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8/7/2019 Whitebark Pine Die off Aerial Assessment
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Assessment of whitebark pine mortality in the mountainareas of the Greater Yellowstone Ecosystem and the
associated ecological implications
W. W. Macfarlane, J. A. Logan and W.R. Kern
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The Greater Yellowstone
Ecosystem (GYE)
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Their strength lies in their numbers
andtheir jaws
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Jeff Hicke 2005
Jesse A. Logan 2009
A Climate Change Issue
Winters are becoming mild enough that even adult beetles, a freezeintolerant stage, are surviving => Spring re-emergence of parent adults.
Brood produced by re-emerged adults may experience enough thermal
energy to complete the life cycle within the same year of attack.
Due to reduced chemical defenses (vs. lodgepole pine), these survivingbeetles, at even relatively low densities, are able to kill whitebark pine
trees.
The combination of a warming climate and the vulnerability of whitebark
pine to attacking beetles has resulted in a shift from non-overlapping,
semivoltine (life cycle requiring two years to complete) generations to
overlapping, bi-modal, univoltine (life cycle completed in a single year).
Resulting in unprecedented levels of outbreaks both in intensity and
spatial distribution (i.e., high-elevation systems).
1999
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Resulting in an alarming level of mortality in previously
inhospitable high elevation whitebark pine forests
EcoFlight 2007
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2009Research Response
2009
We developed and used an aerial
survey method to inventorymountain pine beetle-related
mortality in whitebark pine, across
the entire GYE.
Landscape Assessment System (LAS)
A collaboration between USDA
Forest Service, GYCC Whitebark
Subcommittee , Geo-Graphics
and NRDC.
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LAS Aerial Survey MethodA tool for mapping the extent and intensity of MPB-related
mortality in WBP
Flightlines consisted of 8,673 km and
were parallel with a fixed interval of
approximately 8 km apart (4 km oneach side of the plane).
Flightlines run parallel and along side
mountain ridges instead of over the
crest to ensure higher quality oblique
photos.
A total of 4,653 photos in 2,595
small catchments were captured
GYE Study Area and 2009 LAS Flightlines:
Flight height: 300-600 m
above ground elevation
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1 -Occasional spots ofred trees on the landscape
3 Coalescing spots of red and graytrees across the landscape.
4 Sea -of -Red where approximately 95% +of the visible forest is dead
5-6 -Post outbreak forest mortalityratings (gray forest)
2 -Multiple spots of red and gray treeson the landscape
LAS Mountain Pine Beetle-related Mortality Categories
O -No unusual mountain pine beetle-causedmortality (refers to landscapes that may contain theoccasional red tree but there is no evidence of mortality
expanding to neighboring trees)
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Small Catchment
Mortality Map
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Photo by JOHN McCOLGAN/BLM Alaska Fire Service
Jeff Henry, July 23, 1988
Dunraven Pass - Kathy Peterson; Sept. 1988
Jim Peaco, 1988
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Serious ecological consequences are
already in motion
(1) Reproductive strategies of whitebark asymmetric
mutualismShawn T. MCKinney, Carl E. Fiedler, AND Diana F. Tomback. 2009.
Invasive pathogen threatens birdpine mutualism: implications for sustaining a
high-elevation ecosystem. Ecol. Appl. 19: 597-607.
(2) Size and scale of disturbance event
(3) Lack of co-evolved history with whitebark
Chemical defenses
Raffa, Bentz, Six & Studentsfungal associates Six & Bentz & their Students
(4) Distribution of whitebark/lodgepole forest in the GYE
(5) Synergism with WPBRSix, D. L., and J. Adams. 2006. White pine blister rust severity and selection of
individual whitebark pine by the mountain pine beetle. J. Entomol. Sci. 47: 345-
353.
(6)Serious questions of ecosystem resiliency (See poster)
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Fire Landscape Spatial Pattern
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Main goal: assess ecological
implications using wildliferesponses to ongoingwhitebark mortality
At what level of
whitebark mortality doesa forest stop performingcertain ecologicalfunctions?
This will help managersfocus protection andrestoration efforts inareas most likely tomaintain/ regainecological function
2010-11 Research
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Acknowledgments: USDA Forest Service, Natural Resources Defense Council