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APPENDIX 9-102.K
WILDLIFE AND VEGETATION IMPACT ANALYSIS
THIS PAGE LEFT BLANK FOR TWO-SIDED DUPLICATION.
URSA OPERATING COMPANY, LLC.
B&V TEMPORARY WATER PIPELINE
Impact Analysis: Section 4-203-G (6) – Environmental Impacts
Garfield County Land Use and Development Code
Prepared for:
Ursa Operating Company, LLC.
792 Buckhorn Drive
Rifle, Colorado 81650
Prepared by:
WestWater Engineering
2516 Foresight Circle #1
Grand Junction, CO 81505
Nicholas Jaramillo, Biologist/Environmental Scientist
January 2017
WestWater Engineering Page 1 of 13 January 2017
INTRODUCTION
Project Description
At the request of Ursa Operating Company, LLC. (Ursa), WestWater Engineering (WestWater) has
prepared this Garfield County Impact Analysis for the proposed B&V Temporary Water Pipeline project
consisting of a surface water pipeline approximately 2.01 miles in length. The project would be located on
private lands in Garfield County, Colorado in Sections 7 and 8, Township 7 South, Range 95 West. The
current primary uses of the surrounding area include residential, agricultural, rangeland, natural gas
development, and wildlife habitat.
This document reports the results and analysis of findings pertinent to the Garfield County Land Use and
Development Code (amended November 12, 2013) as they apply to this project.
Survey Methods
No specific site visit was made for this project, although portions of this project overlapped with other
recent surveys conducted by WestWater in this area. Based on existing information from our database,
literature review, and experience working in the geographical area, WestWater biologists can make
generalizations regarding the biological resources that may be present in the project area.
Vegetation communities were determined through aerial photography and WestWater’s previous
experience in the project area. Plant species occurrence and identification was aided by using pertinent
published field guides (Spackman et al. 1997, Kershaw et al. 1998, Whitson et al. 2001, CWMA 2013,
Weber and Wittmann 2012). Mapped soil types, as published by the Natural Resources Conservation
Service (NRCS), U.S. Department of Agriculture (USDA), were reviewed to determine the soil types and
expected natural vegetation characteristics at the project site (NRCS 2017).
A desktop review was performed to identify known raptor and special status wildlife species occurrences
within 0.125 mile of the proposed pipeline. Noxious weed conditions are reported in a separate Integrated
Vegetation and Noxious Weed Management Plan (IVNWMP) that was prepared separately for this
project (WestWater 2017). Data locations are reported in map datum NAD83, Zone 12.
SECTION 4-203-G (6) - ENVIRONMENTAL IMPACTS
EXISTING ENVIRONMENTAL CONDITIONS
WATERS OF THE U.S. – Army Corps of Engineers (ACOE)
Based on available mapping and aerial photographs, five areas of potentially jurisdictional wetlands or
Waters of the U.S. are adjacent to or crossed by the project. These are described in Table 1 and Figure 2.
Table 1. Potential Army Corps of Engineers jurisdictional Waters of the U.S.
Label Comments
WOUS-1 Colorado River – crossing will be made by suspending pipeline from existing
infrastructure and no impact will be made within ordinary high water mark.
WOUS-2 USGS mapped drainage.
WOUS-3 USGS mapped drainage.
WOUS-4 USGS mapped drainage.
WOUS-5 USGS mapped drainage.
VEGETATION
The affected area covers a variety of habitat types consisting of native and disturbed rangelands as well as
agricultural areas and a small amount of riparian or wetland communities. Common grasses include
annual wheatgrass (Eremopyrum triticeum), bulbous bluegrass (Poa bulbosa), crested wheatgrass
(Agropyron cristatum), downy brome (cheatgrass) (Bromus tectorum), indian ricegrass (Achnatherum
WestWater Engineering Page 2 of 13 January 2017
hymenoides), intermediate wheatgrass (Thinopyrum intermedium), orchardgrass (Dactylis glomerata),
smooth brome (Bromus inermis), timothy (Phleum subulatum), and western wheatgrass (Pascopyrum
smithii). Shrub and woodland communities in the area are dominated by a mixture of basin and
Wyoming big sagebrush (Artemisia tridentata tridentata and A.t. wyomingensis ) and pinyon-juniper
(Pinus edulis – Juniperus osteosperma) woodlands with areas of greasewood (Sarcobatus vermiculatus).
