Ex#13 Critical Areas Report 7-12-2022 OptimizedCritical Areas Report
for
Ponderosa Ridge East Preliminary Plat
site located in the
NW comer of Section 5, T24N, R44E, W.M.
City of Spokane Valley WA, Tax Parcel #44052.9011
July 12, 2022
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Biology
Soil &
Water,1nc.
Critical Areas Report
for
Ponderosa Ridge East Preliminary Plat
site located in the
NW comer of Section 5, T24N, R44E, W.M.
City of Spokane Valley WA, Tax Parcel #44052.9011
July 12, 2022
Retained by
Lanzce Douglass Construction
Contact Person: Lanzce Douglass
1402 E. Magnesium
Spokane, VVA 99217
Phone: (509) 951-4785
Email: lanzce@irentspokane.com
Investigated by
Biology Soil & VVater, Inc.
Contact Person: Larry Dawes, Principal Biologist
3102 N. Girard Road
Spokane Valley, VVA 99212-1529
Phone 509-327-2684
Email: bswinc@icehouse.net
LIST OF CONTACTS
Lanzce Douglass Construction
Contact Person: Lanzce Douglass
1402 E. Magnesium
Spokane, WA 99217
Phone: (509) 951-4785
Email: lanzce@irentspokane.com
Todd Whipple
Whipple Consulting Engineers
21 South Pines RD
Spokane Valley, WA 99206
(509) 893-2617
( toddw@whipplece.com)
Larry Dawes
Biology Soil & Water, Inc
3102 N. Girard Road
Spokane Valley, WA 99212
Phone 509-327-2684
bswinc@icehouse.net
Critical Areas Report
Ponderosa Ridge East Preliminary Plat
located in the
City of Spokane Valley, Spokane County WA
Tax Parcel #44052.9011
July 12, 2022
1.0 INTRODUCTION
In 2004, Biology Soil and Water, Inc. (BSW) submitted a Habitat Management
Plan (HMP) for the Ponderosa Ridge Planned Unit Development (PUD) Preliminary Plat
located in the NW comer of Section 5, T24N, R44E, W.M. (Figures 1-3). The west half
of the 2004 Ponderosa Ridge PUD was in Spokane County and the east half was in the
City of Spokane Valley. Part of the 2004 project was constructed in the County (west)
half of the project when the plat expired. No work was completed in the City of Spokane
Valley. A new Preliminary Plat for the site must be approved before the remainder of the
development can be completed. The currently proposed Ponderosa Ridge East
Preliminary Plat is the east half of the 2004 project. The proposed Preliminary Plat
consists of 81 lots on the 16.95 acre parcel (Figure 4). Open space is provided in six
tracts with a total combined area of 1.21 acres.
Under mandate of the Washington State Growth Management Act, the City of
Spokane Valley Municipal Code adopted Title 21: Environmental Controls. Section
21.40: Critical Areas mandates the protection of wetlands, fish, wildlife, and habitats.
The intent of these regulations is to avoid, minimize, rectify, reduce, or compensate for
impacts arising from land development and other activities affecting critical areas.
The conclusions in this report are based on an evaluation of habitat and species
data from Federal, State, and Local jurisdictions, an evaluation of construction plans and
specifications for the project, a literature review, and field investigations by the author of
this report. The project area was investigated for the following Federally listed species
(Appendix 1). The project will have no effect on the Threatened species Bull Trout or
proposed Bull Trout Critical Habitat. The project will not result in the destruction or
adverse modification of potential, designated, or proposed Critical Habitat or Essential
Fish Habitat for any fish species. The project will have no effect on the threatened
species Spalding's silene or the Yellow-billed cuckoo. The project will have no effect on
the Candidate species Monarch butterfly. There will be no significant adverse effect on
a.ny 11sted Species of Concern~
The priority habitats and species of Spokane County are adopted from the
Washington State Priority Habitats and Species Program (PHS) (WDF&W 1996). The
Washington Department of Fish and Wildlife (WDFW) Priority Habitats and Species
mapped for the site include White-tailed deer, Rocky Mountain Elk, the Gray Wolf, and
Shrub/Steppe habitat (Appendix 2). Only the White-tailed deer will be affected by this
project.
The Department of Natural Resources (DNR) Water Type Map depicts a Type N
and a Type U Water on adjacent property to the west (Figure 5). The DNR mapped Type
N water is over 400 feet from the Ponderosa Ridge East property, so the buffer does not
encumber the subject property. The Type U Water is depicted on the National Wetland
1
Ponderosa Ridge East
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LOCATED IN A PORTION OF
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SPOKANE VALLEY, WA
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CRITICAL AREAS:
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PONDEROSA RIDGE EAST
PRELIMINARY PLAT COVER
44TH AVE & FARR RD
PP1
JOB NUMBER
20·2798 SPOKANE VALLEY, WA
612122, 8:49 AM
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Inventory Map as a Riverine, Intermittent, Stream Bed, Seasonally Flooded (R4SBC)
wetland (Figure 6). The map does not depict the accurate location of the draw and the
mapped wetland/stream does not exist. Even if the mapped stream/wetland did exist at
the mapped location the associated buffer would not encumber the Ponderosa Ridge East
Preliminary Plat. The Ponderosa Ridge East Preliminary Plat is not encumbered by a
wetland, stream, or the buff er associated with a stream or wetland.
The Critical Areas map designations listed for the site require a qualified biologist
to field verify the accuracy of all mapped designations, determine if the proposed
development would have adverse impacts on a priority habitat or species, and prepare a
Habitat Management plan that addresses the associated issues.
2.0 SITE AND HABITAT DESCRIPTION
In 2004, Biology Soil and Water, Inc. (BSW) submitted a Habitat Management
Plan (HMP) for the Ponderosa Planned Unit Development (PUD) Preliminary Plat. The
2004 Preliminary Plat proposed 82 lots in the City of Spokane Valley (east half) and 100
lots in Spokane County (west half). When the plat expired, only part of the project had
been constructed in the County portion of the project and none of the project had been
constructed in the City of Spokane Valley. The portion constructed in the County before
the plat expired was named Ponderosa Ridge I. In 2022, a Preliminary Plat for Ponderosa
Ridge II was submitted to complete construction of the Spokane County part of the
original 2004 plat. The currently proposed Ponderosa Ridge East Preliminary Plat is for
that portion of the original 2004 plat located in the City of Spokane Valley. The
Ponderosa Ridge II development defines the West border of the Ponderosa Ridge East
property. Existing residential development on the south side of 44th Avenue, west side of
Farr Road, and north side of Holman Road define the north, east, and south sides of the
property respectively.
The 2004 Habitat Management Plan (HMP) proposed N/S wildlife travel
corridors through the west part of the project located in Spokane County. The
topographic draw that bisects the County portion of the site from north to south was
protected as natural travel corridor with forested habitat utilized by wildlife. A powerline
easement provides an alternative wildlife travel route through the northwest part of the
site. In 2004, no travel corridor was proposed for the City (east) part of the project
because it was already bordered by residential development on the north, east, and south
sides and construction of the County part of the project would block wildlife access from
the west.
In Spokane County, homes already constructed on the east and west sides of
Ponderosa Lane extend about 850 feet south from 44th A venue. The proposed Ponderosa
Ridge II development will extend Ponderosa Lane south to the south end of property with
new home constructed on the east and west sides of that street. The completion of that
development phase in Spokane County will block wildlife access to the Ponderosa Ridge
East site from the west.
Deer, elk, coyotes, wolves, bear, cougars, racoons, skunks, and other small
mammals will only be able to enter the Ponderosa East development by crossing streets
and yards in surrounding residential neighborhoods. A wildlife travel corridor that links
Ponderosa Ridge East to habitat patches on adjacent properties is not an option. Any
open space tract created within the project limits must start within residential
7
June 2, 2022
Wetlands D
D Estuarine and Marine Deepwater []
D Estuarine and Marine Wetland D
Freshwater Emergent Wetland • Freshwater Forested/Shrub Wetland D
Freshwater Pond D
Ponderosa
Lake
Other
Riverine
This map is for general reference only. The US Fish and Wildlife
Service is not responsible for the accuracy or currentness of the
base data shown on this map. All wetlands related data should
be used in accordance with the layer metadata found on the
Wetlands Mapper web site.
National Wetlands Inventory (NWI)
This page was produced by the NWI mapper
development and end in residential development. The Ponderosa East phase of the
development includes 6 open space tracts with a combined area of 1.21 acres. All 6 of
the tracts provide only small, isolated fragments of potential habitat for birds with no
functional access routes or habitat value for large mammals.
