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The Fire Ecology of Big Sur and
  the Central Coast Ranges

            Les Rowntree
  Morro Bay Natural History Museum
           March 21, 2011
Today’s Talk
Big Sur Overview

Resources for Fire
Ecology

Fire Ecology 101: 4
important points

Fire History (the last
20,000 years)

The 2008 Big Sur
Basin Complex Fire
Vegetation Communities
       of Big Sur
Micro-climate         Chamise chaparral
gradients: Both
elevation and coast   Coastal redwoods
to inland
                      Mixed redwoods and
Central Coast Scrub   hardwoods

Maritime chaparral    Other conifers (both
                      pine and fir)
Coast Range
grasslands            Oak woodlands
Reference Point: The Basin Complex Fire,
June 21 - July 27 2008




                        inversion with fog layer below
University of California
         Press
$5.00 (Free to Members)

VOL. 35, NO. 4 • FALL 2007




FREMONTIA
JOURNAL          OF     THE   CALIFORNIA   NATIVE   PLANT   SOCIETY




                                           SPECIAL ISSUE: CHAPARRAL
                                               CALIFORNIA CHAPARRAL
                                                        MANZANITAS
                                   FREEZING AND CHAPARRAL PATTERNS
                                                 CHAPARRAL AND FIRE
                                            CHAPARRAL BULBS AND FIRE
                                  THE COST OF LIVING WITH CHAPARRAL
                       POST-FIRE RECOVERY OF CHAPARRAL IN SAN DIEGO




  VOLUME 35:4, FALL 2007
Heyday Press
photo by David McNew
Fire Ecology 101 (1)
A wide range of plant and plant
community responses to fire:
       Fire Dependent: plants need fire to
       reproduce (knobcone and Bishop pines)

       Fire Enhanced: plants expand population
       with fire, but also reproduce without it
       (oaks)

       Fire Neutral: fires neither expand or limit
       plant populations (Douglas fir)

       Fire Inhibited: fire is detrimental to plants
       (Santa Lucia fire)
mature seed tree




7-year old Bishop pine seedlings
Fire Ecology 101 (2)
Plants and plant populations are adapted
not to fire itself but, instead, to fire
regimes
   A fire regime is the frequency, magnitude,
   spatial extent, and seasonality of a series of
   fires
   Magnitude is intensity (amount of energy
   released) and severity (impact on the
   ecosystem
Fire Ecology 101 (3a)
Fire affects individual plants directly
and indirectly
     Direct effects on the individual are a
     function of fire behavior and individual
     plant’s morphology and physiology
         Morphology refers to plant structure (shape,
          height, placement of seeds and buds, root
          structure)

         Physiology refers to production and
          regulation of chemicals within plant tissue
Fire Ecology 101 (3b)
Indirect effects are the changes in the
physical and chemical environment of the
surrounding environment in terms of
nutrients, light, soil substrate and
chemistry, and microclimate of the plant
community.
   These changes can differentially affect
   sprouting, growth, colonization, and
   establishment of varied species
colonization, and establishment of varied speciesThese
changes can differentially affect sprouting, growth, colonization,

and   Fire Ecology 101 (4a)                                   of


 Seeding and sprouting are the main ways
 plants and trees recover from (and,
 through time, adapt to) fire
      Some species such as chamise actually do both,
      spread seed AND root sprout

      Additionally, within the chaparral community,
      some species of the two major genera,
      Arctostaphylos and Ceanothus, spread seeds while
      other species root sprout

      Redwoods also both seed and/or sprout after a
      fire
chamise seedlings and stump sprouting
manzanita, Lick Fire (Lee Dittman photos)
Chaparral Seeders Lose While
Sprouters Gain When Fire Frequency
Increases (4b)
  Although chaparral is thought of as a fire enhanced
  community, it can suffer and actually diminish as fire
  regimes change

  Shrubs dependent on fire-cued seed germination were
  most sensitive to frequent fire and lost substantial
  cover to other functional types, including drought-
  deciduous sub-shrubs that typify coastal sage scrub and
  nonnative annual grasses. (Keeley)

       Seed banks needing a certain amount of time to age in the
       soil before they can germinate.

