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Demonstration of Ecosystem Management Options
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DEMO Home > Research > Vegetation > Postharvest > Tree Damage


Research

Vegetation—Postharvest: Effects of Varying Levels and Patterns of Green-Tree Retention On Amount of Harvesting Damage

Photo of tree damage in DEMO Study Forest.

John R. Moore1, Douglas A. Maguire2
David L. Phillips2, and
Charles B. Halpern3


1Department of Forest Resources
john.moore@forestresearch.co.nz


2Department of Forest Science
Oregon State University
Corvallis, Oregon 97331


3College of Forest Resources
Box 352100
University of Washington
Seattle, WA 98195-2100

 

We provide a brief overview of this work below. For full text see:


Moore, J.; Maguire, D.; Phillips, D.; Halpern, C. 2002. Effects of varying levels and patterns of green-tree retention on amount of harvesting damage. Western Journal of Applied Forestry. 17: 202-206.


In this study, we assessed the magnitude and distribution of tree bole damage resulting from implementation of the retention harvest treatments that make up the DEMO experiment (see Treatment Implementation and Experimental Design).


Among the six study blocks (see Study Area), Douglas-fir (Pseudotsuga menziesii (Mirb.) Franco) and western hemlock (Tsuga heterophylla (Raf.) Sarg.) made up 75 percent of all measured trees (55 and 20 percent, respectively), and the proportion of trees damaged was similar for both species. Suppressed trees tended to be more susceptible to damage than were trees in other crown classes (table 1).


Table 1—Distribution of fresh scars by crown class

 

Crown Class
All trees
Damaged trees
Percentage of total trees
Percentage within crown class
Percentage of all damaged trees
Dominant
4.1
3.5
2.2
Co-dominant
42.3
6.0
39.6
Intermediate
19.2
5.8
17.3
Supressed
32.7
8.1
40.9
Unknown / dead
1.7
0.0
0.0

 

A greater proportion of trees in the dispersed-retention treatments were damaged than in the aggregated treatments (table 2). Only in the two dispersed-retention treatments were levels of damage significantly different from the controls (p<0.05). The greatest proportion of damaged trees occurred in the 15-percent dispersed-retention treatment and was likely due to the wider dispersion and higher intensity of felling and yarding operations associated with this treatment. The pattern of damage across treatments was similar for both small (≤25 cm d.b.h.) and large (>25 cm d.b.h.) trees. Some evidence was also found that sites with gentler slopes had less damage than those with steeper topography.


Table 2—Proportion of trees with fresh scars among the six experimental treatments

Treatment
All trees
Trees ≤25 cm d.b.h.
Trees >25 cm d.b.h.
 
Percent
100-percent control
0.8
1.1
0.6
75-percent aggregated
2.2
3.4
1.3
40-percent dispersed
17.0*
18.1*
15.4*
40-percent aggragated
2.4
2.7
2.3
15-percent dispersed
27.2*
25.0*
29.3*
15-percent aggragated
1.6
1.7
1.8

Means with an asterisk differ significantly (p<0.05) from the control. Fresh scars in the control treatment may reflect wind damage.


Given these initial patterns of harvest-related damage, we expect that the future incidence of stem rot and growth reductions will be greatest in the dispersed-retention treatments.

US Forest Service - Pacific Northwest Research Station, Demonstration of Ecosystem Management Options
Last Modified: Thursday,27March2008 at12:39:30EDT


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