2018
DOI: 10.1016/j.foreco.2018.07.054
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Assessing the single-tree and small group selection cutting system as intermediate disturbance to promote regeneration and diversity in temperate mixedwood stands

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Cited by 41 publications
(28 citation statements)
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References 68 publications
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“…We hypothesized that species richness for both shrub and tree seedling species groups should increase with gap area, because larger gaps have higher resource levels and more microsite heterogeneity than small gaps [28,29]. Shrubs were more diverse in our study in resource-rich gaps when compared to the forest understory; this was consistent with shrubs possessing traits more adapted to disturbances, including persistence followed by fast vegetative growth for rapid colonization of newly created habitat patches [16,17].…”
Section: Diversity-resource Relationship and Species Traitssupporting
confidence: 62%
“…We hypothesized that species richness for both shrub and tree seedling species groups should increase with gap area, because larger gaps have higher resource levels and more microsite heterogeneity than small gaps [28,29]. Shrubs were more diverse in our study in resource-rich gaps when compared to the forest understory; this was consistent with shrubs possessing traits more adapted to disturbances, including persistence followed by fast vegetative growth for rapid colonization of newly created habitat patches [16,17].…”
Section: Diversity-resource Relationship and Species Traitssupporting
confidence: 62%
“…The effects of disturbance on taxonomic diversity of the tree regeneration layer often vary with the disturbance severity. For example, taxonomic diversity of the regeneration layer following heavy cutting (e.g., group openings, heavy shelterwood harvests, and clear‐cutting with reserves) has been shown to significantly increase relative to undisturbed forests (Jenkins & Parker, 1998; Elliott & Knoepp, 2005; Nuttle et al ., 2013), while only minor changes occur following lighter cutting and other low‐severity vegetation management treatments (e.g., light thinning, single‐tree selection) (Schweitzer & Dey, 2011; Seiwa et al ., 2012; Raymond et al ., 2018).…”
Section: Discussionmentioning
confidence: 99%
“…Considerations include maintaining the seed source and creating suitable seedbed for limiting species by exposing mineral soil through mechanical scarification for yellow birch (Betula alleghaniensis) or hemlock (Kern et al 2017(Kern et al , 2019 or prescribed burning for pines (Clabo and Clatterbuck 2015), or by retaining highly decayed deadwood for spruce (Raymond and Bédard 2017) or hemlock (Kern et al 2017). In the absence of conditions suitable for germination, underplanting pine (Kabrick et al 2015) or spruce (Kenefic et al 2014, Raymond et al 2018 or other artificial methods may be required. Controlling the microclimate to meet the shade and light requirements of varying species can be accomplished with irregular shelterwoods or group selection in spruce-hardwoods (Raymond et al 2018), shelterwoods in fir-hardwoods (Raymond and Bédard, 2017), or shelterwood and seed tree methods in shortleaf pine-oak (Kabrick et al 2015).…”
Section: Key Findingsmentioning
confidence: 99%
“…In the absence of conditions suitable for germination, underplanting pine (Kabrick et al 2015) or spruce (Kenefic et al 2014, Raymond et al 2018 or other artificial methods may be required. Controlling the microclimate to meet the shade and light requirements of varying species can be accomplished with irregular shelterwoods or group selection in spruce-hardwoods (Raymond et al 2018), shelterwoods in fir-hardwoods (Raymond and Bédard, 2017), or shelterwood and seed tree methods in shortleaf pine-oak (Kabrick et al 2015). Competition control can be accomplished via mechanical or chemical treatments in northern temperate forests or prescribed fires in central and mid-Atlantic regions (Fig.…”
Section: Key Findingsmentioning
confidence: 99%