       Chaparral seeds don’t respond to heat itself but rather to
       gasses in smoke. That may be true of other seeders too
Changing Fire Regimes
End of Pleistocene (Ice Age) and
before humans, 20 - 12,000 bp.
Period of “natural fire”
Early to late Holocene, 12,000 bp to
1769; period of Native American
burning
Modern historical period, from
Spanish missions to present day
- 20,000 bp. Last Glacial
                          Maximum (LGM)
                          - Dry summer
                          Mediterranean climate
                          - Sea level ~ 400 ft lower
                          - All plant species
                          represented, but in
art by Laura Cunningham   different configurations
                          and with different
                          distributions
                          - No humans in CA (as far
                          as we know)
                          - Lightning and volcanoes
                          only source of ignition
Period of Native American
Burning, 12,000 bp - 1769 CE
Climate warms (with
some fluctuations) to
current state

Warmest period 8 -3 kya

Sea level rises to current
state ~ 4000 bp

Grazing megafauna
extinct (change in
grasslands?)
Period of Native American
Burning, 12,000 bp - 1769 CE
 How and what do we know about Indian
 burning?
 Danger of conflating what little we know
 into all-encompassing generalizations
 Native Americans cultures changed
 continually during this long period of time,
 thus reasonable to assume their strategies
 and methods of burning also changed
Period of Native American
Burning, 12,000 bp - 1769 CE
 Reasons for burning: encourage specific plant
 species; eliminate competiting species; clean up
 the landscape by ridding it of pests, brush, and
 snags; fire used to expand grassland habitat for
 hunted animal and bird species; enhance fertility
 by recycling nutrients; encourage acorn growth
 and harvest, etc.
 Result: pyrodiversity from frequent low intensity
 fires
 Environments most changed: grassland/shrub
 interface; oak woodlands; perhaps chaparral
Effects of Indian Burning
         on Big Sur

Three groups: Ohlone; Esselen; Salinan
Currently, earliest dates for Big Sur ~
5000 bp
Inferences about settlement patterns
and density
Conjecture regarding effects on plant
communities vegetation communities
Spanish Mission Period,
         1769-1830

Introduction of
livestock and field
crops to Coast Ranges

Exotic annual grasses

Disruption of Native
American society

Ban on Indian burning,
1793
Effects of Spanish
   Settlement on Big Sur
Native Americans close
to San Antonio and
Carmel missions most
effected

Possibility of remnant
groups of Indians in the
Big Sur interior

Effect on plant
communities? Grassland
change begins. Oak
woodlands and animals
Mexican Rancho Period,
       1830-1850
Burning resumes with
pasture-improvement
mentality

Livestock expands with
hide and tallow
economy

Common that Native
Americans act as labor
force with cattle herds
Mexican Rancho Period,
       1830-1850
Early American
settlers appear,
logging redwoods,
harvesting tanoak,
making charcoal for
iron forges

All of these activities
increase incidence of
fire in Coast Ranges
and enhance grassland
species change
Early American Period,
            1850-1906
Might have been period
of greatest burning in
Coast Ranges

And also greatest change
in plant communities
with exotic species
spreading rapidly in grass
and shrub lands, aided by
fire and plowed fields

Sheep, cattle, and wheat
cultures all burned grass
and shrub lands              The wild and wooly West
Logging in Coast Range Also Responsible
  for Burning, Intentional and Accidental
Fires set to clear slash away,
facilitate transport of logs,
and open forest for tanbark
harvesting
Effects in Big Sur
Big Sur isolated with only connections via ship, coastal trail to
Monterey, and southern connection to Salinas Valley

Some redwood logging

Wheat cultivation on northern marine terraces (Palo Colorado)

May not have been much free range livestock because of
topography

Earliest settlers had different attitudes about using fire to clear
pasture

Large fires recorded in newspapers. In 1894, reports of a fire
“burning for weeks” covering upper watersheds of central
Santa Lucia mountains. Around 50,000 acres burned in
human-caused fire in July 1903, and 150,000 acres in 1906
Fire Prevention and Suppression
Begins in the Coast Ranges, 1906
1906, Monterey and San Luis Obispo forest reserves
created. These became national forests in 1907