The site is currently dominated by an open canopy, mixed age class, Ponderosa
pine overstory. Small patches of aspen/snowberry habitat type are scattered along the
hillside. Individual aspen patches on the subject property are considerably less than two
acres in area so they do not meet the WDF&W definition of Priority Habitat. Large
patches of snowberry and service berry dominate the shrub understory. Rose, ocean
spray, hawthorn, and Oregon grape are also well represented. The shrub clusters provide
protective cover and browse opportunities for deer, foraging opportunities for birds, and
open space for resident and migratory species. The presence of a small amount of
knapweed indicates a minor degree of historical disturbance.
3.0: SITE INVESTIGATION FINDINGS
3.1 Vegetative Species Observed at the Site
Upland tree, shrub, forb, and grass vegetative classes identified at the site are
described in Table 1. No rare, sensitive, endangered, or otherwise protected plant species
were identified.
Table 1. Plant Species.
Common Name Scientific Name Alnha Code
Trees: black hawthorn Crataegus douglasii CRDO
Ponderosa pine Pinus ponderosa PIPO
quaking aspen Populus tremuloides POTR
Shrubs: service berry Amelanchier alnifolia AMAL
kinnikinnik Arctostaphylos uva-ursi AUUR
tall Oregon grape Berberis aquifolium BEAQ
redstem ceanothus Ceanothus sanguineus CESA
creeping Oregon grape Berberis repens BERE
oceans pray Holodiscus discolor HODI
mock orange Philadelphus lewisii PHLE
golden currant Ribes aureum RIAU
Nootkarose Rosa nutkana RONU
Wood's rose Rosa woodsii ROWO
snowberry Symphoricarpos albus SYAL
Herbs: yarrow Achillea millefolium ACMI
arrow leaf balsamroot Balsamorhiza sagitata BASA
thistle* Cirsium vulgare CIVU
willow weed Epilobium watsonii EPWA
St. John's wort* Hypericum perforatum HYPE
spotted knapweed * Centaurea maculosa CEMA
prickly lettuce Lactuca serriola LASE
dalmatian toadflax * Linaria dalmatica LIDA
common plantain Plantago major PLMA
tansy Tanacetum potentilloides TAPO
9
yellow salsify * Tragopogon dubius TRDU
mullein* Verbascumthapsus VETH
vetch Vicia cracea VICR
Grasses: brome-grass * Bromus inermis BRIN
Idaho fescue Festuca idahoensis FEID
bluebunch wheatgrass Agropyron spicatum AGSP
pinegrass Calamagrostis rubescens CARU
cheatgrass* Bromus tectorum BRTE
bulbous bluegrass Paa bulbosa POBU
Kentucky bluegrass Paa pratensis POPR
Sandberg bluegrass Paa secunda POSE
* -introduced/exotic species
3.2: Investigation for Presence of White-tailed Deer and Elk:
The site was investigated on September 2, 3, 6 and 8, 2004, May 30 and 10 July
2022 to assess the quantity and quality of elk and white-tailed deer habitat, assess the
extent of habitat utilization by elk and deer, and to determine the number of each species
currently living on the site.
Presence of animals: A systematic search of the site and adjacent one-
quarter mile perimeter was conducted once early in the early morning and
two times in the evening.
Investigation for sign: The site was also investigated for signs of elk and
white-tailed deer presence such as trails, scat, beds, scrapes/rubs, browsed
vegetation, wallows, etc.
Perimeter survey and habitat summary: A one-quarter mile perimeter
beyond the property boundary was assessed to determine utilization of
habitat adjacent to the property and off-site influences on the elk and
white-tailed deer populations. Elk and white-tailed deer habitat was
assessed and is summarized below.
4.0 USF & W Listed Species
The USFWS and NMFS species lists were accessed on their websites on
61212022. No NMFS species are listed for the vicinity. The USF&W list indicated the
potential presence of the species and critical habitat(s) shown in Table 2 (and in
Appendix 1 ).
1 Tab e 2. USFWS listed species and critical habitats potentiallv present in the vicinity of
Species ESU/DPS Federal Status Designated Critical Habitat
Bull trout Salvelinus confluentus Col River Threatened Yes
Spalding's silene, Silene spaldinRii Threatened No
Monarch Butterfly Danaus p/exivvus Candidate No
Yellow-billed cuckoo, Coccyzus Threatened No
americanus,
10
4.1: Bull Trout (Salvelinus confluentus) Threatened
The U.S. Fish and Wildlife Service (USF&WS) lists the Columbia River
population of bull trout as threatened. Small pockets of bull trout are present in isolated
habitat fragments in the main stem and tributaries of the Columbia River. One isolated
fragment of the Columbia River segment includes Coeur d'Alene Lake, its tributaries in
the drainage basin, and the Spokane River. Bull trout populations have been identified in
Coeur d'Alene Lake and three tributaries in its sub-basin. There is no stream on the
subject property and the mapped stream on adjacent property does not have a surface
water connection to the Spokane River so the project will have No Effect on Bull Trout
or proposed Bull Trout Critical Habitat.
4.2: Spalding's catchfly (Silene spaldingii), Federal Status: Threatened
The survey for Spalding's silene was completed by walking pedestrian survey
transects that were spaced to allow 100% visual coverage of the vegetative canopy. The
distance between transect center lines was reduced as necessary to account for differences
in terrain, vegetation density, and ground surface visibility.
Silene spaldingii populations have been identified in the Palouse Grasslands of
west-central Idaho and southeastern Washington; the Channeled Scablands in eastern
Washington; the Blue Mountain Basins in northeastern Oregon; the Canyon Grasslands
of the Snake River and its tributaries in Idaho. Within the Canyon Grasslands, Silene
spaldingii is found at the lowest and highest elevations rangewide from 365 to 1,615
meters (1,200 to 5,300 feet) (ICDC 2007; summarized in USFWS 2007). Spalding's
silene is found primarily in open grasslands and Idaho fescue/snowberry associations at
elevations of 1900-3050 feet. Some of these sites occur in a mosaic of grassland and
Ponderosa pine forest. Spalding's silene populations have been found on all aspects,
although there seems to be a preference for slopes that face north. On drier sites, the
species can be found on the bluebunch wheatgrass/Idaho fescue association. Some of the
preferred conditions exist on this site.
Each Silene spaldingii stem bears four to seven (up to 12) pairs of 2-3 inch long,
lance-shaped leaves (Hitchcock et al., 1964 ). It has swollen nodes where the leaves
attach to the stem. The plant is covered in dense sticky hairs that frequently trap dust and
insects. Flowers have a tubular calyx approximately 0.6 inches long; the pale white
petals extend slightly beyond the sepals. Flowers bloom from mid-July through August
and sometimes into September. BSW investigated the site in late May but revisited the
site on 10 July 2022 because the timing of the May site investigation occurred before the
plant species would be flowering.
The project biologist is a qualified botanist, is familiar with the species, and has
observed it at other locations. Silene spaldingii overlaps in range and is somewhat
similar in appearance with several other species in the genus, however, no species in that
genus were at the project location so confusion of species was not an issue. The project
biologist conducted a uniform grid search pattern covering each project area. No
populations of Spalding's silene were identified in the Project Area during the field
investigations. The project will have NO EFFECT on Spalding's Silene and will not
result in the destruction or adverse modification of potential, designated or
proposed Spalding's silene Critical Habitat.
11
4.3: Monarch Butterfly (Danaus plexippus)
During the summer, Monarch butterflies mate and lay eggs several times until
September when the final generation must migrate south to avoid lethal winter conditions
in the Spokane area. Due to habitat destruction, fewer Monarchs return each year to their
summer range in the Spokane vicinity. Monarch reproduction relies entirely on the
milkweed plant. Female monarchs lay their eggs on the underside of milkweed leaves.
Monarch caterpillars feed exclusively on milkweed and cannot feed on any other plant.
The 2022 plant survey confirmed that no milkweed or potential Monarch habitat occurs
in the vicinity of the Project Area. The project will have NO EFFECT on the Monarch
butterfly and will not result in the destruction or adverse modification of potential,
designated or proposed Monarch butterfly Critical Habitat.
4.4: Yellow-billed Cuckoo (Coccyzus americanus), Federal Status: Threatened
The yellow-billed cuckoo was formerly a very rare summer visitor to western
Washington, especially in the Puget Sound area [Roberson 1980]. Jewitt et al. (1953)
described the former breeding range in Washington as ranging north to Bellingham, east
to Ellensburg, south to Vancouver, and west to Grays Harbor. There are only two
published records of yellow-billed cuckoo in eastern Washington. Yellowbilled cuckoos
were detected on July 21, 1956, 20 miles north of Grand Coulee Darn in Okanogan
County [Weber and Larrison 1977] and in June 1978 at George, Grant County [Roberson
1980].
