Section-based Monitoring of Breeding Birds within the Shortgrass
Managing for heterogeneity in shortgrass steppe · Century Bement 1969 Management Paradigm....
Transcript of Managing for heterogeneity in shortgrass steppe · Century Bement 1969 Management Paradigm....
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Managing for heterogeneity in shortgrass steppe:
A birds-eye view of the effects of fire, prairie dogs and cattle grazing
David Augustine, USDA – ARS, Rangeland Resources Research Unit, Fort Collins, CO
Justin Derner, USDA – ARS, Rangeland Resources Research Unit, Cheyenne, WY
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Outline• Disturbance Ecology & Bird Conservation in the
Shortgrass Steppe (SGS)– Role of livestock grazing, prairie dogs, & fire in SGS – Mountain Plover breeding habitat in SGS
• Comparison of livestock grazing, fire, and prairie dog effects on:– Vegetation cover/structure– Mountain Plovers
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Large Grazers
Fire
Large Grazers
Drought
Prairie Dogs
Fire
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20th Century
Bement 1969
Management Paradigm Conservation Concern
Knopf 1996
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20th Century
Bement 1969
Management Paradigm Conservation Concern
Knopf 1996
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How can livestock grazing be used to provide nesting habitat for mountain plovers?
What are the costs to livestock weight gains?
Can prescribed burning and prairie dogs be used in combination with livestock grazing to provide nesting habitat for mountain plovers? What are the costs?
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Prairie Dogs
P. Stapp, M. Antolin, and M. Ball. 2004. Patterns of extinction in prairie dog metapopulations. Front Ecol Environ 2:235-240
•Estimated to historically occupy 2 – 15% of shortgrass and mixed-grass landscapes
•Can impart more intense and chronic (year-round) herbivory regime than ungulates
•Non-ruminants, significant soil movement
Pawnee National Grassland, CO
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Fire
•Historically a component of the shortgrass steppe, although return intervals are uncertain
•Currently: extensive network of roads, croplands and VFDs effectively suppress wildfires; prescribed burning rarely used on private lands
•Pawnee National Grassland, CO: Prescribed burning on ~2,600 acres (1.3%) per year since 1995
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Mountain Plovers in Shortgrass Steppe
“The range of variation under historic disturbance regimes is an important context to evaluate current and desired conditions [for land
management] … When evaluating the range of variation … use knowledge about the organisms that exist in an ecosystem today to
make inferences about the conditions that were likely to have existed in the past.” (FSH 1909.12, 43.13)
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Mountain Plovers in Shortgrass Steppe
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Mountain Plovers in Shortgrass Steppe
Studies on Pawnee National Grassland, CO, 1970s – 1990s:
•Graul (1975): 92% of nests in “blue grama – buffalo grass patches”, mean vegetation height < 8 cm, slopes < 2°
•Knopf and Miller (1994): Examined importance of bare soil in plover nestinghabitat “on the relatively prairie-dog-free Pawnee National Grassland of Colorado”:
• Nest sites had more bare ground (mean = 32%), more cow manure piles, and less cactus than random shortgrass sites
• Noted that “30% bare ground is likely closer to a minimum habitat requirement than an optimal one in Mountain Plover ecology”
•>20,000 Mountain Plovers estimated in the vicinity of Pawnee National Grassland in early 1970s (Graul 1976), but rare in this area by late 1990s
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Management strategies for Mountain Plover nesting habitat
• Livestock Grazing Intensity:– Moderate summer grazing (0.5 AUM ha-1)– Heavy summer grazing (0.8 – 1.1 AUM ha-1)– Heavy spring grazing + supplemental feed
• Prescribed burning:– Spring patch burns (Pawnee NG)– Fall patch burns (CPER)
• Black-tailed Prairie Dog Colonies: – On-off colony comparisons– Effects of plague-induced colony extirpations
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Management strategies for Mountain Plover nesting habitat
• Livestock Grazing Intensity:– Moderate summer grazing (0.5 AUM ha-1) 3– Heavy summer grazing (0.8 – 1.1 AUM ha-1) 3– Heavy spring grazing + supplemental feed
• Prescribed burning:– Spring patch burns (Pawnee NG) 3– Fall patch burns (CPER)
• Black-tailed Prairie Dog Colonies: – On-off colony comparisons 3– Effects of plague-induced colony extirpations
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Management strategies for Mountain Plover nesting habitat
Measurements (2007 & 2008):
– Vegetation cover and height in a randomly-located grid of 45 1-m2
plots in all pastures, colonies & burns
– Vegetation cover and height at plover nest and foraging sites (13 1-m2 plots per site)
– All measurements during May 1 – 14 (early nesting phase)
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Management strategies for Mountain Plover nesting habitat
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Summer-ModerateCattle Grazing
Summer-HeavyCattle Grazing
Prescribed Burns+ Cattle
Prairie Dogs +Cattle
Plover-Occupied
Mea
n C
over
of B
are
Soil
(%)
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Management strategies for Mountain Plover nesting habitat
Booth et al. (2008) Image-based monitoring to measure ecological change in rangeland. Frontiers in Ecology and the Environment 6:185-190.
