Abstract:We reviewed all available studies on Phragmites australis management in the United States. Our results show that there is a heavy emphasis on herbicides to manage Phragmites, relative to other methods, and a lack of information on what types of plant communities establish once Phragmites is removed. Our model of Phragmites establishment and reproduction describes the invasion as a symptom of watershed-scale land use and disturbance. We advocate more holistic approaches to control and management that focus on i… Show more
“…This finding is supported by others (Lombard et al 2012;Martin and Blossey 2013b) and it is likely that eradication will be even more elusive in areas with high patch connectivity (Chambers et al 1999;Kulmatiski et al 2010;McCormick et al 2010;Kettenring et al 2012Kettenring et al , 2016Hazelton et al 2014) or in areas with longer invasion histories. For example, the Michigan Department of Environmental Quality has developed a management prioritization tool (MIDEQ 2014) using multiple ecological, human values, and feasibility criteria where populations covering \100 m 2 are assigned a score of 9 and areas of 4000-80,000 m 2 a score of 5, with sites scoring higher receiving priority for management.…”
Section: Discussionsupporting
confidence: 76%
“…It has long been a concern to many scientists (Blossey 1999;Downey 2011Downey , 2014) that published evidence on unintended impacts of NIS management, whether biological, mechanical, physical or chemical, is almost entirely absent (Reid et al 2009;Buckley and Han 2014;Foxcroft et al 2014;Blossey 2016b) including information on outcomes of P. australis management (Hazelton et al 2014). For example, half a million ha of public lands were sprayed with herbicide in the US in 2010 alone to reduce populations of non-indigenous plants with practically no information provided on outcomes (Wagner et al 2017).…”
Section: Discussionmentioning
confidence: 99%
“…In these areas, suppression and containment strategies may be warranted, but potential project benefits need to be weighed against significant drawbacks. Management of large P. australis populations can divert conservation resources from other projects, have questionable efficacy, and may tax society beyond what will be an acceptable long-term commitment (Martin and Blossey 2013b;Hazelton et al 2014). At a minimum, outcome assessments of management are essential to evaluate economic and ecological costs and benefits of this approach.…”
Section: Discussionmentioning
confidence: 99%
“…The species is one of the most widespread and successful NIS in North America (Chambers et al 1999;Kettenring et al 2012;Saltonstall and Meyerson 2016) and has a long history of management (Marks et al 1994;Martin and Blossey 2013b;Hazelton et al 2014). Targeting P. australis is usually justified due to its ability to dominate wetland plant communities with widespread anticipated and documented negative impacts on native plant, invertebrate, fish, reptile and bird communities (Benoit and Askins 1999;Able and Hagan 2000;National Research Council 2004;Bolton and Brooks 2010;Kessler et al 2011;Dibble and Meyerson 2016).…”
Invasive plant management (largely mechanical and chemical) consumes an ever-increasing portion of budgets for land management organizations, but metrics of success, other than extent of areas treated or resources expended is rarely available. Here we assess success of managing 346 populations of invasive Phragmites australis (range 0.36-4134 m 2 ; cover 37-75%) in the Adirondack Park in upstate New York, USA. We began by treating 18 patches in 2010 using herbicide; gradually adding patches treated annually or intermittently for a total of 334 by the end of the project period. We monitored each population annually and if P. australis was present mapped its spatial extent and estimated cover. We considered P. australis eradicated when live stems were absent from a site for at least three consecutive years. Our treatments reduced size and cover of P. australis populations and eradication was achieved at 104 of 294 sites. However, probability of eradicating P. australis over a 7-year project timeframe was 0.83 for the smallest patches (0.36 m 2 ), whereas at medium (45 m 2 ) and large patches ([3000 m 2 ) probability of eradication decreased to 0.26 and 0.02, respectively. Our results question efficacy of managing large P. australis populations with the goal of eradication. We urge conservation organizations to clearly articulate management objectives beyond short-term suppression of target plants and to promote accountability by providing quantitative measurements of outcomes.
