COS 39-6 - CANCELLED - Size discrimination of direct and indirect mechanical tree mortality processes in old-growth forests

Tuesday, August 4, 2009: 3:20 PM
Cinnarron, Albuquerque Convention Center
Andrew J. Larson, College of Forestry and Conservation, University of Montana, Missoula, MT and Jerry F. Franklin, School of Environmental and Forest Sciences, University of Washington, Seattle, WA
Background/Question/Methods

The relative importance of different causes of tree mortality in old-growth forests is poorly understood.  We studied the frequency and causes of tree mortality in old-growth conifer forests through repeat censuses of a series of 12, 1.00 ha permanent forest dynamics plots.  All study plots were located in old-growth forests (300-1200 years since stand-initiating disturbance) within Mt. Rainer National Park, WA, USA

Results/Conclusions

A total of 1130 tree mortalities occurred during the three decade study period.  Of the total, 457 trees (40.4% of all mortalities) died proximately from mechanical causes.  Within the mechanical class, 297 trees (65.0% of mechanical mortalities) died due to direct mechanical processes: uprooting or stem breakage by wind, snow and ice, or structural failure.  In contrast, 160 trees (35.0% of mechanical mortalities) died due to indirect mechanical causes; specifically, crushing by falling trees or tree parts (limbs, branches, boles).  Strong size discrimination of direct and indirect mechanical mortality agents was apparent: mean diameter of trees killed by direct mechanical processes was significantly greater (P<0.01) than mean diameter of trees killed by indirect mechanical processes.  Evidence for a contributing role of decay organisms (heart rot, structural root rot, hollow stem) was recorded in 33.3% of trees killed by direct mechanical processes, but was evident in only 5.0% of trees killed by crushing.  These results support the ideas that (1) asymmetrical interactions between trees in old-growth forests are not limited to competition for resources (e.g., light), but also include physical interactions; and (2) decay organisms indirectly contribute to the mortality of uninfected trees by predisposing large, “crush-capable” trees to mechanical mortality.

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