The investigation for the Yell ow-billed cuckoo focused on specific habitat
requirements of that species. Cuckoos prefer to nest in areas with at least 10 hectares
(ha) (25 acres) of contiguous riparian woodland [Laymon 1998]. The typical patch size
is 20 ha (50 acres) or greater, and the likelihood of occupancy increases dramatically with
increasing patch size, but they have been found breeding in patch sizes as small as 4 ha
(10 acres) along the Colorado River in southern California [Johnson, Matthew J., 2007].
Yellow-billed cuckoo's nest in undisturbed stands of cottonwood/willow galleries greater
than 10 acres in total area and greater than 100 meters wide along waterways.
The project area does not contain, and is not close to, adequate habitat patches for
that species. The yellow-billed cuckoo is known not to utilize any habitat with
characteristics of those found on or adjacent to this project. This project will not impact
yellow-billed cuckoo populations or habitat components. There is no suitable habitat for
the yellow billed cuckoo in the vicinity of this project. The project will have NO
EFFECT on yellow-billed cuckoo or any designated or proposed critical habitat for that
species because the species was not observed, there is no suitable habitat present, and
there i:> no po:>:>ibility of effect:> to the :>pccic::i or habitat::i from the project.
5.0 WDF&W Priority Habitat and Species Assessment (Appendix 2)
5.1 White-tailed Deer (Odocoileus virginianus) Presence and Habitat:
Common white-tailed deer habitat characteristics on the site include mixed
species woodlands in multiple successional stages, two types of edge habitat, high
availability of cover, presence of seasonal and permanent water nearby, low elevation,
short, diversified slopes, and high quantity and quality of browse. White-tailed deer
browse that is abundant on the site includes common snowberry, rose species, Oregon
grape, kinnikinnik, and ceanothus.
12
Winter Range:
Winter ranges are generally occupied from early December through late March,
depending on weather conditions and food availability. Winter range is the most critical
component of landscapes used by deer. The quality and quantity of available winter
range are the primary limiting factors for white-tailed deer populations in Washington.
Critical areas of closed-canopy (stands of at least 11 min height with overstory cover of
at least 70%) that provide snow intercept are limited on the subject property. Deer
activity on the site is also limited by the small size of the property, surrounding
residential development, and because there is no water on the site. However, the site has
some winter range characteristics including low elevation, deciduous and coniferous tree
stands, and an abundant browse supply so the site is currently included as part of the
home range for a small group of deer.
Spring/Summer/Fall Range:
The site provides classic spring, summer, and fall range characteristics for white-
tailed deer including sloping meadows dominated by grasses, low elevation, and high
quantity and quality browse (including ceanothus, rose, and common snowberry ), escape
and thermal cover, natural travel corridors, and a small, forested area with some diversity
of forest successional stages. The limiting factors for white-tailed deer utilization of the
site are lack of on-site water and the relatively small, forested patch for cover. Three
White-tailed deer were observed on the site on May 30, 2022. The presence of browsed
shrubs, pellet piles, and a heavily used trail system, the identification of bed sites, and a
deer skeleton confirm the site is part of the home range of a small number of white-tailed
deer.
5.2 Elk ( Cervus elaphus) Presence and Habitat:
Elk prefer grazing but also browse on trees and shrubs, depending on availability
and nutrient content. The site provides food for elk but given the proximity and density
of existing residential development and high road density, the site is unsuitable for elk.
Elk may have historically wandered through the subject property, but under current
conditions it is very unlikely. The unpeopled acres of the Dishman Hills and Iller Creek
Conservation Areas on the north, west and south would be highly preferred elk travel
routes. No sign of elk was observed on the subject property. BSW concludes that the
Ponderosa property does not offer the seclusion required by elk, but the wooded draw on
adjacent property to the west could serve as a travel corridor in the unlikely event that elk
wander into the project area. The project will have no effect on elk or elk habitat.
5.3 Gray wolf (Canis lupus) Endangered
Gray wolves occupy a wide spectrum of remote habitats that contain an adequate
year-round prey base of ungulates, alternative prey, secluded denning and rendezvous
sites, and isolation from human activity. No known populations or individual wolves are
known to utilize or depend on the subject property as an important component of their
home range. No scat, tracks, denning, or potential rendezvous sites were identified on the
site. The surrounding residential development, the presence of primary and secondary
roads, relative scarcity of prey species, and the absence of rendezvous and denning sites
make the likelihood of adverse impact to the gray wolf very low.
13
It is possible that the gray wolf could wander through the site in search of prey,
but due to lack of seclusion, wolves would not utilize the site for denning or rearing
young. Dispersion of wolves could occur if they were traveling through the site when
heavy equipment was operating during project construction. Traffic on adjacent roads
and human activity near the site would probably deter wolves from coming near the site
during the daytime when project construction activity would be under way. Once
construction is complete, human disturbance associated with the residential area would
discourage wolf activity. Unpeopled open space outside the project area in the Iller
Creek and Dishman Hills Conservation Areas provides adequate habitat for wolves to
move if they were disturbed while passing through the vicinity. The project will have no
effect on wolves.
5.4 Shrub/Steppe Habitat
WDF&W used the boundary of this 16.95 acre tax parcel to define a shrub/steppe
habitat polygon on the PHS map. WDF&W defines Shrub-Steppe as a "nonforested
vegetation type consisting of one or more layers of perennial bunchgrasses and a conspicuous but
discontinuous layer of shrubs." Sagebrush is usually a dominant or co-dominant shrubsteppe
species, but the species snowberry (Symphoricarpos albus) and rose (Rosa spp.) that occur on the
subject property are often present in more meadowlike expressions of the shrub-steppe habitat
type. The subject property has a high quality, healthy, mature, and diverse shrub canopy.
The grass species Idaho fescue (Festuca idahoensis), Bluebunch wheatgrass (Pseudoroegneria
spicata), and Sandberg bluegrass (Poa secunda), that are present on the subject property also
occur in shrubsteppe habitat.
However, there is no sagebrush on the site and the bunchgrasses identified on this site
also occur in wetter locations and forested habitat types throughout the northwest as do
snowberry and rose species. The subject property has an open canopy Ponderosa pine overstory
because it receives more precipitation than areas defined as shrubsteppe habitat. The tree
canopy also includes a patch of 60-70 aspens in the 3-10 dbh class with a snowberry and
Oregon grape understory. The site has large patches of hawthorn shrubs with Oregon
grape, snowberry, and rose on the perimeters. Aspens and hawthorns are found in
landscape positions with greater precipitation and higher soil moisture holding capacity
than occurs in steppe habitat.
WDF&W defines Shrub-Steppe habitat as containing various habitat features, including
diverse topography, riparian areas, and canyons. This small fragment of habitat does not have a
variety of habitat features or habitat diversity. This landscape position is 100% upland in
character, and the site has a nice upland shrub canopy, but it is not shrubsteppe habitat as
defined by the WDF&W guidance used to describe and identify that habitat type.
5.5 Investigation of Other Wildlife Presence:
Several wildlife species utilize the open Ponderosa pine woodlands and
grassland/mixed shrub plant communities present at the project area. Systematic searches
were conducted during the early morning and evening hours for mammals, raptors, and
songbirds in 2004 and 2022. All observations were recorded, and overall wildlife habitat
quality was assessed. Besides deer, no protected species were observed on the site.
14
Table 3: Animal Species (or sign) Observed in 2004 and/or 2022
Common Name Scientific Name
Mammals: coyote Canis latrans
Birds:
white-tailed deer Odocoileus virginianus
vole Microtus spp.
yellow-pine chipmunk Eutamias amoenus
black-billed magpie
black-capped chickadee
mourning dove
American robin
pygmy nuthatch
California quail
chipping sparrow
American goldfinch
house sparrow
ring-necked pheasant
American crow
white-breasted nuthatch
5.6 Investigation of Other Critical Areas (Appendix 4)
The Marble soil series mapped by the NRCS Web Soil Survey are loamy sand in
the upper 8 inches underlain by sand to bedrock at 80 inches. The soils are well-drained.
The site is described by FIRMette as an Area of Minimal Flood Hazard. There are no
mapped geohazard areas on the site.
6.0 HABITAT MANAGEMENT PLAN
The following Habitat Management Plan elements will be included in the
Declaration of Protective Covenants.
1) Ponderosa Ridge East Will Form a Homeowners Association.
The Declaration of Protective Covenants of the homeowner' s association will
include the provisions for wildlife habitat protection described in this HMP.
2) Retain native vegetation on the lots.
To the extent allowed by fire codes, homeowners are encouraged retain native
vegetation including the open canopy forested component and understory shrub cover
habitat to maximize food, thermal protection, hiding cover, nesting, and brooding cover
for resident birds and mammals.
