fire ecology of the southern great plainsfireecology.okstate.edu/...fire-ecology-0805am.pdf · fire...

Post on 08-Jul-2020

4 Views

Category:

Documents

0 Downloads

Preview:

Click to see full reader

TRANSCRIPT

Fire Ecology of the Southern Great Plains

Jim AnsleyCharles Taylor

Rangeland Ecology and Management

Texas A&M University

Dave Engle

Natural Resource Ecology and Management

Iowa State University

Sam FuhlendorfJohn Weir

Terry Bidwell

Natural Resource Ecology and Management

Oklahoma State University

http://gisdata.usgs.net/website/MRLC/viewer.php

Southern Great Plains

Southern Great PlainsOutline

1.Fire Sensitive Trees – Ashe Juniper and Eastern Redcedar

2.Resprouting Shrubs and Trees – Shinnery oak, Sand sagebrush, Plum, Sumac, Mesquite, Live Oak, Post Oak

3.Grasslands- Tall-, Mixed- & Short-grass Prairies

4.Controlling factors of fire effects

http://gisdata.usgs.net/website/MRLC/viewer.php

Fire Sensitive Trees

1900 20201950 2000Year

WoodlandGrassland/Savanna

Woody P

lant Cover (%

)

0

40

80

Increasers

Decreasers

Gra

ssla

ndC

ondi

tion

Gra

ssla

ndC

ondi

tion

Gra

ssla

ndC

ondi

tion

Fire

Ani

mal

Uni

ts/S

ectio

n

0

20

40

60

80

100

120

140

160

Historical Stocking Rate DeclineSonora Experiment Station

JuniperSize and Density

SeedDispersal

SeedProduction

Mortality

Mid-Grass

Short-Grass

Grazing

HerbaceousBiomass

FireIntensity

FireFrequency

Landscape Dynamics(Fuhlendorf et al. 1996)

Patch DynamicsWeatherPatterns

Fuhlendorf et al. 1996Fuhlendorf et al. in review

Year0 20 40 60 80 100 120 140H

erba

ceou

s B

iom

ass

(per

cent

of m

axim

um)

0

10

20

30

40

50

60

70

80

90

100

Larg

e Tr

ees/

ha (>

6m d

ia.)

0

10

20

30

40

50

60

Ungrazed and No Fire

Remaining Herb. BiomassTree Density

Potential Herb. Biomass

Ungrazed with a 10 year fire frequency

Remaining Herbaceous BiomassTree Density

Potential Herbaceous Biomass

Year0 20 40 60 80 100 120 140H

erba

ceou

s B

iom

ass

(per

cent

of m

axim

um)

0

10

20

30

40

50

60

70

80

90

100

Larg

e Tr

ees/

ha (>

6m d

ia.)

0

10

20

30

40

50

60

0Year 10 Year 20 Year 30 Year 40

Year of first fire

No Grazing with a 10 year fire frequencyBiomass Remaining after 150 years

XX

X

XBio

mas

s R

emai

ning

(%)

100

50

Timing of the first fire is critical

75

25

Fire-sensitive woody plants Summary

• Ashe Juniper on Low Prod. site (Sonora TX)– Without fire, JUAS dominance in about 60 yr– Without grazing = 15 year fire return interval– Moderate grazing = 5 year fire return interval – Heavy grazing = sell the farm? or extreme fire

• Eastern Redcedar -High Prod. site (Stillwater OK)

– Without fire, JUVI dominance in about 45 yr– Without grazing = 10 year fire return interval– Moderate grazing = 10 year fire return interval – Heavy grazing = 2-3 year fire return interval

• Ashe Juniper on Low Prod. site (Sonora TX)– Without fire, JUAS dominance in about 60 yr– Without grazing = 15 year fire return interval– Moderate grazing = 5 year fire return interval – Heavy grazing = sell the farm? or extreme fire

• Eastern Redcedar -High Prod. site (Stillwater OK)

– Without fire, JUVI dominance in about 45 yr– Without grazing = 10 year fire return interval– Moderate grazing = 10 year fire return interval – Heavy grazing = 2-3 year fire return interval

http://gisdata.usgs.net/website/MRLC/viewer.php

Resprouting shrubs and trees

Oak savanna annual burn

Photo by John Weir

Briggs et al. 2005

Fire Frequency on Tallgrass PrairieRhus glabra, Cornus durmmundii, Prunus americana

Cross Timbers of Texas, Oklahoma & KansasWithout fire

Cross Timbers of Texas, Oklahoma & KansasWithout fire

4-yr fire return interval4-yr fire return interval

2-yr fire return interval2-yr fire return interval 1-yr fire return interval1-yr fire return interval

3-yr fire return interval3-yr fire return interval

Photo by John Weir

2 year burn frequency

No burn- control

5 year burn frequency

Photo by John Weir

Photos by Jim Ansley

Regrowth 10 years after fire

•Temporary increase in herbaceous dominance

•Minimal negative effect (if any) on density

•Management with fire requires high frequency (e.g. 2-5 year return interval).

•Temporary increase in herbaceous dominance

•Minimal negative effect (if any) on density

•Management with fire requires high frequency (e.g. 2-5 year return interval).

Resprouting shrubs and treesSummary

Resprouting shrubs and treesSummary

http://gisdata.usgs.net/website/MRLC/viewer.php

Grasslands

Years since focal disturbance0 1 2 3 4 5A

bove

grou

nd b

iom

ass

(g/0

.1m

2)

0

20

40

60

80 Spring firesSummer and Fall fires

R2=0.72

End

of y

ear s

tand

ing

crop

(g 0

.10

m-2

)Bison Unit of the Tallgrass Prairie Preserve

Blair 1997

Transient Maxima Hypothesis

Ansley et al. 2006

Season has minimal longterm effects in grasslands

• Howe 1994• Engle et al. 2000• Engle and Bidwell 2001• Brockway et al. 2002• Towne and Kemp 2003• Fuhlendorf and Engle 2004• Fuhlendorf et al. 2006• Ansley et al. 2006

Pre-fire ConditionPre-fire Condition

1 Year Post-fire1 Year Post-fire

1 Month Post-fire1 Month Post-fire

Photos by Jim Ansley

Grasslands Summary

1. Reduce woody plant encroachment2. Alter grazing distribution to provide

heterogeneity3. Short term, stochastic effects on

composition– Interaction with weather– Frequency and season have less effect than

time since fire.

Factors that influence fire effects

1. Everything that influences fire intensity– Fuel load, humidity, temperature, Fuel

moisture etc..– Grazing– Season

Photos by Jim Ansley

0

20

40

60

80

100

0 100 200 300 400 500

Mean fuel load (g m-2)

Sco

rch

prop

ortio

n (%

) Fuel Moisture <5%r2= 0.154P = 0.14

Fuel Moisture > 20%r2= 0.876P < 0.01

Effect of Summer Fire

Twidwell, Fuhlendorf & Engle in review

Factors that influence fire effects

1. Everything that influences fire intensity1. Fuel load, humidity, temperature, Fuel

moisture etc..2. Grazing3. Season

2. Fire Frequency / Time Since Fire

Summary and Synthesis

1.Focus on woody-herbaceous interaction2.For Fire Sensitive species

• Fire interval – 5-15 yr• Grazing and initial conditions are critical

3.For Re-sprouting Species• Fire interval – 2-5 yrs

4.For Grasslands• Time since fire

5.Critical issues• Fire intensity• Time since fire

Rx Fire Associations

• Cooperation among landowners

• Rural fire departments• Go beyond ownership

boundaries• Can limit liability• Create a new land ethic• Provide training

top related