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2017-02-03_PERMIT FILE - C1980004A (11)
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2017-02-03_PERMIT FILE - C1980004A (11)
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Last modified
1/15/2019 12:57:51 PM
Creation date
7/13/2017 7:35:57 AM
Metadata
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Template:
DRMS Permit Index
Permit No
C1980004A
IBM Index Class Name
Permit File
Doc Date
2/3/2017
Section_Exhibit Name
Tables 4.2 to 4.5-28
Media Type
D
Archive
Yes
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Biological Assessment for DMG Permit Renewals McClane Canyon & Munger Canyon Mines <br />~; 1998; Andrews and Righter 1992). Breeding birds occur in low densities throughout their range <br />(Kingery 1998). Numbers of wintering birds across the state are higher than breeding numbers, <br />and are concentrated around prairie dog colonies or areas with significant populations of ground <br />squirrels, cottontails, or jackrabbits (Andrews and Righter 1992). Populations and reproductive <br />success of ferruginous hawks may fluctuate with prey populations (Smith et al. 1981; Woffinden <br />and Murphy 1977). <br />Ferruginous hawks nest in open landscapes in isolated junipers or less commonly, on the <br />ground (Righter et al. 2004), on rock outcrops, utility poles, or windmills (Andrews and Righter <br />1992). Common roosts are hilltops near prairie dog colonies, cottonwoods, and utility poles <br />(Righter et al. 2004). Threats to ferruginous hawks include conversion of grasslands and <br />shrubsteppe rangelands to croplands and urban developments, and widespread extermination <br />of prairie dog colonies and other rodents (Kingery 1998; Bechard et al. 1995). A few records of <br />ferruginous hawk in Garfield County have been documented by CNHP, but none of the <br />occurrences were in the Howard Canyon USGS quadrangle (CNHP 2005). This species is <br />unlikely to nest in the relatively narrow canyons of McClane or Munger, although it potentially <br />hunts for rodents in the sagebrush or semi-desert shrub canyon bottoms of the assessment <br />areas, especially during winter. Human presence and mine activities may influence ferruginous <br />hawk foraging patterns in the immediate area, but are unlikely to produce measurable effects on <br />the species. <br />Yellow-billed cuckoo (C). Probably never common in western Colorado (Bailey and Niedrach <br />1965), this bird is now considered an extremely rare summer resident and nearly extirpated in <br />western Colorado (Kingery 1998; Righter et al. 2004). The species does not winter in Colorado. <br />Reasons for decline of the yellow-billed cuckoo throughout the western U.S. have been <br />attributed to destruction of its preferred riparian habitat due to agricultural conversions, flood <br />control projects, and urbanization (Hughes 1999). In some parts of its breeding range, pesticide <br />use may have affected the yellow-billed cuckoo's prey base-injurious pest insects such as tent <br />caterpillars, which tend to occur in cyclic outbreaks (Hughes 1999; Ryser 1985). Only one <br />confirmed nesting occurrence was recorded in western Colorado (the Yampa River near <br />Hayden) during Colorado BBA surveys from 1987 through 1994 (Kingery 1998). CNHP (2005) <br />lists one record of yellow-billed cuckoo in La Plata County. Since the 1990, only one to two <br />yellow-billed cuckoo observations, and no nesting reports, have occurred annually in western <br />Colorado, mostly from the Uncompahgre River and Grand valleys (Righter et al. 2004). <br />The preferred habitat of yellow-billed cuckoo is low elevation river corridors. They nest in old- <br />growth cottonwood forests or woodlands with dense, scrubby understories of willows or other <br />riparian shrubs (Kingery 1998; Hughes 1999). Studies in Calrfomia indicate this species may <br />need extensive stands of riparian forest for nesting success (Righter et al. 2004 citing Gaines <br />and Laymon 1984). Limited habitat in and adjacent to the permitted areas of surface <br />disturbance (approximately 2 acres of perennial and 4 acres of ephemeral riparian corridor) is <br />only marginally suitable for this species due to sparseness of cottonwoods, the small stature of <br />existing cottonwoods, and lack of significant cottonwood canopy. Given the availability of more <br />suitable nesting habitat in the Grand Valley some 20 miles south, and given the low abundance <br />of this species in western Colorado and the low likelihood of it selecting the marginal habitat in <br />the assessment areas, the proposed actions are not likely to cause measurable effects to <br />yellow-billed cuckoo. <br />5.2 Fishes <br />The upper Colorado River Basin is home to 12 native fish species, four of which are listed as <br />endangered under the ESA: bon ail (USFWS 1980), Colorado oikeminnow (USFWS 1967), <br />March 27, 2006 10 Rare Earth Science, LLC <br />
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