Forest Insect Disturbance Ecology Lab
Outline
- 1. Annual Aerial Surveys with Treatment Points
- 2. Brief Review of Level 1 Treatment
- 3. Overview of Neighborhood Analysis Method
- 4. Results and Discussion
Assessment of efficacy of Level 1 MPB treatment using neighborhood - - PowerPoint PPT Presentation
Assessment of efficacy of Level 1 MPB treatment using neighborhood analysis Outline 1. Annual Aerial Surveys with Treatment Points 2. Brief Review of Level 1 Treatment 3. Overview of Neighborhood Analysis Method 4. Results and Discussion F
Forest Insect Disturbance Ecology Lab
Aerial Survey Data 2006-2015
identified during annual aerial surveys
year with a focus on leading-edge areas
treatments at reducing spread?
Overview of Level 1 Treatments
aerial survey
locate green-attack trees within a 50m radius
Photo: Lux 2007
Overview of Level 1 Treatments
according to management zone (leading edge, holding, salvage)
infested trees prior to emergence (between Oct-Mar)
Photo: ASRD 2007
Identify parent infestations and assess effect of treatment in surrounding zone of influence
Forest Insect Disturbance Ecology Lab
Overview of Approach
treatment effect
effect
(1km*1km) masking technique was employed to removed high density areas
2011 survey pts.
(1km*1km) masking technique was employed to removed high density areas
surveyed in consecutive years are excluded
forest are excluded
Example 2011 survey area with high density masks
effect
“parent” infestation polygons
survey points with increasing distance between points for grouping
each other grouped as a single infestation
year created by buffering around survey points within each group (750m buffer)
250 500 750 1000 500 1000 1500 2000 # of Groups Grouping distance (m)
Survey 2008 - Frequency of Groups by Buffer Distance
Number of groups Expected groups
15 30 500 1000 1500 2000 Deviation
dynamics by limiting analysis to points within 4km from parent
at 1km (55% of offspring) and 2km (75% of offspring)
0% 25% 50% 75% 100% 0.0 1.0 2.0 3.0 4.0 5.0 Percentile Distance from Parent (km)
Distance From Parent Percentile: Within 4km
2007 2008 2009 2010 2011 2012 2013 All
2011 Parent polygons with 2km ZOI areas and 2012 offspring points
2011 Parent polygons with 2km ZOI areas and 2012 offspring points: Zoomed
Forest Insect Disturbance Ecology Lab
(new red/dead trees in year t+1) in the same polygon in the next year
surprisingly low (54-68%) in non-immigration years
years
Detection Efficiency
20% 40% 60% 80% 2006 2007 2008 2009 2010 2011 2012 Detection rate (%)
Detection efficiency within parent polygon by infestation year
Results: Relationship between Parent and ZOI Attack intensity: 1 km zone of influence
R² = 0.413 R² = 0.1353 4 8 12 16 4 8 12 16 Average ZOI Attack Intensity (dead/km2) Parent Attack Intensity Classes (dead/km2)
ZOI attack intensity vs Parent Attack intensity (1km ZOI)
Treated Untreated
parents into classes based upon Attack Intensity
be effective in reducing attack intensity in ZOI area
parent attack intensity
R² = 0.4214 R² = 0.0996 4 8 12 16 4 8 12 16 Average ZOI Attack Intensity (dead/km2) Parent Attack Intensity Classes (dead/km2)
ZOI attack intensity vs Parent Attack intensity (2km ZOI)
Treated Untreated
parents into classes based upon Attack Intensity
effective in reducing attack intensity in ZOI area
parent attack intensity Results: Relationship between Parent and ZOI Attack intensity: 2 km zone of influence
relative change from parent to ZOI in treated vs untreated parents
independently (2008 excluded)
excluded
41%
Results: Relative reduction in ZOI Attack intensity: 1 km zone of influence
0% 20% 40% 60% 80% 100% 120% 2007 2009 2010 2011 2012 Reduction in AI
Effect of treatment on ZOI attack intensity
Proportion of infestations treated in each year
2007 2009 2010 2011 2012 17% 31% 6% 14% 29%
33%
Results: Relative reduction in ZOI Attack intensity: 2 km zone of influence
0% 20% 40% 60% 80% 100% 120% 2007 2009 2010 2011 2012 Reduction in AI
Effect of treatment on ZOI attack intensity
Proportion of infestations treated in each year
2007 2009 2010 2011 2012 17% 31% 6% 14% 29%
Forest Insect Disturbance Ecology Lab
effective
dead/km2)
1. Treatment efficacy can be increased with increasing efforts at green attack detection/treatment
DSS/Risk assessment
Ground surveys
r-value surveys
Dispersal bait deployment
Aerial surveys
Green:red surveys Dispersal bait collection Oct.
May – Jun. Jun.– Jul. Aug.– Sep. Sep.
Adapt Do Learn
Control
Proportion of trees treated (P) Years (t) of continued effort to suppress (N=1)
0.80 0.85 0.90 0.95 1.00 10 20 30 40 50 60
R=2 R=3 R=4
N0=10,000 infested trees
From: Carroll et al. 2006
Nt = N0[R(1-P)]t where P > 1-1/R
Proportion of trees treated (P)
0.80 0.85 0.90 0.95 1.00 10 20 30 40 50 60
N0=100,000 infested trees
R=4 R=2 R=3
Forest Insect Disturbance Ecology Lab