Resource availability, specifically food and nest opportunities, are determining
factors of the size and species richness of the bird community. Impacts on relative
density, species richness, breeding, habitat, seasonal range dynamics and movement
corridors will occur in proportion to habitat loss from the project. Homeowners are
encouraged to landscape yards to provide multiple canopy levels for birds.
3) Minimize site disturbance beyond the manicured yard.
Homeowners are encouraged to build comfortable, nicely manicured yards but to
minimize site disturbance beyond the manicured yard. Minimize the removal of native
vegetation beyond the manicured yard to maximize the quantity and quality of wildlife
habitat. Homeowners are encouraged to enhance their properties with native vegetation
from the species list provided below.
15
4) Homeowners shall manage noxious weeds as mandated by RCW 17.10, Spokane
County, and The City of Spokane Valley.
Weed control along roads and in common areas shall be rigorously managed by
the homeowner's association. Noxious weeds will explode along new roads, open space
tracts, and on homesites as soon as the soils are disturbed. HOA funds must be allocated
for annual weed monitoring and control. Weed control measures shall be implemented in
ways that do not adversely impact native vegetation. Homeowners shall manage noxious
weeds on individual parcels as mandated by RCW 17.10, The City of Spokane Valley,
and Spokane County.
5) Residents shall restrain free-ranging pets.
Scavenging and predation on eggs and nestlings by rabbits, squirrels, mice,
coyotes, opossums, raccoons, and skunks contribute to the steady annual attrition rate of
birds. However, predation by domesticated dogs and cats has a devastating effect on
resident bird populations. It is estimated that domesticated cats in North America kill 4
million songbirds everyday. Residents shall not allow pets to roam :freely to avoid
impacts to the resident bird community. City/County Ordinances shall be strictly
interpreted with respect to specific language prohibiting livestock and the restraint of
pets.
6) Disturbed areas shall be reseeded with native grasses.
Any disturbed soils in dedicated open space tracts shall be re-seeded with native
grasses where maintenance is not required. This will prevent soil erosion and noxious
weed invasion when earth-moving activities are completed. A mixture of native grasses
will be selected to maintain the ecological integrity of the site. Once replanted, these
areas should be left in a natural condition to provide food, cover, and refuge for wildlife.
7) Landscape to avoid human/animal conflicts.
Human/animal conflicts may be reduced by thoughtful landscaping practices.
Preserve existing vegetation and landscape with native plant materials with the
expectation that deer will eat your shrubs. Or landscape with plants that deer do not find
palatable. The Spokane County Conservation District can provide a list of unpalatable
species. District extension agents can also provide homeowners with a list of native trees
and shrubs offered for sale by that agency each spring.
Table 4: White-tailed Deer Vegetation Preferences
Stratum
Tree:
Common Name
Rocky mountain maple
paper birch
black hawthorn
Douglas fir
ponderosa pine
quacking aspen
black cottonwood
willow
western red cedar
16
Scientific Name
Acre glabrum
Betula sp.
Crataegus douglasii
Pseudostuga menziesii
Pinus ponderosa
Populus tremuloides
Populus trichocarpa
Salix sp.
Thuja plicata
hemlock Tsuga heterophylla
Shrub: kinnikinnik: Actostaphylos uva-ursi
serviceberry Amelanchier alnifolia
creeping/low Oregon grape Berberis repens
redstem ceanothus Ceanothus sanguineus
deerbrush, buckbrush Ceanothus velutinus
red-osier dogwood Cornus stolonifera
mytle boxwood Pachistima myrsinites
blue elderberry Sambucus cerulea
common snowberry Symphoricarpus a/bus
Herb: wild strawberry Fragaria virginiana
trumpet/orange honeysuckle Lonicera ciliosa
clubmoss Lycopodium selago
thimbleberry Rubrus parviflora
blackberry/raspberry Rubrus sp.
huckleberry Vaccinium sp.
Other: any berry or fruit, mushrooms, arboreal lichens, moss, agricultural crops.
8) Landscaping should enhance wildlife habitat.
The replication of structural complexity, vertical stratification, and microhabitat
diversity should be emphasized in the planting design. Shrubs should be planted with the
goal of enhancing wildlife habitat. The vegetation should be planted in patches, have
curving edges, and not be planted in a uniform manner.
Rationale
Structural complexity refers to the arrangement and degree of interspersion of
plant community types throughout the system. Complex structural patterns (such as
variable patch size, curving edges, and high degree of interspersion between species)
increase the value of a system for wildlife. Good wildlife habitat consists of open areas
interspersed with clusters of vegetation, several horizontal layers, and a variable
structural pattern.
Vertical stratification describes a community with good structural diversity and
several horizontal layers (logs, woody debris, forbs, shrubs, and trees). Woody debris
provides travel routes, perch sites, cover, and thermal refuge for a variety of small
mammals and ground nesting birds.
Microhabitat diversity refers to variety in microhabitat types. Examples of
microhabitat types include herbaceous cover and shrubs that provide food, habitat, and
substrate for a variety of plants and animals.
7.0 CONCLUSIONS
The best way to preserve wildlife species density and species richness is to
minimize human intrusion into their domain. Animal species have varying degrees of
tolerance to human activity. Some birds build their nests on human constructions,
communicate over traffic, eat our garbage, and move freely among the cars on our streets.
On the other extreme, some species require hundreds of square miles of unpeopled land
for their homes.
17
The Growth Management Act (GMA) suggests that we stop urban sprawl and
preserve areas with a distinct rural character. The GMA says that by increasing human
density within a delineated boundary we will preserve wildlife habitat outside of the
boundary. In writing Habitat Management Plans, biologist's endeavor to find ways to
accommodate increased housing density within the urban growth boundaries while
maintaining green space and wildlife corridors in the same area. These objectives are not
always compatible and must be viewed in the larger context of the GMA goals of
preserving rural character and wildlife habitat outside the growth boundaries. These
GMA goals reflect the fact that most species are not well adapted to life in an urban
environment. This development sits on the edge of the Urban Growth Boundary.
Every new development results in a loss of wildlife habitat. Little can be done to
compensate for the loss of habitat caused by an increasing human population. The best
we can do is what we are doing, relegating growth to areas within the urban growth
boundaries and building at high density. As the population of Spokane County continues
to grow, there is no alternative to maximizing density in designated growth areas to
protect undisturbed wildlands outside of the growth boundary. People and animals must
both adjust to increasing density inside the urban growth boundary.
The 2004 Preliminary Plan and Habitat Management Plan was designed to
accommodate wildlife travel through the west part of the development as dictated by
natural topography and habitat features. No travel corridors were proposed in the
Ponderosa Ridge East part of the site because existing residential development on the
south side of 44th Avenue, west side of Farr Road, and north side of Holman Road denied
wildlife access to the site from the north, east, and south sides of the property
respectively. The Ponderosa Ridge II development will block wildlife access to the
Ponderosa Ridge East site from the west. The Ponderosa East site will be surrounded by
residential development. White-tailed deer live within a well-defined home range with
an area of about one square mile. The proposed development will eliminate part of the
home range of White-tailed deer living in the vicinity. Resident deer will have to adjust
their home range boundary to rely more on adjacent forested land to the south and west
that is outside the Urban Growth Boundary. The remaining fragments of habitat within
the development will still be accessible by birds.
18
8.0: LIMITATIONS
Within the limitations of scope, schedule, and budget, BSW services have been
executed in accordance with best available science and generally accepted professional
practices for the conditions at the time the work was performed. This report is not
intended to represent a legal opinion. Specifically, there is no positive or negative
recommendation towards the purchase, sale, lease, or construction on the subject
property. Now nt, e ressed or implied, is made.
Larry Dawes
Principal Biologist
Biology Soil & Water, Inc.
3102 N. Girard Road
Spokane Valley, WA 99212-1529
Phone 509-327-2684
Email: bswinc@icehouse.net
19
7-12-;(. o 2 2-
Date
BIBLIOGRAPHY AND SUGGESTED REFERENCES
Berglund, Erwin R.. 1976. Seeding to Control Erosion Along Forest Roads. Extension
Circular 885. Oregon State University Extension Service. 6-8p.
Cooper, Stephen V., Kenneth E. Neiman, and David W. Roberts. 1991. Forest habitat
Types of Northern Idaho: A second Approximation. USDA: Forest Service;
Intermountain research Station. General Technical Report INT-236. 143 p.
Forman, R. T. and M. Gordon. 1986. Landscape Ecology. John Wiley and Sons, New
York. 619 p.
Grubb, P. J. 1977. The maintenance of species richness in plant communities: The
importance of regeneration niche. Biological Review 52: 107-145.
