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                  <text>Colorado Division of Parks and Wildlife
September 2014-September 2015
WILDLIFE RESEARCH REPORT
State of:
Cost Center:
Work Package:
Task No.:

Colorado
3420
0659
N/A

Federal Aid
Project No.

N/A

:
:
:
:

Division of Parks and Wildlife
Avian Research
Greater Sage-grouse Conservation
Development of landscape scale resource selection
models for the management of Gunnison sagegrouse in the Gunnison Basin population

Period Covered: September 1, 2014 – August 31, 2015
Author: M. Rice
Personnel: A. Apa, N. Seward, J Wenum
All information in this report is preliminary and subject to further evaluation. Information MAY
NOT BE PUBLISHED OR QUOTED without permission of the author. Manipulation of these data
beyond that contained in this report is discouraged.
EXTENDED ABSTRACT
Gunnison sage-grouse (Centrocercus minimus) have declined substantially from their historica
range and were listed as threatened by the U. S. Fish and Wildlife Service in November of 2014. GUSG
are distributed into seven isolated populations in Colorado and one population, Gunnison Basin (GB)
comprises 85-09% of all GUSG in the state. Concern over the small population size and isolated and
fragmented nature of many of the smaller populations has led to interest in the habitat use of GUSG.
Much of the information that has been used on GUSG habitat selection has come from studies pertaining
to Greater Sage-grouse. Currently the USFWS have designated most of the Gunnison basin as critical
habitat, but there may be some variability to the quality and use of that critical habitat which could refine
those maps for better management of the species. To successfully manage and understand the Gunnison
sage-grouse, we must identify the habitat that is most important to the birds using data driven models.
Colorado Parks and Wildlife has collected radio-telemetry data from almost 200 birds from 2004-2010
which could be used to model habitat selection with a robust dataset specific to the Gunnison sage-grouse
in the Gunnison basin.
We utilized radio-telemetry data from individual GUSG caught during the spring and fall periods
2004-2010. Following release, radiotelemetry locations of radio-marked individuals were estimated on
the ground using hand-held Yagi antennas once every 1-3 days (from date of capture through September)
to monitor status (dead or alive) and movement patterns. We were able to estimate resource selection
models for the breeding (April to July 15) and summer seasons (July 16 to September). We used 188
birds and 3,936 locations for the breeding season model and 171 birds and 3,721 locations for the summer
model. We buffered each use location by the average daily movement which was 180.5m in the breeding
period and 223m in the summer period. We generated 9,000 “available” locations across the entire
Gunnison basin and used the same seasonal buffers. Vegetation, topographical, and development
variables were extracted for each buffer to be used in the analysis. Development variables included roads,
subdivisions, trails, easements, and address points collected by Gunnison County. We used a generalized

�mixed linear model with a logistic link and a random effect for individual birds to model habitat use. We
used all linear combinations of variables and model averaged over the 95% model set. We utilized an
average prediction surface in ArcMap 10.1.
The breeding model indicated that GUSG were 2.24 times as likely to be located in sagebrush and
1.5 times as likely to be located in high densities of trails (Table 1). Being closer to subdivisions and
easements and further from wetlands were also important predictors. Finally, GUSG are 1.49 more likely
to NOT be located in forest. There were also smaller effects including being located in grassland, slightly
higher elevations, in areas with higher water density, in areas with high road density and further from
class 1 and 2 roads and further from address points (Table 1). The resulting prediction surface indicated
that large swaths of sagebrush had a higher relative probability of GUSG presence and many of the
drainages were avoided (Figure 1).
The summer model indicated that GUSG were 3.64 times as likely to be located in sagebrush,
2.41 times as likely to be located in irrigated agriculture, 1.41 times as likely to be in grassland, and 1.8
times as likely to be in alpine(Table 2). Being closer to subdivisions and easements and further from
house address points were also important predictors. Finally, GUSG are 1.49 more likely to NOT be
located in forest. GUSG are more likely to be in areas with high trail densities, low road densities, and
high water densities. GUSG are also more likely to be closer to roads and slightly further from wetlands.
They are also going to be located in higher elevations (Table 2). The resulting prediction surface
indicated that GUSG used a more diverse set of habitats and tended to move into higher areas within the
Gunnison basin (Figure 2).
Overall Gunnison sage-grouse are dependent on large swaths of sagebrush although they tend to
have more diverse selection during the summer when they utilize numerous habitats including grassland,
irrigated agriculture, and alpine. They tend to be close to subdivisions and easements and in areas with
high levels of trail density in both seasons. Overall, not all the human related variables were negatively
impacting GUSG although it was dependent on the season. These models can be used to further refine
the estimated critical habitat currently being used by USFWS as they reduce the amount of critical habitat
in both seasons. In addition, these models provide information regarding two seasons in the GUSG life
cycle and can be used to manage the population on the ground.

