States. Although it is not recommended to apply herbicides after flowering, land managers frequently desire to conduct management during this timing. We applied glyphosate and triclopyr (3% v/v and 1% v/v using 31.8% and 39.8% acid equivalent formulations, respectively) POST to established, second-year A. petiolata populations at three locations when petals were dehiscing and evaluated control, seed production, and seed viability. POST glyphosate applications at this timing provided 100% control of A. petiolata by 4 wk after treatment at all locations, whereas triclopyr efficacy was variable, providing 38% to 62% control. Seed production was only reduced at one location, with similar results regardless of treatment. Percent seed viability was also reduced, and when combined with reductions in seed production, resulted in a 71% to 99% reduction in number of viable seeds produced per plant regardless of treatment. While applications did not eliminate viable seed production, our findings indicate that glyphosate and triclopyr applied while petals are dehiscing is a viable alternative to cutting or hand pulling at this timing, as it substantially decreased viable A. petiolata seed production.

Highlights

  • Our study indicated that glyphosate applications at this timing provided 100% control of A. petiolata plants by 4 wk after treatment at all locations, whereas triclopyr efficacy was inconsistent

  • Our findings suggest late spring glyphosate and triclopyr applications should not be recommended over early spring applications to rosettes for A. petiolata management, as our late spring application timing did not prevent viable seed production, and may require multiple years of implementation to eradicate populations

  • Our main study goal is to quantify the impacts of herbicide treatments on A. petiolata seed production and viability, visual assessment of control on the target weed species was collected as it is useful information for land managers (Enloe et al 2016)

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Summary

Introduction

Bieb.) Cavara & Grande] is a biennial invasive forb originally from Europe (Nuzzo 2000). It was introduced into North America in the 1800s (Grieve 2013) and by 2000 had spread to 34 U.S states and four Canadian provinces (Nuzzo 2000). A. petiolata commonly infests forests in partial sunlight, it can be present in a wide range of habitats, including railroad ballast, floodplains, and xeric ridgetops (Byers and Quinn 1998; Nuzzo 2000). Forest understories dominated by A. petiolata are associated with negative impacts to native ecosystems, including low richness and diversity of native herbaceous vegetation (Anderson et al 1996; Nuzzo 2000) and reduced growth of tree seedlings that depend on arbuscular mycorrhizal fungi (Burke 2008; Stinson et al 2006)

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