Gerlach, D., S. Atwater, and J. Schnell. 1994. The Wildlife Series: Deer. Stackpole
Books, Pennsylvania. 174-243p.
Hesselton, William T., & RuthAnn Manson Hesselton. 1982. White-tailed deer. in Wild
Mammals of North America. edit. by Chapman, J. A., and G. A. Feldharner. The
John Hopkins University Press, Baltimore and London. 878-902p.
Hitchcock, C. Leo, and Arthur Cronquist. 1994. Flora of the Pacific Northwest.
University of Washington Press, Seattle, WA. 730p.
Marchinton, R. L., and D. H. Hirth. 1984. Behavior. in White-tailed Deer: Ecology and
Management. Ed by L. K .. Halls. Stackpole Books, Pennsylvania.
Martin, A. C., H. I. Zim, and A. L. Nelson. 1951. American Wildlife and Plants. Diver
Publications, Inc., New York. 484 p.
McCaffery, K. R., and W. A. Creed. 1969. Significance of forest openings for deer in
northern Wisconsin. Technical Bulletin 44. Madison: Wisconsin Department of
Natural Resources. 104 p.
Orme, M. L., and T. A. Leege. 1975. The reproduction ecology ofredstem (Ceanothus
sanguineus). Job Completion. Rep. Job 6, Project W-160-R-2. Boise: Idaho Fish
and Game Department. 95 p.
Singer, F. J. 1979. Habitat partitioning and wildlife relationships of cervids in Glacier
National Park, Montana. Journal of Wildlife Management. 43(2):437-444.
Smith, R. L., and J. L. Loggin. 1984. Basis of Role and Management. in White-tailed
Deer: Ecology and Management. Ed by L. K .. Halls. Stackpole Books,
Pennsylvania. 203-646p.
20
Spokane County Public Works Department: Building and Planning Division, Critical
Areas Ordinance for the Protection of Wetlands, Fish and Wildlife Habitats and
Geo-hazard Areas. Spokane County, WA. 69p.
Washington Department of Fish and Wildlife. Priority Habitats and Species List
updated June 2022. Habitat Program. Olympia, Washington.
Washington Department of Fish and Wildlife and the Upper Columbia Basin Working
Group of Timber, Fish and Wildlife (TFW). 1996. Deer Winter Range. WDFW
96-3-FS104. Olympia, Washington. 2p.
Wilson, A. D .. 1969. A Review of browse in the nutrition of grazing animals. Journal of
Range Management 22:23-28.
Zim, H. S., A. C. Martin, and A. L. Nelson. 1961. American Wildlife & Plants: A Guide
to Wildlife Food Habits. Dover Publications, Inc. New York, NY.
21
Appendix 1
USF & W Threatened and Endangered Species
22
In Reply Refer To:
United States Department of the Interior
FISH AND WILDLIFE SERVICE
Washington Fish And Wildlife Office
510 Desmond Drive Se, Suite 102
Lacey, WA 98503-1263
Phone: (360) 753-9440 Fax: (360) 753-9405
Project Code: 2022-0049726
Project Name: Painted Hills PRD
June 02, 2022
Subject: List of threatened and endangered species that may occur in your proposed project
location or may be affected by your proposed project
To Whom It May Concern:
The enclosed species list identifies threatened, endangered, proposed and candidate species, as
well as proposed and final designated critical habitat, that may occur within the boundary of your
proposed project and/or may be affected by your proposed project. The species list fulfills the
requirements of the U.S. Fish and Wildlife Service (Service) under section 7( c) of the
Endangered Species Act (Act) of 1973, as amended (16 U.S.C. 1531 et seq.).
New information based on updated surveys, changes in the abundance and distribution of
species, changed habitat conditions, or other factors could change this list. Please feel free to
contact us if you need more current information or assistance regarding the potential impacts to
federally proposed, listed, and candidate species and federally designated and proposed critical
habitat. Please note that under 50 CFR 402.12(e) of the regulations implementing section 7 of the
Act, the accuracy of this species list should be verified after 90 days. This verification can be
completed formally or informally as desired. The Service recommends that verification be
completed by visiting the ECOS-IPaC website at regular intervals during project planning and
implementation for updates to species lists and information. An updated list may be requested
through the ECOS-IPaC system by completing the same process used to receive the enclosed list.
The purpose of the Act is to provide a means vvhereby threatened and endangered species and the
ecosystems upon which they depend may be conserved. Under sections 7(a)(l) and 7(a)(2) of the
Act and its implementing regulations (50 CFR 402 et seq.), Federal agencies are required to
utilize their authorities to carry out programs for the conservation of threatened and endangered
species and to determine whether projects may affect threatened and endangered species and/or
designated critical habitat.
A Biological Assessment is required for construction projects (or other undertakings having
similar physical impacts) that are major Federal actions significantly affecting the quality of the
human environment as defined in the National Environmental Policy Act (42 U.S.C. 4332(2)
(c)). For projects other than major construction activities, the Service suggests that a biological
06/02/2022
evaluation similar to a Biological Assessment be prepared to determine whether the project may
affect listed or proposed species and/or designated or proposed critical habitat. Recommended
contents of a Biological Assessment are described at 50 CFR 402.12.
2
If a Federal agency determines, based on the Biological Assessment or biological evaluation, that
listed species and/or designated critical habitat may be affected by the proposed project, the
agency is required to consult with the Service pursuant to 50 CFR 402. In addition, the Service
recommends that candidate species, proposed species and proposed critical habitat be addressed
within the consultation. More information on the regulations and procedures for section 7
consultation, including the role of permit or license applicants, can be found in the "Endangered
Species Consultation Handbook" at:
http://www.fws.gov/endangered/esa-library/pdf/TOC-GLOS.PDF
Migratory Birds: In addition to responsibilities to protect threatened and endangered species
under the Endangered Species Act (ESA), there are additional responsibilities under the
Migratory Bird Treaty Act (MBTA) and the Bald and Golden Eagle Protection Act (BG EPA) to
protect native birds from project-related impacts. Any activity, intentional or unintentional,
resulting in take of migratory birds, including eagles, is prohibited unless otherwise permitted by
the U.S. Fish and Wildlife Service (SO C.F.R. Sec. 10.12 and 16 U.S.C. Sec. 668(a)). For more
information regarding these Acts see https://www.fws.gov/birds/policies-and-regulations.php.
The MBTA has no provision for allowing take of migratory birds that may be unintentionally
killed or injured by otherwise lawful activities. It is the responsibility of the project proponent to
comply with these Acts by identifying potential impacts to migratory birds and eagles within
applicable NEPA documents (when there is a federal nexus) or a Bird/Eagle Conservation Plan
(when there is no federal nexus). Proponents should implement conservation measures to avoid
or minimize the production of project-related stressors or minimize the exposure of birds and
their resources to the project-related stressors. For more information on avian stressors and
recommended conservation measures see https://www.fws.gov/birds/bird-enthusiasts/threats-to-
birds. php.
In addition to MBTA and BG EPA, Executive Order 13186: Responsibilities of Federal Agencies
to Protect Migratory Birds, obligates all Federal agencies that engage in or authorize activities
that might affect migratory birds, to minimize those effects and encourage conservation measures
that will improve bird populations. Executive Order 13186 provides for the protection of both
migratory birds and migratory bird habitat. For information regarding the implementation of
Executive Order 13186, please visit https://www.fws.gov/birds/policies-and-regulations/
executive-orders/e0-13186.php.
We appreciate your concern for threatened and endangered species. The Service encourages
Federal agencies to include conservation of threatened and endangered species into their project
planning to further the purposes of the Act. Please include the Consultation Code in the header of
this letter with any request for consultation or correspondence about your project that you submit
to our office.
06/02/2022
Official Species List
This list is provided pursuant to Section 7 of the Endangered Species Act, and fulfills the
requirement for Federal agencies to "request of the Secretary of the Interior information whether
any species which is listed or proposed to be listed may be present in the area of a proposed
action".
This species list is provided by:
Washington Fish And Wildlife Office
510 Desmond Drive Se, Suite 102
Lacey, WA 98503-1263
(360) 753-9440
1
06/02/2022
Project Summary
Project Code: 2022-0049726
Event Code: None
Project Name: Painted Hills PRD
Project Type: New Constr -Above Ground
Project Description: The property owner proposes filling the site with residential homes
Project Location:
Approximate location of the project can be viewed in Google Maps: https://
www.google.com/maps/@4 7 .61142875,-117.27805495,14z
Counties: Spokane County, Washington
2
06/02/2022 3
Endangered Species Act Species
There is a total of 4 threatened, endangered, or candidate species on this species list.
Species on this list should be considered in an effects analysis for your project and could include
species that exist in another geographic area. For example, certain fish may appear on the species
list because a project could affect downstream species.