    1919, merger of Monterey, SLO, and Santa
    Barbara national forests into SBNF

    1938, name changed to Los Padres NF

Although fire prevention and suppression are policy,
question is whether this was effective right away

If so, the incidence of fires lessened, and fuel buildup
begins. Or did happen only later?
Changes to NF fire prevention in the
1930s:
   • Trucks replace horses
      Work begun on N-F road
     and Highway 1 in 1931
   • Lookout system
      3 in Big Sur area of LPNF
   • CCC labor for prevention and
   suppression
   • Argument can be made that
   effective fire suppression only
   began in 1930s
Changing Fire Regimes
     in Big Sur
According to USFS
records, the average
figure for acreage
burned changed from
6700 acres in pre-war
years to 400 acres in
the 1960s

Did this lead to a fuel
build up that fueled
more recent large
fires?
Recent Big Sur Fires
2008, Basin-Indians   1977, Marble-Cone.
Complex. (162,818 +   178,000 acres
81,378 acres)
                      1970, Buckeye.
1999, Kirk Complex.   60,000 acres
87,000 acres
                      (lightning-ignited)
1985, Rat Creek-
Gorda. 80,000 acres
The Basin
    Complex Fire,
    June 21 - July
       27, 2008




photo by Eric
https://picasaweb.google.com/eneitzel/
BasinComplex#
Basin Complex Fire
California lightning event produced 6000
ground strikes, resulting in 1000 fires in
northern CA
Early in the fire season
Followed two years of drought that
resulted in dry fuel throughout Big Sur
Changing wind and humidity conditions
during month of fire
map of two fires, Gallery and Basin, 4 days into
the event
Fire retardant
       and
  watersheds
(and steelhead)
Rizzo Lab,
UC Davis
SOD did not increase intensity in all
plots; canopy vs ground fires
September 2, 2008

      and

  April 6, 2009
September 2, 2008
       and
   June 6, 2009
  Bottchers Gap
September 2, 2008
      and
   May 5, 2009
September
2008


    April 2009
June 2010
June 2010
April 2009
Fuelbreaks and firelines
Fire ecology of big sur; March 2011
Fire ecology of big sur; March 2011
Fire ecology of big sur; March 2011
Fire ecology of big sur; March 2011
Fire ecology of big sur; March 2011
Fire ecology of big sur; March 2011
Fire ecology of big sur; March 2011
Fire ecology of big sur; March 2011

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Fire ecology of big sur; March 2011

