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Gunnison Sage-Grouse Use of Conservation Reserve Program Fields in Utah and Response to Emergency Grazing. By: Sarah G. Lupis, Terry A. Messmer, and Todd Black. Presented By: Wesley Wiegreffe. Introduction: Ranges. Historical Range: (Young et al. 2000) Gunnison Basin of Colorado
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Gunnison Sage-Grouse Use of Conservation Reserve Program Fields in Utah and Response to Emergency Grazing By: Sarah G. Lupis, Terry A. Messmer, and Todd Black Presented By: Wesley Wiegreffe
Introduction: Ranges • Historical Range: (Young et al. 2000) • Gunnison Basin of Colorado • Northern New Mexico • Northeastern Arizona • Current Range and Numbers: • Eight Populations • < 5000 breeding birds • Colorado and Utah
Introduction: Utah Range • San Juan County • Inhabit 13,625 km² in within Utah • 90% of range privately owned and in agricultural production (Mitchell and Maxfield 2000)
Introduction: Conservation • San Juan County Gunnison Sage-Grouse Working Group • Conservation Reserve Program • Food Security Act 1985 • 21,600 acres • Cost: $1.2 million / Income: $1.0 million
Introduction: Conditions • 2002 – Severe Drought • CRP opened to domestic grazing of livestock • Option every five years • Must have 40% loss in moisture • (D. Christenson, Farm Service Agency)
Introduction: Effects • Grazing may be factor in range declines₁ • Destruction of sage-brush (Artemisia spp.)₂ • Deterioration of habitat by grazing₂ • Trampled eggs₂ • Avoidance of grazed areas₂ 1(Johnsgaurd 1973, Connelly and Braune1997) 2( Beck and Mitchell 2000)
Introduction: Effects • Possible Positive Direct Effects (Beck & Mitchell 2000) • Use of light-moderate grazed areas • Stimulated food growth • Recovery of forbs under rest-rotation system
Objectives • Study grouse habitat-use patterns relative to other available habitats • Determine if CRP achieve desired vegetation cover conditions • Monitoring of Gunnison-Sage Grouse response to grazing practice
Study Area • 2,417 kms² • Active lek sites • Grassland and • sagebrush • 60% CRP
Methods: Radiotelemetry • Capture (Mar and Apr 2001 & 2002) • 10:00 pm – 6:00am • Spotlighting • Net/Net gun from vehicle • Necklace-style radio collar (19 hrs on/15 hrs off)
Methods: Radiotelemetry • Located Birds May and Sept 2001 and 2002 3x a week • Radio receivers, 3-element handheld Yagi antennae, omni antennae • Minimized nest abandonment • Visual identification with binoculars • Recorded: date, time, sex, # birds, cover • Nest successful: > 1 egg hatched • Brood successful: > 1 chick survive 50 days posthatch
Methods: CRP Usage • Data analyzed at two scales: • Landscape scale • Bird-use (selected) sites • land used in greater proportion than available • Vegetation Sampling • Two perpendicular 20 meter transects • Visual estimation of cover using Daubenmire frame • (Daubenmire 1959)
Methods:Grazing Response • Field Boundaries Mapped • ArcView GIS 3.2 • Natural Recourse Conservation Service provided: • CRP field location • Biomass estimates • Stocking rates • Measured vegetation on both grazed and ungrazed fields
Methods: Data Analysis • Landscape scale • Chi Squared Analysis – goodness of fit • Observed usage vs. Expected usage • Equal access to all parts of Concentrated Zone assumed • All test considered significant at p < 0.05
Results: Birds & Nests • 2001 • Captured 4 Males/1 Female • 1 Male Death • 2002 • Captured 3 Males/5 Females • 1 Male Death • Three Hens Nested • All nests successful • 2 broods successful
Results: Brood Cover • 2001 • Chi Squared: 0.058 • P< 1 • CRP not selected for • 2002 • Chi Squared: 7.674 • P< 0.10 • CRP not selected for
Results: Male Cover • 2001 • Chi Squared: 0.194 • P < 1 • CRP not selected for • 2002 • Chi Squared: 7.856 • P < 1 • CRP not selected for
Results: Stocking Rates & Biomass Four Fields Grazed in 2002 (provided by NRCS)
Results: Male Response • Before in all fields: 43% (18/42) occurrence • Cattle Present: • Field 1 – 18% (2/11) • Field 2 – 0% • Field 3 – 0% • Field 4 – 38% (3/8) • Avoidance of grazed fields during and after
Results: Broodless Response • Before in all fields: 56% (14/25) occurrence • Cattle Present: • Field 1 – 8% (1/12) • Field 2 – 5% (1/19) • Field 3 – 0% • Field 4 – 0% • Avoidance of grazed fields during and after
Results: Brood Response • Brooding Hen Located in Field 1 throughout study • Before: 50% • After: 72.7% (8/11)
Conclusions • No statistical evidence to support that Gunnison Sage-Grouse select for CRP lands • CRP did not meet the guidelines recommended for cover by the Gunnison Sage-Grouse Rangewide Conservation Plan (Gunnison Sage-Grouse Rangwide Steering Committee 2005) • Less shrub present (3-10%) than recommended (10-40%)
Conclusions • Gunnison Sage-Grouse movement and habitat usage were related to actual presence of livestock and only temporarily displaced • Decrease in use of land during occupation of cattle • 2003-2004 return to CRP land that was previously grazed (S. Ward, Utah State University, Unpublished Data)
Management Implications • CRP has provided protection for Greater Sage-Grouse in Washington (Schroeder at al. 2000) and it provides year-round protection (Hays et al. 1998) • This paper further supports need for sustained CRP land over long term and sagebrush management
Management Implications • Loss of CRP land could result in loss of habitat, increasing mortality by concentrating birds in marginable habitat • Seasonal Livestock grazing of CRP lands should rotate usage to provide areas for breeding in spring and summer • Livestock grazing could be used as a method to increase sage canopy cover (Crawford et al. 2004)
Connection to Class Material • Gunnison Sage-Grouse are listed as an endangered species by both IUCN and ESA • Narrow Geographic Range • Few Populations • Small Populations • This study represents an effort to manage for this species based on its: • Ecology • Impact of Humans
Connection to Class Material • Example of National Conservation • Conservation Reserve Program is a service provided by the Farm Service Agency, which is a branch of the United States Department of Agriculture • Type of Protected Area • Habitat/Species Management Area – land set aside for scientific research, management and monitoring but can be harvested
Connection to Class Material • CRP manages for the defragmentation of this population of this population of Gunnison Sage-Grouse • Leasing of CRP land could result in an example of the Tragedy of the Commons • Extirpation of population by cattle • Cost to rancher communized while the profits are privatized