“…This finding is supported by others (Lombard et al 2012;Martin and Blossey 2013b) and it is likely that eradication will be even more elusive in areas with high patch connectivity (Chambers et al 1999;Kulmatiski et al 2010;McCormick et al 2010;Kettenring et al 2012Kettenring et al , 2016Hazelton et al 2014) or in areas with longer invasion histories. For example, the Michigan Department of Environmental Quality has developed a management prioritization tool (MIDEQ 2014) using multiple ecological, human values, and feasibility criteria where populations covering \100 m 2 are assigned a score of 9 and areas of 4000-80,000 m 2 a score of 5, with sites scoring higher receiving priority for management.…”
Section: Discussionsupporting
confidence: 76%
“…It has long been a concern to many scientists (Blossey 1999;Downey 2011Downey , 2014) that published evidence on unintended impacts of NIS management, whether biological, mechanical, physical or chemical, is almost entirely absent (Reid et al 2009;Buckley and Han 2014;Foxcroft et al 2014;Blossey 2016b) including information on outcomes of P. australis management (Hazelton et al 2014). For example, half a million ha of public lands were sprayed with herbicide in the US in 2010 alone to reduce populations of non-indigenous plants with practically no information provided on outcomes (Wagner et al 2017).…”
Section: Discussionmentioning
confidence: 99%
“…In these areas, suppression and containment strategies may be warranted, but potential project benefits need to be weighed against significant drawbacks. Management of large P. australis populations can divert conservation resources from other projects, have questionable efficacy, and may tax society beyond what will be an acceptable long-term commitment (Martin and Blossey 2013b;Hazelton et al 2014). At a minimum, outcome assessments of management are essential to evaluate economic and ecological costs and benefits of this approach.…”
Section: Discussionmentioning
confidence: 99%
“…The species is one of the most widespread and successful NIS in North America (Chambers et al 1999;Kettenring et al 2012;Saltonstall and Meyerson 2016) and has a long history of management (Marks et al 1994;Martin and Blossey 2013b;Hazelton et al 2014). Targeting P. australis is usually justified due to its ability to dominate wetland plant communities with widespread anticipated and documented negative impacts on native plant, invertebrate, fish, reptile and bird communities (Benoit and Askins 1999;Able and Hagan 2000;National Research Council 2004;Bolton and Brooks 2010;Kessler et al 2011;Dibble and Meyerson 2016).…”
Invasive plant management (largely mechanical and chemical) consumes an ever-increasing portion of budgets for land management organizations, but metrics of success, other than extent of areas treated or resources expended is rarely available. Here we assess success of managing 346 populations of invasive Phragmites australis (range 0.36-4134 m 2 ; cover 37-75%) in the Adirondack Park in upstate New York, USA. We began by treating 18 patches in 2010 using herbicide; gradually adding patches treated annually or intermittently for a total of 334 by the end of the project period. We monitored each population annually and if P. australis was present mapped its spatial extent and estimated cover. We considered P. australis eradicated when live stems were absent from a site for at least three consecutive years. Our treatments reduced size and cover of P. australis populations and eradication was achieved at 104 of 294 sites. However, probability of eradicating P. australis over a 7-year project timeframe was 0.83 for the smallest patches (0.36 m 2 ), whereas at medium (45 m 2 ) and large patches ([3000 m 2 ) probability of eradication decreased to 0.26 and 0.02, respectively. Our results question efficacy of managing large P. australis populations with the goal of eradication. We urge conservation organizations to clearly articulate management objectives beyond short-term suppression of target plants and to promote accountability by providing quantitative measurements of outcomes.
“…The State of Michigan (2017) lists Phragmites as an invasive species. The introduced, invasive genotype has darker leaves than its native cousin, has lighter-colored rhizomes, and forms more monotypic stands (Great Lakes Commission 2017) ( A thorough review by Hazelton et al (2014) documented how Phragmites establishment in coastal wetland ecosystems is associated with decreased biodiversity, reduced habitat quality for fish and wildlife, and disrupted biogeochemical cycles. Phragmites also negatively effects human use of coastal and wetland areas.…”
The presence of Phragmites australis, an invasive wetland plant, negatively affects coastal property values and home prices rise with distance from Phragmites. Home prices increased as distance to Phragmites increased at a rate of $3.90/meter. Removing Phragmites from a property so that the next closest Phragmites was 400 m away results in a property value increase of over $1,500. Removing all Phragmites within 400 m of any property results in a total property value impact of $837,000. This generates about $13,457-$15,121 in additional property taxes each year once the prices and taxes adjust to the plant's removal. We estimated the cost of Phragmites removal at $687/ha. Removing the approximately 36 ha of Phragmites in the area would cost about $25,041. Future treatments would likely be less than that of the first year. The estimated cost of the first year of Phragmites removal is less than the estimated two years of annual property tax revenue increases.
Water scarcity and invasive vegetation threaten arid‐region wetlands and wetland managers seek ways to enhance wetland ecosystem services with limited water, labor, and financial resources. While prior systems modeling efforts have focused on water management to improve flow‐based ecosystem and habitat objectives, here we consider water allocation and invasive vegetation management that jointly target the concurrent hydrologic and vegetation habitat needs of priority wetland bird species. We formulate a composite weighted usable area for wetlands (WU) objective function that represents the wetland surface area that provides suitable water level and vegetation cover conditions for priority bird species. Maximizing the WU is subject to constraints such as water balance, hydraulic infrastructure capacity, invasive vegetation growth and control, and a limited financial budget to control vegetation. We apply the model at the Bear River Migratory Bird Refuge on the Great Salt Lake, Utah, compare model‐recommended management actions to past Refuge water and vegetation control activities, and find that managers can almost double the area of suitable habitat by more dynamically managing water levels and managing invasive vegetation in August at the beginning of the window for control operations. Scenario and sensitivity analyses show the importance to jointly consider hydrology and vegetation system components rather than only the hydrological component.
scite is a Brooklyn-based organization that helps researchers better discover and understand research articles through Smart Citations–citations that display the context of the citation and describe whether the article provides supporting or contrasting evidence. scite is used by students and researchers from around the world and is funded in part by the National Science Foundation and the National Institute on Drug Abuse of the National Institutes of Health.