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Fire Modeling and Risk PreventionOrinda, CA
Katie McKnight | Kirsten Jurich
• Mitigation Objectives
• Research Question
• Rationale
• Study Site
• Assumptions and Limitations
• Data Analysis & Results
• Findings
• Recommendations
TABLE OF CONTENTS
• Perform a high-resolution simulation of mitigation measures specific to the Sleepy Hollow region of Orinda
OBJECTIVES
• Results can be used to assess effectiveness of mitigation measures and inform concerned homeowners and future fire mitigation strategies
RESEARCH QUESTION
What impact would pine tree removal have on fire vulnerability for Sleepy Hollow homeowners?
Photo Source: disasterandemergencysurvival.com
• Tallest pine trees likely closer to death than shorter
pines
• Dead pines pose large fire risk to the community
• If pine trees on the verge of death were
removed, how would that change the fire
potential?
RATIONALE
BARK BEETLES
STUDY SITE
Grove of pines
• 24.7-acre study site chosen• DSM - DEM = nDSM • Query: 69 to 125 feet • Digitized unburnable vs. burnable zones and fuel types• Used street view in Google Earth to verify locations• About 1.4 acres of pine trees
Corner of Normandy Ln. and Sleepy Hollow Ln.
METHODOLOGY
600’
View from study site
Two scenarios analyzed in FlamMap:
1. Existing Condition (unchanged fuel model)
2. Pine Mitigation (fuel model changed from class 10 to 1 in pine locations)
METHODOLOGY
• Flame Length (feet)
• Crown Fire Activity (class)
• Heat per Unit Area (kJ/m2)
• Rate of Spread (chains/hr)
Variables measured:
• Spatial changes (ArcGIS)
• Histogram comparisons (Excel)
Data Analysis:
FUEL MODELS: land use type
Existing Condition Pine Mitigation
600’
FUEL MODELS: land use type
Existing Condition Pine Mitigation
600’
ASSUMPTIONS & LIMITATIONS
• Wind blowing uphill at 20 feet above surface at 35 mph
• Fuel moisture, aspect, elevation, slope and canopy cover inputs adapted from Claremont
Canyon dataset provided
• “Near-death” pines assumed to be within 69’ - 125’ height range
• Verifications of pines made through Google Earth Pro street view
CROWN FIRE ACTIVITY: class
Existing Condition Pine Mitigation
600’
• Assessment of changes in crown fire activity (CFA) over entire study area
• 2 %, or 0.5 acres, of total study area shifted from active crown fire (class 3) to surface fire (class 1)
HEAT PER UNIT AREA: kJ/m2
Existing Condition Pine Mitigation
600’
• Assessment of changes in heat per unit area (HUA) over entire study area
• Of the area affected by mitigation, largest reduction in HPU between -15,000 to -20,000 kJ/m2 (-48%)
• Second largest reduction in HPU between -60,000 to -65,000 kJ/m2 (-33%)
RATE OF SPREAD: chains per hour
Existing Condition Pine Mitigation
600’
• Changes likely due to shift in land use from tree canopy to grass (quicker burn)
• ROS between 70 to 80 chains per hour decreased by 38%, but increased by 10% between 30 to 40 c/hr
FLAME LENGTH: feet
Existing Condition Pine Mitigation
600’
• Assessment of changes in flame length over entire study area
• Reduction of: 60’ - 70’ flames over 0.4 acres 70’ - 80’ flames over 0.2 acres 80’ - 90’ flames over 0.1 acres 90’ - 100’ flames over 0.03 acres
• Increase in: 0’ - 10’ flames over 0.7 acres
• Tree removal of near-death pines can greatly reduce flame length, rate of spread, heat per
burned area and crown fire activity
• Effects of pine tree removal include:
FINDINGS
• shift in crown fire activity from active crown fire to surface fire
• overall reduction of heat per unit area by 47,000,000 kJ/m2
• overall decreases in high rates of spread at dangerous intervals (60 - 100 chains per
hour) to more manageable rates of spread (0 - 20 chains per hour)
• reduction from very large flame lengths (between 60 - 100 feet) to moderate flame
lengths (0 - 10 feet)
• Alert fire officials to potential bark-beetle related tree deaths
RECOMMENDATIONS
• Community outreach to train homeowners in identifying indicators of bark beetle
infestations
• Crowd-sourcing application to monitor affected areas
• Expedited permitting process for removal of infested pine trees