Understanding Fire Regimes in Rocky Mountain Conifer Ecosystems
This resource delves into the fire ecology of Rocky Mountain mixed conifer forests, focusing on various fire regimes, their components, and historical vs. modern contrasts. Topics include fire frequency, severity, and the ecological roles of species like Ponderosa pine and Douglas-fir. The implications of land use changes, fire suppression, and resultant shifts in vegetation are highlighted. This session will impact understanding of ecosystem management, fire behavior, and conservation strategies. Powerpoints are available on the class website.
Understanding Fire Regimes in Rocky Mountain Conifer Ecosystems
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Presentation Transcript
CLASS UPDATES • Office hours: Fridays 9AM-12noon (or email me for an appointment) • Powerpoints – on class website • Schedule changes: thesis statement, outline, first draft • Exams – will be returned on Thursday • Quiz Thursday (today’s lecture/discussion only)
Fire Ecology:Rocky Mountain Mixed Conifer Forests NREM390 October 5, 2010
Fire Regimes: Review • Components of fire regimes • Extent • Frequency • Seasonality • Intensity • Duration • Severity • Historic vs. Modern Fire Regime?
Fire classification:severity and frequency (return interval) • Short fire return intervals (<20 years) • Low-severity surface fires are common . • Fire tolerant herbaceous species or shrubs dominate. • Species composition often similar. • Intermediate fire return intervals (20-75 years) • Fuel buildup and continuous in distribution • Moderate-severity fires (patchy crown fires) or some high-severity fires • Greater changes in plant composition • Long fire return intervals (>100 years) • Very high fuel loads possible • High-severity fire commonly occur (stand-replacing crown fires) • Postfire & prefire vegetation can be very different • Mixed-severity fires • Combination of frequent low-severity & infrequent high severity fires
How do historical (pre-settlement) and modern (current) fire regimes differ – and why? • In ecosystems with high frequency, low intensity fire regimes (e.g., dry forests, grasslands, woodlands, savannas): • Significant changes to fire regime due to: • Land use change (agriculture, urban) • Fire suppression and fuel accumulation • Change in vegetation type and structure • Forests with low frequency, high severity stand-replacing fire regimes: • Much less change from historical fire regimes – Why?
Fire regimes in Rocky Mountain Conifer Ecosystems Spruce-Fir 9,000-11,000 ft Lodgepole pine (aspen, spruce-fir) 8,000-9,000 ft Alpine Meadows >11,000 ft Ponderosa pine 5,500-6,500 ft Short- grass steppe <5,500 ft Douglas-fir mixed conifer 6,500-8,000 ft.
Ponderosa Pine: Ecology • Shade intolerant • Early successional • Fire resistant • Thick bark • Seedlings > 5 yr. old • Mast seeding (episodic)
Ponderosa pine: fire regime • Fire frequency: 5-30 yrs. • Light surface fires • Regeneration: • Patches of old trees crown fire & seed bed • Mast year + fire-free period • 1900s: grazing & fire suppression • Many seedlings survive • Fuel build up • High severity, stand-replacing fires
Ponderosa pine: Low intensity, frequent surface fires (historic) Stand-replacing fires
Fire regimes in Rocky Mountain Conifer Ecosystems Spruce-Fir 9,000-11,000 ft Lodgepole pine (aspen, spruce-fir) 8,000-9,000 ft Alpine Meadows >11,000 ft Ponderosa pine 5,500-6,500 ft Short- grass steppe <5,500 ft Douglas-fir mixed conifer 6,500-8,000 ft.
