TY - JOUR
T1 - Nonnative species influence vegetative response to ecological restoration
T2 - Two forests with divergent restoration outcomes
AU - McGlone, Christopher M.
AU - Stoddard, Michael T.
AU - Springer, Judith D.
AU - Daniels, Mark L.
AU - Fulé, Peter Z.
AU - Wallace Covington, W.
N1 - Funding Information:
Thanks to the Coconino National Forest for assistance with the Fort Valley study, especially A. Farnsworth, B. Thornton, T. Randall-Parker, and G. Waldrip, Rocky Mountain Research Station, especially C. Edminster. The authors also thank the Bureau of Land Management Arizona Strip Field Office for assistance with the Mt. Trumbull Project, especially Ken Moore and Whit Bunting. Additionally, the staff and students of the Ecological Restoration Institute were invaluable for field data collection. A special thanks to H. Smith and D. Normandin for logistical support for this project. We also thank the two anonymous reviewers for their insightful suggestions that greatly improved this manuscript. This work was funded by USDA Forest Service and the USDI Bureau of Land Management.
Copyright:
Copyright 2012 Elsevier B.V., All rights reserved.
PY - 2012/12/1
Y1 - 2012/12/1
N2 - Changes in the vegetative structure and diversity of ponderosa pine forests have generated interest in conducting ecological restoration projects to improve the overall forest health of these ecosystems. Ecological restoration prescriptions often consist of thinning trees to emulate pre-1870s forest structure followed by prescribed burning. Disturbances associated with ecological restoration can, however, promote invasion by nonnative species. We compared two northern Arizona ponderosa pine forests treated for ecological restoration, one at the Fort Valley Experimental Forest and one at Mt. Trumbull on the Grand Canyon-Parashant National Monument. We examined the response of native and nonnative plant species, as well as all species combined, to treatments at the two forests. Both study sites showed a significant increase in native and nonnative species cover and richness by the fifth year post-treatment that remained significant by the tenth year post-treatment. Despite these general trends in native and nonnative community development, the understory vegetation at the two sites followed diverging successional patterns after treatment. By the tenth year post-treatment Fort Valley was dominated by native species and Mt. Trumbull was dominated by a single nonnative species, cheatgrass. The differences in post-treatment understory recovery are likely due to pretreatment forest conditions. At Fort Valley, nonnatives were present, but accounted for only 0.11% of the pretreatment cover. At Mt. Trumbull, nonnatives accounted for 5.26% of the pretreatment understory cover, with cheatgrass accounting for approximately 4% of the understory cover. Additionally, the soil seedbank at Fort Valley had greater overall species richness and greater native perennial grass richness than Mt. Trumbull. We propose that the application of ecological restoration treatments should be targeted to sites with low abundance of nonnatives prior to treatment. Sites containing high abundance of nonnatives prior to treatment should be managed for nonnative species mitigation before initiating any ecological restoration projects.
AB - Changes in the vegetative structure and diversity of ponderosa pine forests have generated interest in conducting ecological restoration projects to improve the overall forest health of these ecosystems. Ecological restoration prescriptions often consist of thinning trees to emulate pre-1870s forest structure followed by prescribed burning. Disturbances associated with ecological restoration can, however, promote invasion by nonnative species. We compared two northern Arizona ponderosa pine forests treated for ecological restoration, one at the Fort Valley Experimental Forest and one at Mt. Trumbull on the Grand Canyon-Parashant National Monument. We examined the response of native and nonnative plant species, as well as all species combined, to treatments at the two forests. Both study sites showed a significant increase in native and nonnative species cover and richness by the fifth year post-treatment that remained significant by the tenth year post-treatment. Despite these general trends in native and nonnative community development, the understory vegetation at the two sites followed diverging successional patterns after treatment. By the tenth year post-treatment Fort Valley was dominated by native species and Mt. Trumbull was dominated by a single nonnative species, cheatgrass. The differences in post-treatment understory recovery are likely due to pretreatment forest conditions. At Fort Valley, nonnatives were present, but accounted for only 0.11% of the pretreatment cover. At Mt. Trumbull, nonnatives accounted for 5.26% of the pretreatment understory cover, with cheatgrass accounting for approximately 4% of the understory cover. Additionally, the soil seedbank at Fort Valley had greater overall species richness and greater native perennial grass richness than Mt. Trumbull. We propose that the application of ecological restoration treatments should be targeted to sites with low abundance of nonnatives prior to treatment. Sites containing high abundance of nonnatives prior to treatment should be managed for nonnative species mitigation before initiating any ecological restoration projects.
KW - Arizona
KW - Cheatgrass
KW - Forest
KW - Nonnative
KW - Ponderosa pine
KW - Prescribed fire
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U2 - 10.1016/j.foreco.2012.08.022
DO - 10.1016/j.foreco.2012.08.022
M3 - Article
AN - SCOPUS:84866169843
SN - 0378-1127
VL - 285
SP - 195
EP - 203
JO - Forest Ecology and Management
JF - Forest Ecology and Management
ER -