Areas of riparian and wetland vegetation are dominated by broadleaf cattail (Typha latifolia), narrowleaf
cottonwood (Populus angustifolia), reed canarygrass (Phalaris arundinacea), and three-leaf sumac (Rhus
trilobata).
Threatened and Endangered Plant Species
The occurrence and distribution of special status plants in this region are strongly influenced by elevation,
hydrology, geologic formations, and soil characteristics present in an area. Threatened and endangered
plants known to occur in Garfield County are listed in Table 2 (USFWS 2017).
Table 2. Special status plants occurring in Garfield County.
Common Name Scientific Name Listing Status
Colorado hookless cactus Sclerocactus glaucus Threatened
DeBeque phacelia Phacelia submutica Threatened
Parachute beardtongue Penstemon debilis Threatened
Ute ladies’-tresses orchid Spiranthes diluvialis Threatened
Due to previous disturbances, soil composition, elevation, hydrology patterns, and distance to known
populations, the project area is unlikely to provide suitable habitat for any special status plant species in
this region. Review of the Colorado Rare Plant Field Guide (Spackman et. al. 1997) and WestWater’s
database confirms that no known populations of special status plants occur nearby.
Noxious Weeds
Noxious weed infestations, control techniques, and revegetation recommendations are reported in an
IVNWMP that was prepared for this project (WestWater 2017). Noxious weed species listed by the State
of Colorado (2005) known to exist in or near the project area include bulbous bluegrass (Poa bulbosa),
bull thistle (Cirsium vulgare), Canada thistle (Cirsium arvense), cheatgrass (Bromus tectorum), chicory
(Cichorium intybus), common burdock (Arctium minus), common mullein (Verbascum thapsus), common
teasel (Dipsacus fullonum), field bindweed (Convolvulus arvensis), houndstongue (Cynoglossum
officinale), musk thistle (Carduus nutans), redstem filaree (Erodium cicutarium), Russian knapweed
(Acroptilon repens), Russian olive (Elaeagnus angustifolia), Salt cedar (tamarisk – Tamarix
ramosissima), and Scotch thistle (Onopordum acanthanium).
Several unlisted nuisance weed species that are present in disturbed areas include flixweed (Descurania
sophia), kochia (Bassia scoparia), Russian thistle (Salsola spp.), and tall tumble mustard (Sisymbrium
altissimum).
WILDLIFE
Threatened, Endangered, and Candidate Wildlife Species
The project area was evaluated for threatened, endangered, or sensitive wildlife species listed in Garfield
County (Table 3) (USFWS 2017).
Table 3. Federal Threatened, Endangered, and Candidate Wildlife Species for Garfield County.
Common Name Scientific Name Status
Bonytail Gila elegans Endangered
Canada lynx Lynx canadensis Threatened
Colorado pikeminnow Ptychocheilus lucius Endangered
WestWater Engineering Page 3 of 13 January 2017
Table 3. Federal Threatened, Endangered, and Candidate Wildlife Species for Garfield County.
Common Name Scientific Name Status
Greenback cutthroat trout* Oncorhynchus clarki stomias Threatened
Humpback chub Gila cypha Endangered
Mexican spotted owl Strix occidentalis lucida Threatened
Razorback sucker Xyrauchen texanus Endangered
Yellow-billed cuckoo Coccyzus americanus Threatened
Bold = Species which may be affected by project.