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Management strategies for Mountain Plover nesting habitat
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5.0
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Summer-ModerateCattle Grazing
Summer-HeavyCattle Grazing
Prescribed Burns+ Cattle
Prairie Dogs +Cattle
Plover-Occupied
Mea
n C
over
of B
are
Soil
(%)
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Management strategies for Mountain Plover nesting habitat
0.0
5.0
10.0
15.0
20.0
25.0
30.0
35.0
40.0
45.0
50.0
Summer-ModerateCattle Grazing
Summer-HeavyCattle Grazing
Prescribed Burns+ Cattle
Prairie Dogs +Cattle
Plover-Occupied
Mea
n C
over
of B
are
Soil
(%)
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Management strategies for Mountain Plover nesting habitat
0.0
1.0
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4.0
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8.0
Summer-ModerateCattle Grazing
Summer-HeavyCattle Grazing
Prescribed Burns +Cattle
Prairie Dogs +Cattle
Plover-Occupied
Vege
tatio
n H
eigh
t (cm
)
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2008 Mountain Plover Survey: PNG & CPER
Replicate Sites PointsSurveyed Surveyed Mean 95% CI
Prescribed Burns 10 76 6.8 (3.3, 23.1)Prairie Dog Colonies 8 54 6.2 (2.1, 18.3)Rangeland (All sites) 20 160 0.6 (0.04, 2.4)Rangeland (Random sites) 12 120 0 --
Density (Plovers per km2)
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2008 Mountain Plover Survey: PNG & CPER
Replicate Sites PointsSurveyed Surveyed Mean 95% CI
Prescribed Burns 10 76 6.8 (3.3, 23.1)Prairie Dog Colonies 8 54 6.2 (2.1, 18.3)Rangeland (All sites) 20 160 0.6 (0.04, 2.4)Rangeland (Random sites) 12 120 0 --
Density (Plovers per km2)
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Vegetation Cover at Mountain Plover Nesting Sites
0
10
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-10 0 10 20 30 40 50 60 70 80 90 100
Distance from Nest (m)
% C
over
Bar
e So
il
1992
20072008
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Vegetation Cover at Mountain Plover Nesting Sites
1992
2007
0
10
20
30
40
50
60
-10 0 10 20 30 40 50 60 70 80 90 100
Distance from Nest (m)
% C
over
Bar
e S
oil
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Vegetation Cover at Mountain Plover Nesting Sites
0
10
20
30
40
50
60
-10 0 10 20 30 40 50 60 70 80 90 100
Distance from Nest (m)
% C
over
Bar
e So
il
1992
20072008
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Adapted from: Knopf (1996)
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Very Heavy
Suppressed
Heavy
Light
Absent
Frequent
Absent
Large complexes
Long-term presence
Small complexes
Intermittent presence
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Vegetation < 5 cm
Short-term pulse ofbare soil
No effect on blue grama
Vegetation < 5 cm
Multiple years ofbare soil
Loss of blue gramadominance
Vegetation < 5cm
Increased dominance of blue grama
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Vegetation < 5 cm
Short-term pulse ofbare soil
No effect on blue grama
Vegetation < 5 cm
Multiple years ofbare soil
Loss of blue gramadominance
Vegetation < 5cm
Increased dominance of blue grama
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Very Heavy
Suppressed
Heavy
Light
Absent
Frequent
Absent
Large complexes
Long-term presence
Small complexes
Intermittent presence
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Very Heavy
Suppressed
Heavy
Light
Absent
Frequent
Absent
Large complexes
Long-term presence
Small complexes
Intermittent presence
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Future Needs:
•Appropriate spatial scales for management practices
•Costs to livestock production
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Acknowledgments:• Fritz Knopf• Patrick McCusker• Beth Humphrey• Mary Ashby• Jeff Thomas• Troy Smith• Tammy Kanode• Jessica Crowder• Josh Baker• Derek Flannery• Tyler Odell