Douglas-fir, mixed conifer: Ecology • Intermediate shade tolerance • Early successional • Seedlings can establish on moist, cool sites • Late successional • Understory of Ponderosa Pine • Understory of Lodgepole Pine • Intermediate fire resistance • mature trees only
Douglas-fir: fire regime • Historic: Mixed fire severity • Light surface fires, 20-60 yr. • Severe stand-replacing fires, >60 yr. • Fire suppression shade tolerant species • Douglas-fir seedlings • Hemlock, white spruce, blue spruce (low fire resistance) • Shift: increased mixed-conifer forests on landscape • Favors high severity, stand-replacing fires
Fire regimes in Rocky Mountain Conifer Ecosystems Spruce-Fir 9,000-11,000 ft Lodgepole pine (aspen, spruce-fir) 8,000-9,000 ft Alpine Meadows >11,000 ft Ponderosa pine 5,500-6,500 ft Short- grass steppe <5,500 ft Douglas-fir mixed conifer 6,500-8,000 ft.
Lodgepole pine: Ecology • Shade intolerant • Early successional • Intermediate fire resistance • Serotiny • Young trees – low serotiny • Old trees – low serotiny (high elevations with low fire frequency • Intermediate age – high serotiny • requires intense ground fires • Melt resin • Exposed mineral soil (seed bed) http://www.cfr.washington.edu/Classes.esc.202/LPBarkBFireRot.htm
Lodgepole pine: fire regime • Mixed severity fire regime • Low-intensity surface fires, 50-100 yr. • Fuel characteristics • Topography & Weather • Stand-replacing fires, 100-400 yr. • Climate driven • drought, winds • Fire suppression • Understory: spruce, fire (low fire resistance) • Low impact on fire dynamics • Altitudinal gradient: Rockies • Moisture, temperature • Biomass accumulation
Fire regimes in Rocky Mountain Conifer Ecosystems Spruce-Fir 9,000-11,000 ft Lodgepole pine (aspen, spruce-fir) 8,000-9,000 ft Alpine Meadows >11,000 ft Ponderosa pine 5,500-6,500 ft Short- grass steppe <5,500 ft Douglas-fir mixed conifer 6,500-8,000 ft.
Relatively • rapid regeneration: • Lodgepole pine • Aspen • Spruce • Fir
High-Elevation Spruce-Fir ecosystems (10,000-11,000 ft)
Ecosystems & fire regimes Lodgepole pine, Spruce-Fir Douglas-fir mixed conifer Ponderosa pine Pinyon- Juniper Tallgrass prairie Short grass steppe / Sagebrush
Low severity Low severity Low to moderate severity Low to moderate severity Mixed severity Fuel load • < 60 yrs • > 100yrs • 50-100 yrs • > 400 yrs 4-36 yrs < 100 yrs 1-5 yrs Fuel load 20-50 yrs Weather, fuel load, topography < 10 yrs < 100 yrs Weather, fuel load, topography Weather, fuel load, topography Fire regimes Weather, fuel load, topography Weather
Lodgepole Pine regeneration after the 1988 Yellowstone Fires Pre-Fire Cougar Creek Yellowstone Lake Post-Fire * Effect of patch size on LP regeneration: Large > Small * Effect of fire severity on LP regeneration: ground fires > crown & surface
Fire and Ecosystem Heterogeneity • Mosaic pattern – “patchiness” • Fire intensity • Burned area • Microclimate variation • Light • Moisture • Nutrients • Species composition & diversity • Different microclimate requirements • Different regeneration strategies • Ecosystem diversity • Successional communities • Dynamic equilibrium (landscape scale)
Other examples of post-fire heterogeneity • Herbaceous vegetation • Light (larger patches) • Seed dispersal high • Aspen • Root suckering (low fire intensity) • Regeneration by seed (woody debris – elk browse) • Spruce-fir • Distance to seed trees • Shade, moisture • Wildlife • Mosaic of different habitats • Increased abundance of food
Initial vegetation cover: Lodgepole pine Probably ground fires, some mortality, new seedlings, mixed-age LP stand No fire until 300 yrs. Mixed LP, spruce-fir, crown fire, slow regen Fire every ~100 yrs. Probably surface fires, high survival no new regeneration, dense LP stand Fire every ~40-50 yrs.