* Until review and rulemaking process is complete regarding recent genetic research, the U.S. Fish and Wildlife Service is
recommending that “Lineage GB” cutthroat trout be managed as greenback cutthroat (USFWS 2012)
Designated critical habitat for two endangered fish species (Colorado pikeminnow and razorback sucker)
occurs in the Colorado River within the project area (Figure 3) and these species have been documented
near Parachute (Maddux et al. 1993). Designated critical habitat for two additional species (bonytail and
humpback chub) occurs downstream of the project near Grand Junction (Maddux et al. 1993).
No designated critical habitat exists for yellow-billed cuckoo, however cottonwood stands near the river
may provide marginal habitat. This species has not recently been documented near Parachute.
No other species listed in Table 3 would be affected, as habitat conditions are not appropriate.
Raptors
At least fifteen raptor species may be found in suitable habitats in the region (Table 4). Nesting season for
raptor species in this area takes place from January through mid-August. The most common raptor
species observed in the area include American Kestrel, Cooper’s Hawk, Golden Eagle, Great Horned
Owl, and Red-tailed Hawk. Bald Eagles are common near the Colorado River and forage near Battlement
Mesa.
Table 4. Raptor species that may occur near the project area.
Common Name Scientific Name BCC*
American Kestrel Falco sparverius No
Bald Eagle§ Haliaeetus leucocephalus Yes
Cooper’s Hawk Accipiter cooperii No
Flammulated Owl Otus flammeolus Yes
Golden Eagle Aquila chrysaetos Yes
Great Horned Owl Bubo virginianus No
Long-eared Owl Asio otus No
Northern Harrier Circus cyaneus No
Northern Goshawk§ Accipiter gentilis No
Northern Pygmy Owl Glaucidium gnoma No
Northern Saw-whet Owl Aegolius acadicus No
Peregrine Falcon+§ Falco peregrines Yes
Prairie Falcon Falco mexicanus Yes
Red-tailed Hawk Buteo jamaicensis No
Sharp-shinned Hawk Accipiter striatus No
Swainson’s Hawk Buteo swainsoni No
*BCC=U.S. Fish and Wildlife Service, Bird of Conservation Concern (USFWS 2008a)
+ State species of concern (CPW 2017a)
§BLM sensitive species (BLM 2009)
WestWater Engineering Page 4 of 13 January 2017
No raptor nests are known to exist within 0.125 mile of the proposed pipeline (Figure 3) although
complete surveys have not been conducted. Indirect impacts to occupied nests could occur if construction
occurs during the nesting season and such nests exist.
Birds of Conservation Concern, Migratory, and Non-migratory Birds (other than raptors)
WestWater biologists evaluated the project area for migratory bird species that could be affected by the
project. Birds of Conservation Concern (BCC) have been identified by the U.S. Fish and Wildlife Service
(USFWS) for priority conservation management in an attempt to prevent the listing of additional species
under the Endangered Species Act (USFWS 2008a). A literature review was conducted to identify BCC
species with potential to occur during other times of the year (Table 5) (Andrews & Righter 1992,
Kingery 1998, Righter et al. 2004).
Table 5. BCC species that may occur in the project area.
Common Name Scientific Name Habitat Description
Brewer’s Sparrow* Spizella breweri Expansive sagebrush shrublands; occasionally
found in greasewood or other shrublands.
Cassin's Finch Haemorhous cassinii Coniferous forest (including pinyon-juniper),
aspen, and cottonwood.
Gray Vireo Vireo vicinior Open pinyon-juniper habitats between 4,500 and
6,500 feet.
Juniper Titmouse Baeolophus ridgwayi Pinyon-juniper woodlands.
Lewis's Woodpecker Melanerpes lewis Open conifers, riparian cottonwoods, and burns.
Pinyon Jay Gymnorhinus cyanocephalus Pinyon-juniper woodlands above 5,000 feet.
* Also a BLM sensitive species (BLM 2009)
U.S. Fish and Wildlife Service guidance indicates that developments may potentially affect nesting
migratory birds within 100 feet of a project. The species in Table 5 and a multitude of other migratory
birds protected by the Migratory Bird Treaty Act (16 U.S.C. 703-712) are expected to occur in the project
area and could be affected by vegetation removal or equipment operation during nesting season.