  • 1. The Fire Ecology of Big Sur and the Central Coast Ranges Les Rowntree Morro Bay Natural History Museum March 21, 2011
  • 2.
  • 3. Today’s Talk Big Sur Overview Resources for Fire Ecology Fire Ecology 101: 4 important points Fire History (the last 20,000 years) The 2008 Big Sur Basin Complex Fire
  • 4.
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  • 8.
  • 9. Vegetation Communities of Big Sur Micro-climate Chamise chaparral gradients: Both elevation and coast Coastal redwoods to inland Mixed redwoods and Central Coast Scrub hardwoods Maritime chaparral Other conifers (both pine and fir) Coast Range grasslands Oak woodlands
  • 10.
  • 11.
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  • 13. Reference Point: The Basin Complex Fire, June 21 - July 27 2008 inversion with fog layer below
  • 15.
  • 16. $5.00 (Free to Members) VOL. 35, NO. 4 • FALL 2007 FREMONTIA JOURNAL OF THE CALIFORNIA NATIVE PLANT SOCIETY SPECIAL ISSUE: CHAPARRAL CALIFORNIA CHAPARRAL MANZANITAS FREEZING AND CHAPARRAL PATTERNS CHAPARRAL AND FIRE CHAPARRAL BULBS AND FIRE THE COST OF LIVING WITH CHAPARRAL POST-FIRE RECOVERY OF CHAPARRAL IN SAN DIEGO VOLUME 35:4, FALL 2007
  • 18.
  • 19. photo by David McNew
  • 20. Fire Ecology 101 (1) A wide range of plant and plant community responses to fire: Fire Dependent: plants need fire to reproduce (knobcone and Bishop pines) Fire Enhanced: plants expand population with fire, but also reproduce without it (oaks) Fire Neutral: fires neither expand or limit plant populations (Douglas fir) Fire Inhibited: fire is detrimental to plants (Santa Lucia fire)
  • 21. mature seed tree 7-year old Bishop pine seedlings
  • 22.
  • 23. Fire Ecology 101 (2) Plants and plant populations are adapted not to fire itself but, instead, to fire regimes A fire regime is the frequency, magnitude, spatial extent, and seasonality of a series of fires Magnitude is intensity (amount of energy released) and severity (impact on the ecosystem
  • 24.
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  • 26. Fire Ecology 101 (3a) Fire affects individual plants directly and indirectly Direct effects on the individual are a function of fire behavior and individual plant’s morphology and physiology Morphology refers to plant structure (shape, height, placement of seeds and buds, root structure) Physiology refers to production and regulation of chemicals within plant tissue
  • 27. Fire Ecology 101 (3b) Indirect effects are the changes in the physical and chemical environment of the surrounding environment in terms of nutrients, light, soil substrate and chemistry, and microclimate of the plant community. These changes can differentially affect sprouting, growth, colonization, and establishment of varied species
  • 28.
  • 29.
  • 30. colonization, and establishment of varied speciesThese changes can differentially affect sprouting, growth, colonization, and Fire Ecology 101 (4a) of Seeding and sprouting are the main ways plants and trees recover from (and, through time, adapt to) fire Some species such as chamise actually do both, spread seed AND root sprout Additionally, within the chaparral community, some species of the two major genera, Arctostaphylos and Ceanothus, spread seeds while other species root sprout Redwoods also both seed and/or sprout after a fire
  • 31. chamise seedlings and stump sprouting manzanita, Lick Fire (Lee Dittman photos)
  • 32.
  • 33. Chaparral Seeders Lose While Sprouters Gain When Fire Frequency Increases (4b) Although chaparral is thought of as a fire enhanced community, it can suffer and actually diminish as fire regimes change Shrubs dependent on fire-cued seed germination were most sensitive to frequent fire and lost substantial cover to other functional types, including drought- deciduous sub-shrubs that typify coastal sage scrub and nonnative annual grasses. (Keeley) Seed banks needing a certain amount of time to age in the soil before they can germinate. Chaparral seeds don’t respond to heat itself but rather to gasses in smoke. That may be true of other seeders too
  • 34. Changing Fire Regimes End of Pleistocene (Ice Age) and before humans, 20 - 12,000 bp. Period of “natural fire” Early to late Holocene, 12,000 bp to 1769; period of Native American burning Modern historical period, from Spanish missions to present day
  • 35. - 20,000 bp. Last Glacial Maximum (LGM) - Dry summer Mediterranean climate - Sea level ~ 400 ft lower - All plant species represented, but in art by Laura Cunningham different configurations and with different distributions - No humans in CA (as far as we know) - Lightning and volcanoes only source of ignition
  • 36. Period of Native American Burning, 12,000 bp - 1769 CE Climate warms (with some fluctuations) to current state Warmest period 8 -3 kya Sea level rises to current state ~ 4000 bp Grazing megafauna extinct (change in grasslands?)
  • 37. Period of Native American Burning, 12,000 bp - 1769 CE How and what do we know about Indian burning? Danger of conflating what little we know into all-encompassing generalizations Native Americans cultures changed continually during this long period of time, thus reasonable to assume their strategies and methods of burning also changed
