2018
DOI: 10.3390/f9060348
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Evaluating Adaptive Management Options for Black Ash Forests in the Face of Emerald Ash Borer Invasion

Abstract: Abstract:The arrival and spread of emerald ash borer (EAB) across the western Great Lakes region has shifted considerable focus towards developing silvicultural strategies that minimize the impacts of this invasive insect on the structure and functioning of black ash (Fraxinus nigra) wetlands. Early experience with clearcutting in these forests highlighted the risks of losing ash to EAB from these ecosystems, with stands often retrogressing to marsh-like conditions with limited tree cover. Given these experien… Show more

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Cited by 40 publications
(30 citation statements)
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“…Potential evapotranspiration (PET) is approximately 600-650 mm per year (Sebestyen et al, 2011). Detailed site histories were unavailable for the 10 study wetlands, but silvicultural practices in black ash wetlands have been historically limited in extent (D'Amato et al, 2018). Based on the available information (e.g., Erdmann et al, 1987;Kurmis and Kim, 1989), we surmise that our sites are late successional or climax communities and have not been harvested for at least a century.…”
Section: Site Descriptionsmentioning
confidence: 99%
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“…Potential evapotranspiration (PET) is approximately 600-650 mm per year (Sebestyen et al, 2011). Detailed site histories were unavailable for the 10 study wetlands, but silvicultural practices in black ash wetlands have been historically limited in extent (D'Amato et al, 2018). Based on the available information (e.g., Erdmann et al, 1987;Kurmis and Kim, 1989), we surmise that our sites are late successional or climax communities and have not been harvested for at least a century.…”
Section: Site Descriptionsmentioning
confidence: 99%
“…and speckled alder (Alnus incana L. Moench) in minor components, and greater abundances of American elm (Ulmus Americana L.) at lowland sites. Black ash stands are commonly highly uneven with respect to age (Erdmann et al, 1987), with canopy tree ages ranging from 130 to 232 years, and stand development under a gap-scale disturbance regime (D'Amato et al, 2018). Black ash are also typically slow-growing, achieving heights of only 10-15 m and diameters at breast height of only 25-30 cm after 100 years (Erdmann et al, 1987).…”
Section: Vegetationmentioning
confidence: 99%
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“…In contrast to our findings at the site level, we did not find support for our prediction that basal area would correlate with tree base elevation within sites. However, this may not be surprising for three primary reasons: 1) black ash trees are extremely slow growing and there can be very little discernible variability in DBH across trees of different age classes (D'Amato et al 2018, Looney et al 2018, 2) hummock heights (and thus tree base elevation), while centered around some site mean, exhibit variation within a site, leading to a range of elevations supporting trees with similar DBH, and 3) tree base elevations were extremely difficult to ascertain using our TLS matching method, leading to high uncertainty in elevation measurements. Perhaps in wetter black ash systems, it is merely the fact that trees are alive (and on hummocks) that is important.…”
Section: Controls On Tree Biomassmentioning
confidence: 99%
“…Annual precipitation is approximately two-thirds rain and one-third snowfall, and potential evapotranspiration is 600-650 mm yr −1 (Sebestyen et al, 2011). Black ash stands are commonly highly uneven-aged (Erdmann et al, 1987), with canopy tree ages ranging from 130 to 232 years, and stand development under a gap-scale disturbance regime (D'Amato et al, 2018). Black ash is also typically slow growing, achieving heights of only 10-15 m and diameters at breast height of only 25-30 cm after 100 years (Erdmann et al, 1987).…”
Section: Site Descriptionsmentioning
confidence: 99%