oak, fire & mesophicationlakestatesfiresci.net/docs/swmioakwkshop_nowacki...- tap roots exploit...
TRANSCRIPT
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Gregory Nowacki Regional Ecologist
USFS Eastern Region
Oak, Fire & Mesophication
Past, current and future trends of oak in the eastern United States
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Reference: S. Pyne. 2015. Between Two Fires. U of AZ Press, Tucson.
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Oak is a fire- and drought-tolerant genus that possesses various adaptations… Thick bark (fire protection) Able compartmentalizer; rot resistant (fire injury) Aggressive sprouter (fire-based reproductive strategy) Opportunistic: responds favorably to disturbance Fuel characteristics (fire promotion)
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MacMillan, P.C. 1988. Decomposition of coarse woody debris in an old-growth Indiana forest. Canadian Journal of Forest Research 18:1353-1362.
Coarse Woody Debris Decay Rates Oak-Hickory vs. Mesophytes
Coarse Woody Debris Decay Rates Oak = Hickory < Beech < Maple
Coarse Woody Debris Decay Rates Oak = Hickory < Beech < Maple
Coarse Woody Debris Decay Rates Oak = Hickory < Beech < Maple
Coarse Woody Debris Decay Rates Oak = Hickory < Beech < Maple
Slow Fast
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Leaf Differences Oak-Hickory vs. Mesophytes
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Oak is a fire- and drought-tolerant genus that possesses various adaptations … Thick bark (fire protection) Able compartmentalizer (fire injury) Aggressive sprouter (fire-based reproductive strategy) Opportunistic: responds favorably to disturbance Fuel characteristics (fire promotion) Water efficient (drought resistance)
- tap roots exploit deep H2O sources - osmotic adjustment: extract H2O from dry soils
- xeromorphic leaves minimizes H2O loss
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Oak Survival Strategy: heavy investment in root system when young >>> waiting for favorable conditions to bolt!
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In the absence of fire
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In the absence of fire ⇒
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In the absence of fire ⇒ canopy closure
shaded understory conditions
⇓
⇓
⇓
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In the absence of fire ⇒ canopy closure
shaded understory conditions
⇓
⇓
⇓
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In the absence of fire ⇒ canopy closure
shaded understory conditions
⇓
⇓
⇓
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So how big is this problem of altered fire regimes and
“mesophication” in the eastern United States?
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So how big is this problem of altered fire regimes and
“mesophication” in the eastern United States? Shameless
self promotion!
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Group V
Group III Group IV
Group I Group II
0 75 100
200
35
0
Fire Regime Group
Low & Mixed Replacement
Frequent
Infrequent
Rare
Fire Severity (% top-kill)
Fire
Fre
quen
cy (
yrs)
Group II Group I
Group IV Group III
Group V
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Fire Regime Change = Past FR – Current FR
Potential Natural Vegetation map (1 km2 pixels)
Group V
Group III Group IV
Group I Group II
0 75 0
35
200
Fire Severity (% Top-kill)
Fire
Fre
quen
cy (
yrs)
100
Fire Regime Groups
V
III IV
I II
0 75 0
35
200
Fire Severity (% Top-kill)
Fire
Fre
quen
cy (
yrs)
100
Fire Regime Groups
AVHRR-NLCD “hybrid” map (1 km2 pixels)
PNV vs. AVHRR-NLCD change map
(1 km2 pixels)
5
4 3
2 1
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Area burned in the eastern U.S.*
* States from Minnesota to Louisiana eastward.
