Expected Impacts on Greater Prairie-Chickens
of Establishing a Wind Turbine Facility Near Rosalia, Kansas Prepared for:
Zilkha Renewable Energy
Houston, Texas
By: Dr. Robert J. Robel
Division of Biology
Kansas State University
September 2002
There are 10 species of grouse native to North America. Prairie
chickens are grouse and they generally are considered birds of the
grasslands. Prairie chickens consist of two taxonomic species, the
lesser prairie-chicken (Tympanuchus pallidicinctus) and the greater
prairie-chicken (Tympanuchus cupido) (American Ornithologists’
Union 1998).
The lesser prairie-chicken has the most restricted distribution
of the two grassland grouse species (Aldrich 1963, Johnsgard 1983).
It is found in rangeland dominated primarily by sand sagebrush (Artemisia
filifolia) or shinnery oak (Quercus havardii) and bluestem grasses
(Andropogan spp.) in eastern New Mexico, southeastern Colorado,
western Oklahoma, the Texas panhandle, and southwestern Kansas.
Even though this area of the Southern Great Plains is populated
sparsely by humans, their activities have had a severe impact on
lesser prairie-chicken populations. Intensive livestock grazing
and conversion of native rangelands to cropland coupled with recurrent
droughts have reduced lesser prairie-chicken habitat by 92% and
populations by approximately 97% range-wide since the 1800s (Crawford
1980). Lesser prairie-chicken populations are now fragmented and
isolated over much of their original range (Geisen 1998), and the
species was petitioned in 1995 for listing under provisions of the
Endangered Species Act (Mote et al. 1999). The U.S. Fish and Wildlife
Service determined that listing the species as threatened was warranted,
but precluded (Clark 1999). The primary range of the lesser prairie-chicken
in Kansas is the southwestern part of the state, far removed from
the proposed site of the wind farm near Rosalia, Kansas.
Three subspecies of the greater prairie-chicken are recognized
(Aldrich 1963, Johnsgard 1983). The heath hen (Tympanuchus cupido
cupido), formerly found along the east coast of the United States,
became extinct in 1932. The Attwater’s prairie-chicken (T.
c. attwateri) is endangered (U.S. Fish and Wildlife Service 1983)
and restricted to isolated areas along the Texas coast. The wild
population of Attwater’s prairie-chicken now numbers less
than 100 birds (Morrow 1999), and efforts are being made to maintain
the population through releases of captivity-reared birds. The greater
prairie-chicken (T. c. pinnatus) had, and still has, a wider distribution
than either the heath hen or the Attwater’s prairie-chicken.
Historically, the greater prairie-chicken ranged across the tallgrass
prairies of North America from eastern Texas north-westward to Alberta
and north-eastward to Michigan and southern Ontario (Figure 1).
It has been extirpated or very much reduced in numbers over much
of its range, and was numerous enough in only four states (Kansas,
Colorado, Nebraska, and South Dakota) to be hunted legally during
2001.
Conversion of the tallgrass prairie habitat to intensive agriculture
is the primary cause of declines in the greater prairie-chicken
population across its original range (Schroeder and Robb 1993).
This conversion over much of the midwestern portion of North America
greatly reduced or degraded the nesting habitat of greater prairie-chickens
and negatively impacted their populations (Christisen 1969, 1985).
Predator populations also reduce nesting success of greater prairie-chickens
(Lawrence 1982). Other factors reported to negatively affect the
numbers of greater prairie-chickens include hunting isolated populations
(Hamerstrom and Hamerstrom 1973); reduced insect availability for
broods because of pesticide use (Flickinger and Swineford 1983);
and interspecific competition with ring-necked pheasants (Phasianus
colchicus) (Vance and Westemeier 1979, Westemeier 1986, Westemeier
et al. 1998).
Figure 1. Distribution of the greater prairie-chicken
in North America in the past (dashed line adapted from Schroeder
and Robb 1993) and present (solid areas adapted from Westemeier
and Gough 1999). Solid line delineates the approximate pre-settlement
boundary of the tallgrass prairie biome. Map reproduced from Svedarsky
et al. 2000:278.
We invite you to participate and contribute to our conservation
efforts and keep Audubon of Kansas moving forward. Your tax-deductible
contributions and volunteer efforts sustain our non-profit organization
and are essential to all aspects of our work—from advocacy,
legislative liaison, education, and support of wildlife-friendly
landowners, to our office staff, publications and website. We
need your commitment!
Copyright 2007
Audubon of Kansas, Inc.
210 Southwind Place
Manhattan, KS 66503
(785) 537-4385
aok@audubonofkansas.org