IPaC does not display listed species or critical habitats under the sole jurisdiction of NOAA
Fisheries1, as USFWS does not have the authority to speak on behalf of NOAA and the
Department of Commerce.
See the "Critical habitats" section below for those critical habitats that lie wholly or partially
within your project area under this office's jurisdiction. Please contact the designated FWS office
if you have questions.
1. NOAA Fisheries, also known as the National Marine Fisheries Service (NMFS), is an
office of the National Oceanic and Atmospheric Administration within the Department of
Commerce.
Birds
NAME STATUS
Yellow-billed Cuckoo Coccyzus americanus Threatened
Population: Western U.S. DPS
There is final critical habitat for this species. The location of the critical habitat is not available.
Species profile: https://ecos.fws.gov/ecp/species/3911
Fishes
NAME
Bull Trout Salvelinus confluentus
Population: U.S.A., conterminous, lower 48 states
There is final critical habitat for this species. The location of the critical habitat is not available.
Species profile: https://ecos.fws.gov/ecp/species/8212
Insects
NAME
Monarch Butterfly Danaus plexippus
No critical habitat has been designated for this species.
Species profile: https://ecos.fws.gov/ecp/species/9743
STATUS
Threatened
STATUS
Candidate
06/02/2022
Flowering Plants
NAME
Spalding's Catchfly Silene spaldingii
There is proposed critical habitat for this species. The location of the critical habitat is not
available.
Species profile: https://ecos.fws.gov/ecp/species/3681
Critical habitats
STATUS
Threatened
THERE ARE NO CRITICAL HABITATS WITHIN YOUR PROJECT AREA UNDER THIS OFFICE'S
JURISDICTION.
4
06/02/2022
IPaC User Contact Information
Agency: Biology Soil & Water, Inc.
Name: Larry Dawes
Address: 3102 N. Girard Road
City:
State:
Zip:
Email
Phone:
Spokane Valley
WA
99212
bswinc@icehouse.net
5093272684
5
Appendix 2
WDF & W Priority Habitats and Species
23
6/29/22, 1 :26 PM PHS Report
ll~ ~fi:,• Priority Habitats and Species on the Web WILD/JFE
Report Date: 06/29/2022, Parcel ID: 44052.9011
PHS Species/Habitats Overview:
Occurence Name Federal Status State Status Sensitive Location
Northwest white-tailed deer N/A N/A No
Rocky Mountain elk N/A N/A No
Shrubsteppe N/A N/A No
Gray wolf Endangered Endangered Yes
114
6129122, 1 :26 PM PHS Report
PHS Species/Habitats Details:
Northwest white-tailed deer
Scientific Name Odocoileus virginianus ochrourus
Priority Area Regular Concentration
Site Name TOWER MOUNTAIN
Notes WHITE-TAILED DEER WINTER RANGE MEDIUM DENSITY USE
AREA
Source Record 900216
Source Dataset PHSREGION
Source Name ANDREWS, JOHN
Source Entity WA Dept. of Fish and Wildlife
Federal Status NIA
State Status NIA
PHS Listing Status PHS LISTED OCCURRENCE
Sensitive N
SGCN N
Display Resolution AS MAPPED
ManagementRecommendations httR:llwdfw. wa .gov/f.1ublications/f.1ub.R!.1R?id=00612
Geometry Type Polygons
Rocky Mountain elk
..
Scientific Name Cervus e/aphus nelsoni
Priority Area Regular Concentration
Site Name TOWER MOUNTAIN/MICA PEAK/TURNBULL
Notes ROCKY MOUNTAIN ELK YEAR ROUND USE AREA. HANGMAN
ELK HERD.
Source Record 918601
Source Dataset PHSREGION
Source Name HICKMAN, JERRY WDFW
Source Entity WA Dept. of Fish and Wildlife
Federal Status N/A
State Status N/A
PHS Listing Status PHS LISTED OCCURRENCE
Sensitive N
SGCN N
Display Resolution AS MAPPED
ManagementRecommendations htti:r//wdfw.wa.gov/12ublications/Qub.rum?id=00614
Geometry Type Polygons
214
6129122, 1 :26 PM PHS Report
Shrubsteppe
Priority Area Habitat Feature
Site Name Spokane County Presumptive Shrubsteppe
Accuracy NA
General location of Shrubsteppe. Confirm or refute with site-scale
Notes info. WDFW recommends using site-scale info to inform site-scale
land use decisions. Expect that on-the-ground conditions (e.g.,
boundaries) will vary from the map.
Source Record 920846
Source Name Keith Folkerts, WDFW
Source Entity WA Dept. of Fish and Wildlife
Federal Status N/A
State Status N/A
PHS Listing Status PHS LISTED OCCURRENCE
Sensitive N
SGCN N
Display Resolution AS MAPPED
Geometry Type Polygons
Gray wolf
Scientific Name Canis lupus
This polygon mask represents one or more records of the above
Notes species or habitat occurrence. Contact PHS Data Release (360-902-
2543) for obtaining information about masked sensitive species and
habitats.
Federal Status Endangered
State Status Endangered
PHS Listing Status PHS Listed Occurrence
Sensitive y
SGCN y
Display Resolution TOWNSHIP
DISCLAIMER. This report includes information that the Washington Department of Fish and Wildlife (WDFW) maintains in a central computer database. It is not an attempt to provide you
with an official agency response as to the impacts of your project on fish and wildlife. This information only documents the location of fish and wildlife resources to the best of our knowledge.
It is not a complete inventory and it is important to note that fish and wildlife resources may occur in areas not currently known to WDFW biologists, or in areas for which comprehensive
surveys have not been conducted. Site specific surveys are frequently necesssary to rule out the presence of priority resources. Locations of fish and wildlife resources are subject to
variation caused by disturbance, changes in season and weather, and other factors. WDFW does not recommend using reports more than six months old.
4/4
Appendix 3
Web Soil Survey
24
47° 36' 59" N
47° 36'21"N
Soil Map-Spokane County, Washington
47800) 4789'.XJ 479'.XXJ 479100 479200 4793Xl
Map Scale: 1:5,790 if printed on A portrait (8.5" x 11") sheet
-----======-----------=========~Meters 0 60 100
-------=======-------------===========~Feet 0 250 [ID 1<XXJ 1!ID
Map projection: Web Mercator Comer mordinates: WGS84 Edge tics: VTM Zone llN WGS84
USDA Natural Resources ~ Conservation Service
Web Soil Survey
National Cooperative Soil Survey
479400 479500
61212022
Page 1of3
47" 36'21" N
Soil Map-Spokane County, Washington
MAP LEGEND
Area of Interest (AOI)
D Area of Interest (AOI)
Soils
D Soil Map Unit Polygons
Soil Map Unit Lines
[J Soil Map Unit Points
Special Point Features
~ Blowout
181 Borrow Pit
lllit Clay Spot
0 Closed Depression
x Gravel Pit . Gravelly Spot ..
0 Landfill
A Lava Flow
.$ Marsh or swamp
~ Mine or Quarry
0 Miscellaneous Water
a Perennial Water
"""
Rock Outcrop
+ Saline Spot .. Sandy Spot . ..
@ Severely Eroded Spot
«> Sinkhole
lJ Slide or Slip
ff) Sodic Spot
USDA Natural Resources ~1Fi Conservation Service
§ Spoil Area
t) Stony Spot
t:G Very Stony Spot
~ Wet Spot
/::. Other
,.. Special Line Features
Water Features
' "" Streams and Canals
Transportation
H-t Rails
~ Interstate Highways
""""' US Routes -Major Roads
Local Roads
Background • Aerial Photography
Web Soil Survey
National Cooperative Soil Survey
MAP !~FORMATION
The soil surveys that comprise your AOI were mapped at
1:24,000.
Warning: Soil Map may not be valid at this scale.
Enlargement of maps beymd the scale of mapping can cause
misunderstanding of the detail of mapping and accuracy of soil
line placement. The maps do not show the small areas of
contrasting soils that could have been shown at a more detailed
scale.
Please rely on the bar scale on each map sheet for map
measurements.
Source of Map: Natural Resources Conservation Service
Web Soil Survey URL:
Coordinate System: Web Mercator (EPSG:3857)
Maps from the Web Soil Survey are based on the Web Mercator
projection, which preserves direction and shape but distorts
distance and area. A projection that preserves area, such as the
Albers equal-area conic projection, should be used if more
accurate calculations of distance or area are required.
This product is generated from the USDA-NRCS certified data as
of the version date(s) listed below.
Soil Survey Area: Spokane County, Washington
Survey Area Data: Versim 13, Aug 23, 2021
Soil map units are labeled (as space allows) for map scales
1 :50,000 or larger.