Post-WWII deployment of men and equipment
to fight fires
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Fire Importance
Mesophication
Dramatic increase of shade-tolerant, mesophytic trees
Decreased flammability due to mesophytic litter & cool, humid microclimate
Fire suppression; canopy closure; increased shade
Pre-1900 Mid-1900s Early 2000s Foreseeable future
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Mesic uplands Ec
osys
tem
sta
te
Conditions
Oak savanna Oak
woodland Oak
forest
a) With fire – historic conditions
Mesophytic hardwoods
Ecos
yste
m s
tate
Conditions
Oak savanna Oak
woodland Oak
forest
b) Without fire – early phases
Mesophytic hardwoods
Ecos
yste
m s
tate
Conditions
Oak savanna Oak
woodland Oak
forest
c) Without fire – mid phases
Mesophytic hardwoods
Ecos
yste
m s
tate
Conditions
Oak savanna Oak
woodland Oak
forest
d) Without fire – late phases
Mesophytic hardwoods
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Xeric uplands Ec
osys
tem
sta
te
Conditions
Oak savanna Oak
woodland Oak
forest Mesophytic hardwoods
a) With fire – historic conditions
Ecos
yste
m s
tate
Conditions
Oak savanna Oak
woodland Oak
forest Mesophytic hardwoods
b) Without fire – early phases
Ecos
yste
m s
tate
Conditions
Oak savanna Oak
woodland Oak
forest Mesophytic hardwoods
c) Without fire – mid phases
Ecos
yste
m s
tate
Conditions
Oak savanna Oak
woodland Oak
forest Mesophytic hardwoods
d) Without fire – late phases
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The demise of fire has been ubiquitous over the eastern U.S.
leading to dire ecological problems in most locations.
Examples
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The Central Pennsylvania
Oak Story
Nowacki, G.J. and M.D. Abrams. 1992. Community, edaphic and historical analysis of mixed oak forests of the Ridge and Valley Province in central Pennsylvania. Canadian Journal of Forest Research 22:790-800.
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The Central Pennsylvania
Oak Story
Nowacki, G.J. and M.D. Abrams. 1992. Community, edaphic and historical analysis of mixed oak forests of the Ridge and Valley Province in central Pennsylvania. Canadian Journal of Forest Research 22:790-800.
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The Central Pennsylvania
Oak Story
Nowacki, G.J. and M.D. Abrams. 1992. Community, edaphic and historical analysis of mixed oak forests of the Ridge and Valley Province in central Pennsylvania. Canadian Journal of Forest Research 22:790-800.
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Fire
Fire
Exploitation: 1775-1900
Presettlement: Oak-Pine-Chestnut-Hickory
Pines selectively removed Hardwoods coppicing
Modern: 1900-today Chestnut blight
Forest conversion!
Year 1908
1913-19 1920-29 1930-39 1940-49 1950-59 1960-69 1970-79 1980-89
Hectares 407,700 108,155 72,378 42,049 21,158 12,784 8,634 3,240 3,388
Pennsylvania Fires
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Disturbance-mediated accelerated succession (Abrams & Nowacki 1992)
Oak succession and habitat changes (Rodewald & Abrams 2002)
So, what to do? Thinning treatments and prescribed burning
Past Present Future>>>
Or simply what happens if stands are harvested in their current state!
This also pertains to blowdown events (Holzmueller et al. 2012).
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Development of Oak savannas, Woodlands, and Forests in Illinois.
Based on the research of:
Roger Anderson, Illinois State Univ.,
Normal, IL.
Anderson (1998)
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Development of Oak savannas, Woodlands, and Forests in Illinois.
Based on the research of:
Roger Anderson, Illinois State Univ.,
Normal, IL.
Anderson (1998)
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Development of Oak savannas, Woodlands, and Forests in Illinois.
Based on the research of:
Roger Anderson, Illinois State Univ.,
Normal, IL.
Anderson (1998)
More shameless
self promotion!
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Anderson (1998)
Fire Vegetation
Topography
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Presettlement Vegetation -- Illinois Prairie Savanna Forest
Current Conditions: Maple invasion!