American Elk and Mule Deer
The project is located in CPW Game Management Unit 42. The project is within CPW mapped mule deer
severe winter range and a winter concentration area (CPW 2017b) (Figure 4). The project is also located
within a mapped elk winter concentration area (Figure 5). Both species utilize the area, mostly during
winter, but a few resident animals may be present year-round.
Black Bear and Mountain Lion
CPW mapping shows the project area to be within overall range for black bear and mountain lion and
both species are known to occur nearby. Portions of the project are within CPW mapped mountain lion-
human conflict areas and black bear-human conflict areas (CPW 2017b).
Bears could occur in the area almost year round with the exception of the hibernation period occurring
from late fall through late spring. At times when foraging is difficult, bears become more visible as they
are more likely to utilize unnatural food sources created by humans.
Mountain lions likely inhabit the general project area primarily during the winter months as they follow
migrating big game herds, but could be found year-round. Lions tend to have large territories and are
highly mobile as they search for food or new territories so sightings tend to be uncommon.
Small Mammals
Common small mammal species in the project area include coyote (Canis latrans), cottontail (Sylvilagus
nuttallii), and numerous rodent species.
WestWater Engineering Page 5 of 13 January 2017
Reptiles
Bull snake (Pituophis catenifer), plateau striped whiptail (Cnemidophorus velox), racer (Coluber
constrictor), sagebrush lizard (Sceloporus graciousus), short-horned lizard (Phrynosoma hernandesi),
western terrestrial garter snake (Thamnophis elegans), and midget faded rattlesnake (Crotalus viridis
concolor) are reptiles potentially occurring in the project area (Hammerson 1999). Other than the midget
faded rattlesnake, which is a BLM sensitive and State species of concern (BLM 2009, CPW 2017a), these
species do not have any special protection.
Aquatic Species
Aquatic species that may occupy the project area include northern leopard frog (Lithobates pipiens – State
Species of Concern and BLM Sensitive), Great Basin spadefoot (Spea intermontana – BLM Sensitive) in
addition to several species without special status designations, such as tiger salamander (Ambystoma
tigrinum) and Woodhouse’s toad (Anaxyrus woodhousii). The Colorado River is home to a multitude of
native and non-native fish species in addition to special status species described previously in this report.
SECTION 4-203-G (6) (a) - DETERMINATION OF LONG AND SHORT-TERM EFFECTS ON
FLORA AND FAUNA
FLORA
The placement of a surface pipeline would have little to no lasting impact on important native vegetation.
In addition to the minor disturbance, much of the vegetation in the various plant communities affected by
the project have already been disturbed by previous developments and management practices. No special
status plant occurrences are known to exist nearby. Noxious weeds occurring in the area are discussed in
an accompanying IVNWMP prepared by WestWater for this project (WestWater 2017).
FAUNA
Colorado River Endangered Fishes
Designated critical habitat for two endangered fish species (Colorado pikeminnow and razorback sucker)
occurs in the Colorado River within the project area and critical habitat for two additional species
(bonytail and humpback chub) occurs downstream of the project near Grand Junction (Maddux et al.
1993). Colorado pikeminnow and razorback sucker have been documented in the river upstream as far as
Rifle (W. R. Elmblad, retired CPW fisheries biologist, pers. comm.).
Potential impacts to aquatic species would be limited to water depletions and increased sediment loads or
pollutants that could move from the project to the river. Implementation of a Spill Prevention, Control,
and Countermeasure Plan (SPCC), a Stormwater Management Plan (SWMP), and Best Management
Practices (BMPs) associated with this type of project will provide a good degree of mitigation for any
potential impacts. Water depletions are addressed by a Programmatic Biological Opinion issued by the
US Fish and Wildlife Service (USFWS 2008b).