  • 38. Period of Native American Burning, 12,000 bp - 1769 CE Reasons for burning: encourage specific plant species; eliminate competiting species; clean up the landscape by ridding it of pests, brush, and snags; fire used to expand grassland habitat for hunted animal and bird species; enhance fertility by recycling nutrients; encourage acorn growth and harvest, etc. Result: pyrodiversity from frequent low intensity fires Environments most changed: grassland/shrub interface; oak woodlands; perhaps chaparral
  • 39. Effects of Indian Burning on Big Sur Three groups: Ohlone; Esselen; Salinan Currently, earliest dates for Big Sur ~ 5000 bp Inferences about settlement patterns and density Conjecture regarding effects on plant communities vegetation communities
  • 40. Spanish Mission Period, 1769-1830 Introduction of livestock and field crops to Coast Ranges Exotic annual grasses Disruption of Native American society Ban on Indian burning, 1793
  • 41. Effects of Spanish Settlement on Big Sur Native Americans close to San Antonio and Carmel missions most effected Possibility of remnant groups of Indians in the Big Sur interior Effect on plant communities? Grassland change begins. Oak woodlands and animals
  • 42. Mexican Rancho Period, 1830-1850 Burning resumes with pasture-improvement mentality Livestock expands with hide and tallow economy Common that Native Americans act as labor force with cattle herds
  • 43. Mexican Rancho Period, 1830-1850 Early American settlers appear, logging redwoods, harvesting tanoak, making charcoal for iron forges All of these activities increase incidence of fire in Coast Ranges and enhance grassland species change
  • 44. Early American Period, 1850-1906 Might have been period of greatest burning in Coast Ranges And also greatest change in plant communities with exotic species spreading rapidly in grass and shrub lands, aided by fire and plowed fields Sheep, cattle, and wheat cultures all burned grass and shrub lands The wild and wooly West
  • 45. Logging in Coast Range Also Responsible for Burning, Intentional and Accidental Fires set to clear slash away, facilitate transport of logs, and open forest for tanbark harvesting
  • 46. Effects in Big Sur Big Sur isolated with only connections via ship, coastal trail to Monterey, and southern connection to Salinas Valley Some redwood logging Wheat cultivation on northern marine terraces (Palo Colorado) May not have been much free range livestock because of topography Earliest settlers had different attitudes about using fire to clear pasture Large fires recorded in newspapers. In 1894, reports of a fire “burning for weeks” covering upper watersheds of central Santa Lucia mountains. Around 50,000 acres burned in human-caused fire in July 1903, and 150,000 acres in 1906
  • 47. Fire Prevention and Suppression Begins in the Coast Ranges, 1906 1906, Monterey and San Luis Obispo forest reserves created. These became national forests in 1907 1919, merger of Monterey, SLO, and Santa Barbara national forests into SBNF 1938, name changed to Los Padres NF Although fire prevention and suppression are policy, question is whether this was effective right away If so, the incidence of fires lessened, and fuel buildup begins. Or did happen only later?
  • 48. Changes to NF fire prevention in the 1930s: • Trucks replace horses Work begun on N-F road and Highway 1 in 1931 • Lookout system 3 in Big Sur area of LPNF • CCC labor for prevention and suppression • Argument can be made that effective fire suppression only began in 1930s
  • 49. Changing Fire Regimes in Big Sur According to USFS records, the average figure for acreage burned changed from 6700 acres in pre-war years to 400 acres in the 1960s Did this lead to a fuel build up that fueled more recent large fires?
  • 50. Recent Big Sur Fires 2008, Basin-Indians 1977, Marble-Cone. Complex. (162,818 + 178,000 acres 81,378 acres) 1970, Buckeye. 1999, Kirk Complex. 60,000 acres 87,000 acres (lightning-ignited) 1985, Rat Creek- Gorda. 80,000 acres
  • 51.
  • 52. The Basin Complex Fire, June 21 - July 27, 2008 photo by Eric https://picasaweb.google.com/eneitzel/ BasinComplex#
  • 53. Basin Complex Fire California lightning event produced 6000 ground strikes, resulting in 1000 fires in northern CA Early in the fire season Followed two years of drought that resulted in dry fuel throughout Big Sur Changing wind and humidity conditions during month of fire
  • 54. map of two fires, Gallery and Basin, 4 days into the event
  • 55.
  • 56.
  • 57. Fire retardant and watersheds (and steelhead)
  • 58.
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  • 63. SOD did not increase intensity in all plots; canopy vs ground fires
  • 64. September 2, 2008 and April 6, 2009
  • 65.
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  • 67.
  • 68. September 2, 2008 and June 6, 2009 Bottchers Gap
  • 69. September 2, 2008 and May 5, 2009
  • 70. September 2008 April 2009
  • 72.
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