Anderson 1991
Fire Gradient
European Settlement: Fire cessation & forest expansion
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Vegetation Type/Site
Presettlement Structure
Modern Structure
Oak-hardwoods (terrace)
Density = 155 trees/ha QMD = 42 cm BA = 22 sq m/ha
Density = 457, 311 trees/ha QMD = 23, 35 cm BA = 20, 30 sq m/ha
Oak forest (low north slope)
Density = 146 trees/ha QMD = 36 cm BA = 15 sq m/ha
Density = 438, 345 trees/ha QMD = 26, 32 cm BA = 24, 28 sq m/ha
Oak forest (high north slope)
Density = 144 trees/ha QMD = 36 cm BA = 14 sq m/ha
Density = 425, 377 trees/ha QMD = 25, 30 cm BA = 20, 26 sq m/ha
Oak forest (ridgetop)
Density = 127 trees/ha QMD = 38 cm BA = 14 sq m/ha
Density = 487, NG trees/ha QMD = 25, NG cm BA = 24, 20 sq m/ha
Oak forest (rocky south slope)
Density = 125 trees/ha QMD = 30 cm BA = 9 sq m/ha
Density = 650, 393 trees/ha QMD = 17, 22 cm BA = 15, 15 sq m/ha
Oak forest (south slope)
Density = 144 trees/ha QMD = 36 cm BA = 16 sq m/ha
Density = 506, 415 trees/ha QMD = 22, 25 cm BA = 16, 21 sq m/ha
Structural Changes: Presettlement (1806-07) to Modern (1970s) Fralish et al. 1991
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Vegetation Type/Site
Presettlement Structure
Modern Structure
Oak-hardwoods (terrace)
Density = 155 trees/ha QMD = 42 cm BA = 22 sq m/ha
Density = 457, 311 trees/ha QMD = 23, 35 cm BA = 20, 30 sq m/ha
Oak forest (low north slope)
Density = 146 trees/ha QMD = 36 cm BA = 15 sq m/ha
Density = 438, 345 trees/ha QMD = 26, 32 cm BA = 24, 28 sq m/ha
Oak forest (high north slope)
Density = 144 trees/ha QMD = 36 cm BA = 14 sq m/ha
Density = 425, 377 trees/ha QMD = 25, 30 cm BA = 20, 26 sq m/ha
Oak forest (ridgetop)
Density = 127 trees/ha QMD = 38 cm BA = 14 sq m/ha
Density = 487, NG trees/ha QMD = 25, NG cm BA = 24, 20 sq m/ha
Oak forest (rocky south slope)
Density = 125 trees/ha QMD = 30 cm BA = 9 sq m/ha
Density = 650, 393 trees/ha QMD = 17, 22 cm BA = 15, 15 sq m/ha
Oak forest (south slope)
Density = 144 trees/ha QMD = 36 cm BA = 16 sq m/ha
Density = 506, 415 trees/ha QMD = 22, 25 cm BA = 16, 21 sq m/ha
Structural Changes: Presettlement (1806-07) to Modern (1970s) Fralish et al. 1991
▲ tree density ▼ mean diameter ▲ basal area
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Western Star Oak Flatwoods Houston/Rolla RD, Mark Twain NF
Untreated Thinned, burned
Typical present-day conditions: • Continuous canopy; high density • Shaded understory • Depauperate ground flora • Deep leaf litter
Restored (thin & 5 burns over 15 yrs): • Open canopy; historic density • High-light conditions • Robust & diverse ground flora • Negligible leaf litter
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Western Star Oak Flatwoods Houston/Rolla RD, Mark Twain NF
Untreated Thinned, burned
Typical present-day conditions: • Continuous canopy; high density • Shaded understory • Depauperate ground flora • Deep leaf litter
Restored (thin & 5 burns over 15 yrs): • Open canopy; historic density • High-light conditions • Robust & diverse ground flora • Negligible leaf litter
The herb layer represents >80% of the
total plant species richness of a forest!
(Gilliam 2007)
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Conclusions
• Oak is a pyrogenic (fire-dependent) genus based on tree life histories and physiological characteristics.
• Fire formerly played a significant role
throughout the East! • Fire suppression efforts over the last century
have been extremely effective — to the detriment of fire-dependent plant communities.
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• Fire suppression has had cascading effects, changing openlands to closed forests and allowing fire-sensitive, shade-tolerant species to prosper (esp. maples) at the expense of oaks.
• Prescribed burning and thinning is needed in
order to maintain oak communities (including attendant ground flora!).
• Opportunities for restoring pyrogenic ecosystems
are rapidly waning…
Conclusions
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The shared materials are not new observations, nor are the remedies rocket science.
Oak succession, primarily to maples Dix 1957: detected in DC forests
What’s the principal problems/limitations? Carvell and Tryon 1961 1) Lack of sunlight reaching the forest floor 2) Lack of disturbance (thinning, grazing &
burning)
Dix, R.L. 1957. Sugar maple in forest succession at Washington, D.C. Ecology 38:663-665.
Carvell, K.L. and E.H. Tryon. 1961. The effect of environmental factors on the abundance of oak regeneration beneath mature oak stands. Forest Science 7:98-105.
What’s the solution? Thinning and burning!
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Questions? Questions?
Questions?
Questions?
Questions? Questions?