Individual Competition Indices for Conifer Plantations

Author(s):  
P. CORONA ◽  
A. FERRARA
2021 ◽  
Vol 489 ◽  
pp. 119073
Author(s):  
Satoshi Yamanaka ◽  
Yuichi Yamaura ◽  
Katsuhiko Sayama ◽  
Shigeho Sato ◽  
Kenichi Ozaki

2021 ◽  
pp. 1-11
Author(s):  
Kazuhiro Kawamura ◽  
Yuichi Yamaura ◽  
Masashi Soga ◽  
Rebecca Spake ◽  
Futoshi Nakamura

2006 ◽  
Vol 237 (1-3) ◽  
pp. 15-28 ◽  
Author(s):  
Etsuko Utsugi ◽  
Hiroshi Kanno ◽  
Naoto Ueno ◽  
Mizuki Tomita ◽  
Tomoyuki Saitoh ◽  
...  

1993 ◽  
Vol 63 (2) ◽  
pp. 171-176 ◽  
Author(s):  
N.S. Weatherley ◽  
E.C. Lloyd ◽  
S.D. Rundle ◽  
S.J. Ormerod

Fire Ecology ◽  
2021 ◽  
Vol 17 (1) ◽  
Author(s):  
Robert A. York ◽  
Jacob Levine ◽  
Kane Russell ◽  
Joseph Restaino

Abstract Background Young, planted forests are particularly vulnerable to wildfire. High severity effects in planted forests translate to the loss of previous reforestation investments and the loss of future ecosystem service gains. We conducted prescribed burns in three ~35-year-old mixed conifer plantations that had previously been masticated and thinned during February in order to demonstrate the effectiveness of winter burning, which is not common in the Sierra Nevada, California. Results On average, 59% of fine fuels were consumed and the fires reduced shrub cover by 94%. The average percent of crown volume that was damaged was 25%, with no mortality observed in overstory trees 1 year following the fires. A plot level analysis of the factors of fire effects did not find strong predictors of fuel consumption. Shrub cover was reduced dramatically, regardless of the specific structure that existed in plots. We found a positive relationship between crown damage and the two variables of Pinus ponderosa relative basal area and shrub cover. But these were not particularly strong predictors. An analysis of the weather conditions that have occurred at this site over the past 20 years indicated that there have consistently been opportunities to conduct winter burns. On average, 12 days per winter were feasible for burning using our criteria. Windows of time are short, typically 1 or 2 days, and may occur at any time during the winter season. Conclusions This study demonstrates that winter burning can be an important piece of broader strategies to reduce wildfire severity in the Sierra Nevada. Preparing forest structures so that they can be more feasible to burn and also preparing burn programs so that they can be nimble enough to burn opportunistically during short windows are key strategies. Both small landowners and large agencies may be able to explore winter burning opportunities to reduce wildfire severity.


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