Date(s) aerial images were photographed: Jul 12, 2020-Aug
14,2020
The orthophoto or other base map on which the soil lines were
compiled and digitized probably differs from the background
imagery displayed on these maps. As a result, some minor
shifting of map unit boundaries may be evident.
6/2/2022
Page 2 of 3
Soil Map-Spokane County, Washington
Map Unit Legend
Map Unit Symbol
.~ s'1 2j ... , -
5027
5067
5211
5212
5313
5413
~
" I~
7122
7181
Totals for Area of Interest
USDA Natural Resources
""SF Conservation Service
Map Unit Name Acres in AOI
Marble loamy sand, 8 to 15
percent slopes
Micapeak-Spokane complex,
30 to 55 percent slopes
Quinnamose-Micapeak
complex, 15 to 30 percent
slopes
Kruse ashy silt loam, 8 to 15
percent slopes
Kruse ashy silt loam, 15 to 30
percent slopes
Kramerhill-Spokane complex,
8 to 25 percent slopes
Keeler-Kruse complex, 15 to
30 percent slopes
Urban land-Marble, disturbed
complex, 3 to 8 percent
slopes
Urban land-Marble, disturbed
complex, 8 to 15 percent
slopes
Urban land-Phoebe, disturbed
complex, 3 to 8 percent
slopes
Web Soil Survey
National Cooperative Soil Survey
Percent of AOI
54.2
1.1
2.1
22.5
6.5
3.0
6.2
30.0
17.3
0.1
143.0
37.9%
0.8%
1.4%
15.8%
4.5%
2.1%
4.3%
20.9%
12.1%
0.1%
100.0%
6/2/2022
Page 3 of 3
Map Unit Description: Marble loamy sand, 8 to 15 percent slopes--Spokane County,
Washington
Spokane County, Washington
3121-Marble loamy sand, 8 to 15 percent slopes
USDA Natural Resources = Conservation Service
Map Unit Setting
National map unit symbol: 2wdk
Elevation: 1,560 to 2,500 feet
Mean annual precipitation: 15 to 22 inches
Mean annual air temperature: 45 to 50 degrees F
Frost-free period: 100 to 140 days
Farmland classification: Prime farmland if irrigated
Map Unit Composition
Marble and similar soils: 75 percent
Minor components: 25 percent
Estimates are based on observations, descriptions, and transects of
the mapunit.
Description of Marble
Setting
Landform: Outwash plains
Landform position (three-dimensional): Tread
Down-slope shape: Linear
Across-slope shape: Linear
Parent material: Sandy glaciofluvial deposits
Typical profile
Oi -0 to 1 inches: slightly decomposed plant material
A -1 to 4 inches: loamy sand
E -4 to 8 inches: loamy sand
E and Bt1 -8 to 27 inches: sand
E and Bt2 -27 to 53 inches: sand
C -53 to 60 inches: sand
Properties and qualities
Slope: 8 to 15 percent
Depth to restrictive feature: More than 80 inches
Drainage class: Well drained
Capacity of the most limiting layer to transmit water (Ksat): High to
very high (5.95 to 19.98 in/hr)
Depth to water table: More than 80 inches
Frequency of flooding: None
Frequency of ponding: None
Available water supply, 0 to 60 inches: Low (about 3.1 inches)
Interpretive groups
Land capability classification (irrigated): None specified
Land capability classification (nonirrigated): 4s
Hydrologic Soil Group: A
Ecological site: F043AY509WA-Warm, Xeric, Sandy, Outwash
Terraces and Plains (Ponderosa Pine/Dry Grass) Pinus
Web Soil Survey
National Cooperative Soil Survey
61212022
Page 1of2
Map Unit Description: Marble loamy sand, 8 to 15 percent slopes--Spokane County,
Washington
ponderosa I Pseudoroegneria spicata , Pinus ponderosa I
Festuca idahoensis
Other vegetative classification: ponderosa pine/Idaho fescue
(CN140)
Hydric soil rating: No
Minor Components
Marblespring
Percent of map unit: 10 percent
Landform: Outwash terraces
Landform position (three-dimensional): Tread
Down-slope shape: Linear
Across-slope shape: Linear
Other vegetative classification: ponderosa pine/bluebunch
wheatgrass (CN130)
Hydric soil rating: No
Hardesty
Percent of map unit: 5 percent
Landform: Depressions, drainageways
Landform position (three-dimensional): Tread
Down-slope shape: Concave, linear
Across-slope shape: Concave, linear
Other vegetative classification: ponderosa pine/ninebark (CN 190)
Hydric soil rating: No
Hagen
Percent of map unit: 5 percent
Landform: Outwash terraces
Landform position (three-dimensional): Riser
Down-slope shape: Linear
Across-slope shape: Convex
Other vegetative classification: ponderosa pine/common snowberry
(CN170)
Hydric soil rating: No
Bong
Percent of map unit: 5 percent
Landform: Outwash plains
Landform position (three-dimensional): Tread
Down-slope shape: Linear
Across-slope shape: Linear
Other vegetative classification: ponderosa pine/bluebunch
wheatgrass (CN 130)
Hydric soil rating: No
Data Source Information
Soil Survey Area: Spokane County, Washington
Survey Area Data: Version 13, Aug 23, 2021
USDA Natural Resources = Conservation Service
Web Soil Survey
National Cooperative Soil Survey
61212022
Page 2 of 2
Map Unit Description: Urban land-Marble, disturbed complex, 3 to 8 percent slopes-Spokane
County, Washington
Spokane County, Washington
USDA Natural Resources
7121-Urban land-Marble, disturbed complex, 3 to 8 percent
slopes
Map Unit Setting
National map unit symbol: 2mdn1
Elevation: 1,750 to 2,360 feet
Mean annual precipitation: 18 to 20 inches
Mean annual air temperature: 45 to 50 degrees F
Frost-free period: 100 to 130 days
Farmland classification: Not prime farmland
Map Unit Composition
Urban land: 60 percent
Marble, disturbed, and similar soils: 35 percent
Minor components: 5 percent
Estimates are based on observations, descriptions, and transects of
the mapunit.
Description of Urban Land
Interpretive groups
Land capability classification (irrigated): None specified
Land capability classification (nonirrigated): 8
Hydric soil rating: No
Description of Marble, Disturbed
Setting
Landform: Outwash plains
Landform position (three-dimensional): Tread
Down-slope shape: Linear
Across-slope shape: Linear
Parent material: Sandy glaciofluvial deposits
Typical profile
A -0 to 4 inches: loamy sand
E -4 to 8 inches: loamy sand
E and Bt1 -8 to 27 inches: sand
E and Bt2 -27 to 53 inches: sand
C -53 to 60 inches: sand
Properties and qualities
Slope: 3 to 8 percent
Depth to restrictive feature: More than 80 inches
Drainage class: Well drained
Capacity of the most limiting layer to transmit water
(Ksat): Moderately high to high (0.57 to 1.98 in/hr)
Depth to water table: More than 80 inches
Frequency of flooding: None
Frequency of ponding: None
"1iiiii Conservation Service
Web Soil Survey
National Cooperative Soil Survey
7/11/2022
Page 1 of 3
Map Unit Description: Urban land-Marble, disturbed complex, 3 to 8 percent slopes-Spokane
County, Washington
USDA Natural Resources
""'ffl Conservation Service
Available water supply, 0 to 60 inches: Very low (about 3.0 inches)
Interpretive groups
Land capability classification (irrigated): None specified
Land capability classification (nonirrigated): 4s
Hydrologic Soil Group: B
Ecological site: F043AY509WA-Warm, Xeric, Sandy, Outwash
Terraces and Plains (Ponderosa Pine/Dry Grass) Pinus
ponderosa I Pseudoroegneria spicata , Pinus ponderosa I
Festuca idahoensis
Other vegetative classification: ponderosa pine/Idaho fescue
(CN140)
Hydric soil rating: No
Minor Components
Hardesty, disturbed
Percent of map unit: 2 percent
Landform: Depressions, drainageways
Landform position (three-dimensional): Tread
Down-slope shape: Concave, linear
Across-slope shape: Concave, linear
Other vegetative classification: ponderosa pine/ninebark (CN 190)
Hydric soil rating: No
Phoebe, disturbed
Percent of map unit: 1 percent
Landform: Outwash plains
Landform position (three-dimensional): Tread
Down-slope shape: Linear
Across-slope shape: Linear
Other vegetative classification: ponderosa pine/common snowberry
(CN170)
Hydric soil rating: No
Marblespring, disturbed
Percent of map unit: 1 percent
Landform: Outwash terraces
Landform position (three-dimensional): Tread
Down-slope shape: Linear
Across-slope shape: Linear
Other vegetative classification: ponderosa pine/bluebunch
wheatgrass (CN130)
Hydric soil rating: No
Hagen, disturbed
Percent of map unit: 1 percent
Landform: Outwash terraces
Landform position (three-dimensional): Tread
Down-slope shape: Linear
Across-slope shape: Convex
Other vegetative classification: ponderosa pine/common snowberry