Raptors
No raptor nesting habitat would be directly affected by the project. Short-term effects could include
temporary displacement of raptors in an avoidance area surrounding active construction areas due to
increased human presence and equipment motion and noise.
American Elk and Mule Deer
No significant amount of foraging habitat will be lost within the footprint of the project. No CPW
mapped migration corridors would be affected. Human presence and activity during construction may
affect animal distribution by creating avoidance areas.
WestWater Engineering Page 6 of 13 January 2017
Additional traffic resulting from this project would contribute minimally to vehicle related wildlife
mortality given the low speed limits and significant, long-term, local traffic. Fences can pose an
increased risk to big game and any required fencing should be constructed according to published
standards that reduce impacts to big game (Hanophy 2009).
Black Bear and Mountain Lion
Potential encounters between bears and personnel could occur if garbage or food is available on
construction sites. Mountain lions are occasionally observed in the area, but generally avoid human
contact. Incidences of human and bear/lion interactions sometimes result in the euthanasia of offending
animals by the CPW.
Small Mammals, Birds (BCC), and Reptiles
Depending on project timing, nesting habitat for migratory birds could be affected by people and
equipment during construction resulting in destruction of active bird nests. No vegetation removal beyond
mowing should be required for development of this project, which would temporarily reduce foraging
habitat for small mammals and birds. Human presence and activity may affect animal distribution. An
increase in traffic could result in vehicle related mortalities.
SECTION 4-203-G (6) (b) – DETERMINATION OF THE EFFECT ON DESIGNATED
ENVIRONMENTAL RESOURCES
Development of the project would not directly affect any designated critical wildlife or occupied plant
habitat for threatened or endangered species. Downstream habitats for aquatic species could be affected
by water depletions, pollutants, and sedimentation. This project would contribute minimally to cumulative
effects of habitat alteration in the area.
SECTION 4-203-G (6) (c) – IMPACTS ON WILDLIFE AND DOMESTIC ANIMALS
Creation of hazardous conditions: Some passerine bird species and small mammals may choose
to inhabit or nest on equipment or objects at the construction site. The inherent risks associated
with these structures are low given the short-term and transient nature of a surface pipeline
project. By closing or covering all ports, hatches, cavities, and openings (such as the ends of
pipes) this potential is decreased. Most non-game bird species and their nests are protected under
the Migratory Bird Treaty Act (16 U.S.C. 703-712; Ch. 128; July 13, 1918; 40 Stat. 755) and
damaging occupied nests could be considered a “take” resulting in a violation. Livestock and big
game will likely avoid the project site during construction.
Direct Construction Effects: Mowing prior to construction will temporarily remove nesting and
foraging habitat for a migratory and non-migratory birds, mammals, and reptiles. This affect
should be minor and short-term if the project takes place outside of nesting season (April-July).
Indirect Construction Effects: Additional human presence and activity related to construction
may influence spatial and temporal use of habitat surrounding the project by wildlife. Since the
surface pipeline would be developed adjacent to significant and long-term human presence
(county roads and other developments), the additional indirect effects in those areas would be
minimal.
Road-kill: Speed limits are relatively low and most wildlife in the area has become habituated to
vehicle traffic on public roads. The potential for vehicle related wildlife mortalities related
specifically to this project would be low.
WestWater Engineering Page 7 of 13 January 2017
REFERENCES
Andrews, R., and R. Righter. 1992. Colorado Birds: A Reference to Their Distribution and Habitat.
Denver Museum of Natural History. Denver.
BLM. 2009. BLM Colorado State Director’s Sensitive Species List. November 20, 2009 Update.
CPW. 2017a. State of Colorado species of concern list. Available online:
http://cpw.state.co.us/learn/Pages/SOC-ThreatenedEndangeredList.aspx. Accessed January 17,
2017.
CPW. 2017b. All species activity mapping data. Available online:
http://www.arcgis.com/home/item.html?id=190573c5aba643a0bc058e6f7f0510b7
Accessed January 17, 2017.
