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Vantage to Pomona FEIS Index 34
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12. December
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2018-12-18 10:00 AM - Commissioners' Agenda
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Vantage to Pomona FEIS Index 34
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Last modified
12/13/2018 1:49:29 PM
Creation date
12/13/2018 1:34:21 PM
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Meeting
Date
12/18/2018
Meeting title
Commissioners' Agenda
Location
Commissioners' Auditorium
Address
205 West 5th Room 109 - Ellensburg
Meeting type
Regular
Meeting document type
Supporting documentation
Supplemental fields
Alpha Order
a
Item
Conduct a Closed Record Meeting to consider the Hearing Examiner's Recommendation for the Vantage to Pomona Transmission Line Conditional Use Permit (CU-18-00001)
Order
1
Placement
Board Discussion and Decision
Row ID
50108
Type
Conduct closed record hearing
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Vantage to Pomona Heights Chapter 4 <br />230 kV Transmission Line Project FEIS Environmental Consequences <br /> PAGE 4-65 <br />would be avian-safe with no potential for electrocution of raptors or other bird species. The proposed <br />Project would result in no identifiable impacts with regard to avian electrocution. <br />Predation <br />Mammalian predators and scavengers may use roads and transmission line ROWs as travel corridors <br />which may facilitate predation on Sage-Grouse (Bennett 1991; Forman and Alexander 1998). Because the <br />Project ROW would occur within sagebrush-steppe and grassland habitats that are already open, the <br />effects of mammalian predation on Sage-Grouse are likely to be less pronounced compared with corridor <br />effects in forested landscapes. In the relatively treeless environment of the Project study area, avian <br />predators are more likely to benefit from a transmission line structures than mammalian predators. <br />Armentrout and Hall (2005) reported that Sage-Grouse nests and adults associated with leks near <br />transmission lines were lost at a higher rate to avian rather than mammalian predators. They reported that <br />predation attributed to mammals actually occurred at a lower rate near transmission lines. <br />Transmission line structures provide substrates for perching, roosting, and nesting for some avian species <br />(i.e., raptors and corvids) (APLIC 2006; Knight et al. 1995; Steenhof et al. 1993). In open areas where <br />natural substrates are limited, this may increase local abundance of avian predator species and increase <br />predation pressures on prey species such as small mammals and nesting birds (Call and Maser 1985; <br />Connelly et al. 2000; Vander Haegen et al. 2002; Howe et al. 2014). While these effects have mainly been <br />documented for terrestrial prey species, predators of fish may also perch on transmission structures and/or <br />transmission lines. <br />The distance that these effects could extend from the transmission line depends on the hunting range of <br />the predator species. Some raptor species may benefit from the proposed Project by the creation of new <br />perching structures from which to hunt prey. Common raven populations have increased fourfold in the <br />western U.S. during the past 40 years (Sauer et al. 2012). Raven populations often increase following <br />human alteration of landscapes due to increased availability of food (e.g., litter associated with human <br />use, roadkill, refuse, landfills), water (e.g., stock ponds, reservoirs), and nesting substrates (e.g., <br />transmission line structures, communication towers, buildings) (Knight and Kawashima 1993; Kristan et <br />al. 2004; Howe et al. 2014). In eastern Idaho, Howe et al. (2014) reported a 31 percent decrease in the <br />odds of nesting by ravens for every 0.6 mile (1.0 kilometer) increase in distance away from a transmission <br />line ROW, with 48 of 82 nests in the study located on transmission line poles. <br />Long-term monitoring of raven nests at JBLM YTC began in 1994. In 1994, 28 raven nests were located <br />on JBLM YTC; seven (25 percent) of them were located on anthropogenic structures, including one on a <br />transmission line structure (Paulus and Malkin 1995). In 2013, 47 raven nests were located on JBLM <br />YTC, a 68 percent increase relative to 1994. Although an attempt is made to locate all raven nests on <br />JBLM YTC each year, search efforts have not been spatially and temporally consistent (JBLM YTC <br />personal communication 2014a). <br />A correlation between raven abundance and transmission lines has been established elsewhere (Howe et <br />al. 2014); at JBLM YTC the distribution of raven nests does not appear to be spatially correlated with the <br />locations of transmission lines. None of the active raven nests identified in 2013 were located on Pacific <br />Power’s existing Pomona-Wanapum 230 kV transmission line structures that the proposed New Northern <br />Route (NNR) Alternative closely parallels. It is unclear if the apparent nesting patterns of ravens at JBLM <br />YTC are real or just an artifact of spatial variation in search effort. <br />The Terrace Heights Landfill is located approximately 2.0 miles south and west of Route Segments 1b <br />and 1c and is likely to provide an abundant source of food for ravens (Paulus and Malkin 1995). <br />Transmission line structures may be more likely to be used by ravens in areas near this abundant food
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