EVALUATING THE COST-EFFECTIVENESS OF ALBERTA’S FOREST MANAGEMENT STRATEGIES IN RESPONSE TO THE MOUNTAIN PINE BEETLE Harry Nelson, Allan Carroll, Arnold Moy, Brad Seely and Clive Welham Faculty of Forestry, UBC WFE/ISFRE June 1 & 2, 2015 University of British Columbia, Vancouver, British Columbia
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EVALUATING THE COST-EFFECTIVENESS OF ALBERTA’S FOREST MANAGEMENT STRATEGIES IN RESPONSE TO THE MOUNTAIN PINE BEETLE Harry Nelson, Allan Carroll, Arnold Moy, Brad Seely and Clive Welham Faculty of Forestry, UBC WFE/ISFRE June 1 & 2, 2015 University of British Columbia, Vancouver, British Columbia
Background • The Mountain Pine
Beetle infestation in British Columbia has affected 18 million m3 of land and is spreading further east into Alberta and beyond. Values at risk include Alberta’s forest industry, worth $9 billion annually, employing 38,000 workers which is largely dependent on pine and is therefore at risk of significant economic loss from MPB-induced mortality; and associated ecosystem services
Courtesy, Hodgson & Cooke 2015
Efforts to Date • Government of
Alberta has spent nearly $370 million on direct control efforts since 2007
• Currently the government of Saskatchewan is funding control efforts in Alberta
Marten Hills, Alberta
Strategies • AESRD has implemented
strategies intended specifically to slow the beetle’s eastward movement, targeting the suppression of MPB populations within stands and areas predicted to have the highest likelihood of promoting additional spread (level 1 and level 2 treatments)
• Province is divided into a leading edge and holding zone
Policy Objectives • The primary goals of the Alberta government’s mitigation
efforts are to slow the spread of MPB into vulnerable pine-dominated watersheds of the eastern slopes and the boreal forest
• The larger policy context is developing a National Pest Management strategy on how to best address other pests and pathogens expanding into new habitat and geographic ranges. • Six et al. (2014) suggests that the opportunities for successful
suppression via direct control are relatively rare, depending on early, aggressive and sustained treatment, and lack of this is what accounts for suppression program failure. This view is supported in a recent study involving case-study meta-analyses of invasives (e.g. Tobin et al. 2014).
Cost Effectiveness Framework • Three-step approach • First identify effects of stand
level treatments • Second, scale to the
landscape given data • Third, quantify the impact
(what would have happened absent interventions)?
• Data show locations of dead trees identified during annual aerial surveys
• Type 1 treatments (Individual tree removal) were applied each year with a focus on front-line areas
• How effective are these expensive treatments at reducing spread?
Aerial Survey Data 2006-2013
Fecundity plotted against trees attacked in a stand
0
2
4
6
8
10
0 5 10 15 20 25
mea
n r
tree count
Mean r vs. tree count
y = abx xc
Presenter
Presentation Notes
Only treatment points are shown here but Survey points were used in combination with treatment point to create the high density masks. The unmasked points in each survey year were used for the analyses.
R² = 0.4214
R² = 0.0996
0
4
8
12
16
0 4 8 12 16
Aver
age
ZOI A
ttack
Inte
nsity
(dea
d/km
2)
Parent Attack Intensity Classes (dead/km2)
ZOI attack intensity vs. Parent Attack intensity (2km ZOI)
Treated
Untreated
• Assessed by grouping parents into classes based upon Attack Intensity
• All years included except 2008 (immigration year)
• Treatment appears to be effective in reducing attack intensity in ZOI area
• Less effective at higher parent attack intensity
Relationship Between Parent and Zone of Attack Intensity
Presenter
Presentation Notes
Relatively smaller treatment effect in 2km ZOI as compared to 1km ZOI
• Assessed by comparing relative change from parent to ZOI in treated vs. untreated parents
• Each year analyzed independently (2008 excluded)
• Parents with < 3 dead excluded
• Substantial error terms
• Mean reduction in AI of 24%
• Less effective in years with high R-values (2010 & 2012 )
-20%
0%
20%
40%
60%
80%
100%
2007 2009 2010 2011 2012
Red
uctio
n in
AI
Effect of treatment on ZOI attack intensity
Relative Reduction in Attack Intensity (2 km zone of influence)
Management Implications • Efforts to date show
treatments reduce fecundity within individual stands
• Depending on population levels, this reduction is sufficient to extirpate local populations
• Next steps involve scaling up to identify if it “slowed the spread”
• In the meantime the results can contribute to identifying stands that are at higher risk and prioritizing monitoring/treatment