CWMA. 2013. S. Anthony, T. D’Amato, A. Doran, S. Elzinga, J. Powell, I. Schonle, K. Uhing. Noxious
Weeds of Colorado, Ninth Edition. Colorado Weed Management Association, Centennial.
Hammerson, G. A. 1999. Amphibians and Reptiles in Colorado, Second Edition. Colorado Division of
Wildlife, Denver.
Hanophy, W. 2009. Fencing with Wildlife in Mind. Colorado Division of Wildlife. Denver. Available
online:
http://wildlife.state.co.us/SiteCollectionDocuments/DOW/LandWater/PrivateLandPrograms/DO
WFencingWithWildlifeInMind.pdf
Kershaw, L., A. MacKinnon, and J. Pojar. 1998. Plants of the Rocky Mountains. Lone Pine Publishing,
Auburn, Washington.
Kingery, H. E. 1998. Colorado Breeding Bird Atlas. Colorado Bird Atlas Partnership, Colorado Division
of Wildlife, Denver.
Maddux, H., L. Fitzpatrick, and W. Noonan. 1993. Colorado River Endangered Fishes Critical Habitat.
Biological Support Document. U.S. Fish and Wildlife Service, Utah/Colorado Field Office, Salt
Lake City, Utah, 225 pp.
NRCS. 2017. Web Soil Survey, U.S. Department of Agriculture, Natural Resource Conservation Service,
Available online: http://websoilsurvey.nrcs.usda.gov. Accessed January 17, 2017.
Righter, R., R. Levad, C. Dexter, and K. Potter. 2004. Birds of Western Colorado Plateau and Mesa
Country. Grand Valley Audubon Society, Grand Junction.
Spackman, S., B. Jennings, J. Coles, C. Dawson, M. Minton, A. Kratz, and C. Spurrier. 1997. Colorado
Rare Plant Field Guide. Prepared for the Bureau of Land Management, the U.S. Forest Service,
and U.S. Fish and Wildlife Service by the Colorado Natural Heritage Program.
State of Colorado. 2005. Rules pertaining to the administration and enforcement of the Colorado Noxious
Weed Act, 35-5-1-119, C.R.S. 2003. Department of Agriculture, Plant Industry Division,
Denver, 78 p.
USFWS. 2008a. Birds of Conservation Concern 2008. U.S. Fish and Wildlife Service, Division of
Migratory Bird Management, U.S. Fish and Wildlife Service, Arlington, Virginia.
USFWS. 2008b. Programmatic Biological Opinion (PBO) (ES/GJ-6-CO-08-F0006) Re: BLM
Colorado River Fluid Minerals Program Water Depletions. USFWS, Ecological
Services. Grand Junction, Colorado
USFWS. 2012. Updated position paper on ESA consultations on greenback cutthroat trout, including the
cutthroat trout referred to as Lineage GB. Updated Oct 4, 2012.
WestWater Engineering Page 8 of 13 January 2017
USFWS. 2017. U.S. Fish and Wildlife Service Endangered Species List for the State of Colorado.
Available online:
http://ecos.fws.gov/tess_public/pub/stateListingAndOccurrenceIndividual.jsp?state=CO.
Accessed January 17, 2017.
Weber, W. A., and R. C. Wittmann. 2012. Colorado Flora, Western Slope. Fourth Edition, University
Press of Colorado, Boulder.
WestWater. 2017. Integrated vegetation and noxious weed management plan for Ursa Operating
Company, LLC’s proposed B&V Temporary Water Pipeline project. Grand Junction.
Whitson, T. D. (editor), L. C. Burrill, S. A. Dewey, D. W. Cudney, B. E. Nelson, R. D. Lee and R. Parker.
2001. Weeds of the West – 9th edition. Western Society of Weed Science in cooperation with
Cooperative Extension Services, University of Wyoming, Laramie.
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URSA OPERATING COMPANY, LLC.