(CN170)
Web Soil Survey
National Cooperative Soil Survey
7/11/2022
Page 2 of 3
Appendix 4
Additional Critical Areas Maps
25
7/12/22, 1:37 PM City of Spokane Valley Geohazards
City of Spokane Valley Geohazards
Geohazards
+
Legend
GeoHazards
Mur :c:pc.I Bou1daries
D Spokane Valley
Steep Slope 30% or Greater
Geohazards •
,... E 44 h v _,
C'2 E
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Layer List
Layers
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National Flood Hazard Layer FIRMette FEMA
.. .:::=: .. m::=::1111 .......... c::=::=::=::=::=::::1111 ........... Feet
0 250 500 1,000 1,500 2,000
R!lcom.::an· I IC::::t:!C:::: N.::iitinn:::JJ M.::iin· flrthnim!ideir11• n.::iif-::a roirot::horl flrfnhar ?(')?11
Legend
SEE FIS REPORT FOR OETAILED LEGEND AND INDEX MAP FOR FIRM PANEL LAYOUT
SPECIAL FLOOD
HAZARD AREAS
OlHER AREAS OF
FLOOD HAZARD
OTHER AREAS
Without Base Flood Elevation (BFE)
Zone A. V. A9·9
With BFE or Depth zone AE. AO, AH, VE. AR
Regulatory Floodway
0.2% Annual Chance Flood Hazard, Areas
of 1% annual chance flood with average
depth less than one foot or with drainage
areas of less than one square mile zone x
Future Conditions 1% Annual
Chance Flood Hazard Zone x
Area with Reduced Flood Risk due to
Levee. See Notes. zone x
Area with Flood Risk due to Levee zone o
NO SCREEN Area of Minimal Flood Hazard zone x
1._ __ _.! Effective LOMRs
Area of Undetermined Flood Hazard Zone 1
GENERAL Channel, Culvert, or Storm Sewer
STRUCTURES I I I I I I I Levee, Dike, or Floodwall
OTHER
FEATURES
MAP PANELS
Cross Sections with 1 % Annual Chance
_.-1Li Water Surface Elevation
a ---Coastal Transect
~ 513~ Base Flood Elevation line (BFE) = Limit of Study
----Jurisdiction Boundary
0
D
~
Coastal Transect Baseline
Profile Baseline
Hydrographic Feature
Digital Data Available
No Digital Data Available
Unmapped
N
L v
The pin displayed on the map is an approximate
point selected by the user and does not represen
an authoritative property location.
This map complies with FEMA's standards for the use of
digital flood maps if it is not void as described below.
The basemap shown complies with FEMA's basemap
accuracy standards
The flood hazard information is derived direclly from the
authoritative NFHL web services provided by FEMA. This map
was exported on 6/2/2022 at 11:46 AM and does not
reflect changes or amendments subsequent to this date and
time. The NFHL and effective information may change or
become superseded by new data over time.
This map image is void if the one or more of the following map
elements do not appear: base map imagery, flood zone labels,
legend, scale bar, map creation date, community identifiers,
FIRM panel number, and FIRM effective date. Map images for
unmapped and unmodernized areas cannot be used for
regulatory purposes.
612122, 11:28 AM
+
NOlfff;lWEST
\lli'.17JllE-T . .!UC:fD
DEER
City of Spokane Valley
Pnority Habitats and Species
rJR.~NAHJRAL
OP.EN SP.~CE
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MOUNT~ft
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~'V'BITE~TAWED
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URBAN NAJtlRAL
OPEN\SPAGE
City of Spokane Valley
E "' m mar(! n 0 1
https://spoka neval ley. maps.arcgis.com/apps/webappviewer/index.html?id=61 d5fd81c2cc4a7 cbbd9b5f6d4512807
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1/1
70
U.S. DEPARTMENT OF THE INTERIOR
U.S. GEOLOGICAL SURVEY
SCALE 1 :24 000
UllITTlUR!l<l!RYll..lOfl:U HO!lltl.<,ll(RIO.HVOJ"-Y.D.>.TUl>\(lf19QI
Tlil$""pw11~lotoof0<mwll.h~ ~==~r:r:h'!.!=:~.~.~~'.!: ..
SPOKANE SE QUADRANGLE
WASHINGTON -SPOKANE COUNTY
7.5-MINUTESER!ES
I I } i
I I ! I ./ ) 66 . I ! I ,'28 i...,
"'_.., __
62
-.. •· .. -·-· o~-·· o~··-·
SPOKANE SE, WA
2010
Biology, Soil Larry Dawes, 3102 N. Girard Road, Spokane Valley, WA 99212 (509) 327-2684
& Water, Inc.
Biology Soil & Water (BSW) is an association of academic, former government,
and private sector scientists with diverse training and experience in the field of
environmental consulting. From our offices in Spokane, BSW provides consulting
services for large and small, federal, state, municipal, industrial, commercial and private
projects throughout the Northwest. BSW is committed to a long-term relationship with
the Northwest, innovative approaches, and continuous education to cope with changing
environmental regulations, conservation objectives, permitting requirements, and
ecosystem management strategies.
Wetland Delineation, Rating and Report
Routine and Comprehensive Delineation, Rating, and Wetland Reports
Wetland and Buffer Mitigation, Design, Construction and Monitoring
Jurisdiction Approved Wetland Designs and Mitigation Plans,
Wetland Construction, Planting, and Monitoring,
Consultation on Conservancy and Protection Options
Critical Areas Ordinance Compliance
Biological Assessments and Ecological Assessments, Priority Habitat & Species Analysis
(required for Federally funded projects)
Threatened, Endangered, Sensitive, and Candidate Species Analysis
Water Typing, Riparian Area, and Shoreline Determinations, Mitigation Plans
Ecological Investigations, Transect and Habitat Studies
Plant and Animal Identification, Population Sampling
Soil Investigations
Hydric Soils, Agricultural and Urban Soils Investigations and Interpretations
Development Suitability Analy:si:s
Shoreline, Wetland, and Riparian Setbacks
Critical Areas Ordinance Interpretation/Compliance
Remote Sensing and Airphoto Interpretations
Wetlands Analysis, Historical and Current Land Use Signatures
LARRY DA WES, Biologist, Hydrologist
SUMMARY: Mr. Dawes is well versed in federal, state, and local environmental
regulations and consults primarily in the field of site assessment. He evaluates project
development plans with respect to Shoreline, Wetland, and Critical Areas Ordinance
issues and works with the jurisdictions regulating land uses and activities on a daily basis.
Mr. Dawes delineates and rates wetlands to establish buffer widths and designs and
implements wetland mitigation plans to meet jurisdiction performance standards. These
plans include wetland design, engineering, construction, revegetation, and monitoring.
He interprets regulations, completes Ecological and Biological Assessments for
development sites, and prepares Management Plans when development encroaches on
critical habitats or species. Mr. Dawes conducts upland, wetland, and aquatic plant
surveys and has also been associated with many water quality assessment and restoration
projects.
EDUCATION:
Master of Science, Biology, Eastern Washington University
Concentration: Site Assessment (Wetland, Water Quality and Habitat
Restoration; Hydrogeology; Botany)
Bachelor of Science, Biology, Eastern Washington University
Concentration: Site Assessment (Zoology, Botany, Water Quality)
Minor, Urban and Regional Planning, EWU
Concentration: Environmental Planning, Law, and Legislation
EXPERIENCE:
1997-present: Biology Soil & Water, Inc Owner/Principal Biologist.
Performs wetland delineation and rating, hydrologic analysis, plant and animal surveys,
and Biological Assessments. Designs wetlands, prepares and implements wetland
mitigation and revegetation plans. Conducts Ecological and Biological Assessments,
prepares/initiates habitat management and mitigation plans for Critical Areas Ordinance
and Endangered Species Act compliance.
1996-1997 Northwest Biological Consulting, Inc. Owner/Operator.
Performed site hydrologic analysis, plant surveys; identified, rated, and delineated
wetlands; prepared habitat management plans, prepared mining reclamation and
revegetation plans.
1994-1996: Eastern Washington University Dept. of Biology Limnology/Water Quality
Researcher. Conducted plant surveys and research. Co-investigator of water quality
assessment and restoration projects. Co-author of water quality publications.
1992-1996: Independent Consultant. Performed wetland identification, rating, and
delineation projects in the Northwest.