�Table 1: Model averaged model coefficients, confidence intervals, and odds ratios for Gunnison sagegrouse during the breeding season in the Gunnison Basin of Colorado.
Variable
β
SE
LCI
UCI
Odds
ratio
Intercept
- 1.671
Sagebrush
0.805
0.065
0.712
0.899
2.24
Grassland
0.184
0.037
0.131
0.238
1.2
forest
- 0.396
0.081
- 0.513
- 0.279
0.67
elevation
0.095
0.039
0.039
0.151
1.10
distance to wetlands
0.517
0.029
0.479
0.554
1.68
water density
0.230
0.029
0.189
0.271
1.26
Road density
0.139
0.032
0.093
0.185
1.15
Distance to roads
0.103
0.032
0.056
0.149
1.11
Trail density
0.463
0.029
0.421
0.504
1.59
Distance to address points
0.309
0.034
0.260
0.358
1.36
Distance to subdivisions
- 0.536
0.049
- 0.607
- 0.495
0.58
Distance to easements
- 0.458
0.039
- 0.514
- 0.402
0.64

Table 2: Model averaged model coefficients, confidence intervals, and odds ratios for Gunnison sagegrouse during the summer season in the Gunnison Basin of Colorado.
Variable
ratio
Intercept
Sagebrush
Grassland
Irrigated agriculture
Alpine
elevation
distance to wetlands
water density
Road density
Distance to roads
Trail density
Distance to address points
Distance to subdivisions
Distance to easements

β

SE

LCI

UCI

- 1.580
1.292
0.342
0.881
0.592
0.238
0.072
0.161
- 0.356
- 0.294
0.339
0.377
- 0.655
- 0.453

0.058
0.033
0.042
0.032
0.039
0.026
0.027
0.040
0.032
0.028
0.034
0.040
0.037

1.209
0.294
0.821
0.547
0.182
0.035
0.123
- 0.413
- 0.340
0.299
0.328
- 0.713
- 0.506

1.376
0.389
0.941
0.638
0.295
0.110
0.199
- 0.299
- 0.249
0.379
0.427
- 0.597
- 0.399

Odds

3.64
1.41
2.41
1.81
1.27
1.07
1.17
0.70
0.75
1.40
1.46
0.52
0.64

�Figure 1: Relatively probability of Gunnison sage-grouse presence during the breeding season across the
Gunnison basin using data from radio-telemetry data collected from 2004 until 2010.

�Figure 2: Relatively probability of Gunnison sage-grouse presence during the summer season across the
Gunnison basin using data from radio-telemetry data collected from 2004 until 2010.

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              <text>Gunnison sage-grouse (&lt;em&gt;Centrocercus minimus&lt;/em&gt;) have declined substantially from their historica range and were listed as threatened by the U. S. Fish and Wildlife Service in November of 2014. GUSG are distributed into seven isolated populations in Colorado and one population, Gunnison Basin (GB) comprises 85-09% of all GUSG in the state. Concern over the small population size and isolated and fragmented nature of many of the smaller populations has led to interest in the habitat use of GUSG. Much of the information that has been used on GUSG habitat selection has come from studies pertaining to Greater Sage-grouse. Currently the USFWS have designated most of the Gunnison basin as critical habitat, but there may be some variability to the quality and use of that critical habitat which could refine those maps for better management of the species. To successfully manage and understand the Gunnison sage-grouse, we must identify the habitat that is most important to the birds using data driven models. Colorado Parks and Wildlife has collected radio-telemetry data from almost 200 birds from 2004-2010 which could be used to model habitat selection with a robust dataset specific to the Gunnison sage-grouse in the Gunnison basin.</text>
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