B&V TEMPORARY WATER PIPELINE
Section 7-202 Protection of Wildlife Habitat Areas
Garfield County Land Use and Development Code
WILDLIFE
Colorado River Endangered Fishes
Designated critical habitat for four endangered fish occurs in the Colorado River within the project area.
Runoff from storms or snowmelt may carry increased sediment loads or pollutants from the pipeline to
the river. Implementation of a Spill Prevention, Control, and Countermeasure Plan (SPCC), a Stormwater
Management Plan (SWMP), and Best Management Practices (BMPs) associated with this type of project
will provide a good degree of mitigation for any potential impacts. Water depletions that could affect
aquatic species associated with the project are addressed under a Programmatic Biological Opinion issued
by the US Fish and Wildlife Service (USFWS 2008).
Raptors
Activities associated with the project have minimal potential to impact raptor populations as no raptor
nesting habitat would be directly affected, and no raptor nests are known to occur near the project area.
Indirect impacts would be related to displacement of foraging activities and the effect would be small
given the abundance of foraging habitat available and short term nature of surface pipeline construction.
Due to these factors, in addition to a high ongoing level of human activity in the general project area, it is
unlikely that the project would contribute to any adverse effects for raptor species.
American Elk, Mule Deer, Black Bear, and Mountain Lion
Implementation of the Integrated Vegetation and Noxious Weed Management Plan (IVNWMP)
(WestWater 2017) would help reduce the spread of noxious weeds in disturbed areas. Low speed limits
and the high volume of local traffic on area roads mitigate potential road kill. Facility fencing should be
consistent with published standards that reduce potential harm to wildlife (Hanophy 2009).
Black bear and mountain lion may occasionally be observed near the site and should not be approached if
encountered. Personnel may be unfamiliar with wildlife in the area and should be informed of the
potential for bear and lion interactions. Personnel should not feed or harass wildlife at any time. Trash
should be stored in bear-proof receptacles and/or removed from the site on a daily basis to prevent
attracting bears to the site. Negative interactions may result in euthanasia of problem animals.
Birds, Small Mammals, and Reptiles
Nesting cover for ground nesting birds and foraging habitat for numerous species could be affected by
mowing or by equipment during construction.
PRESERVATION OF NATIVE VEGETATION
Native vegetation would not be permanently removed for development of the project. Application of the
IVNWMP (WestWater 2017) would help inhibit the spread of noxious weeds within the project area.
Vegetation removal and soil disturbance during construction can create optimal conditions for the
establishment of invasive, non-native species. Vehicles and equipment traveling from weed-infested areas
into weed-free areas could disperse noxious or invasive weed seeds and propagates, resulting in the
establishment of these weeds in previously weed-free areas.
WestWater Engineering Page 2 of 2 October 2016
Several simple practices should be employed to prevent most weed infestations. The following practices
should be adopted for any activity to reduce the costs of noxious weed control through prevention. The
practices include:
Prior to delivery to the site, equipment should be thoroughly cleaned of soils remaining from
previous construction sites which may be contaminated with noxious weeds.
If working in sites with weed-seed contaminated soil, equipment should be cleaned of potentially
seed-bearing soils and vegetative debris at the infested area prior to moving to uncontaminated
terrain.
All maintenance vehicles should be regularly cleaned of soil.
Avoid driving vehicles through areas where weed infestations exist.
REFERENCES
Hanophy, W. 2009. Fencing with Wildlife in Mind. Colorado Division of Wildlife. Denver. Available
online:
http://wildlife.state.co.us/SiteCollectionDocuments/DOW/LandWater/PrivateLandPrograms/DO
WFencingWithWildlifeInMind.pdf
USFWS. 2008. Programmatic Biological Opinion (PBO) (ES/GJ-6-CO-08-F0006) Re: BLM Colorado
River Fluid Minerals Program Water Depletions. USFWS, Ecological Services. Grand Junction.
WestWater Engineering. 2017. Integrated Vegetation and Noxious Weed Management Plan for Ursa
Operating Company, LLC’s proposed B&V Temporary Water Pipeline project. Grand Junction.