HomeMy WebLinkAboutLANDMARK APARTMENTS EXPANSION - FDP190002 - SUBMITTAL DOCUMENTS - ROUND 3 - WETLANDS DOCUMENTSApril 6, 2019
Ms. Kim Berry
Senior Project Manager
Red Tail Acquisitions, LLC-TK Consulting, Inc.
2082 Michelson Drive, 3rd Floor
Irvine, CA 92612
Re: Waters of the U. S. Delineation for the Landmark Apartments Project (Corps File No. NWO-2012-
2597-DEN
Ms. Berry:
I completed a wetland and other Waters of the U. S. delineation for the Landmark Apartments Project
located in Fort Collins, Larimer County, Colorado. The project area is situated in the northwest 1/4 of
Section 23, Township 7 North, Range 69 West (N 40.56572, W 105.09322, NAD 83) (see attached Figure
1). A previous wetland delineation for the project area was submitted to the Corps on October 30, 2012
(see Corps File No. NWQ-2012-2597).
The objective of this project is to construct and rent market-rate apartments, including parking areas and
a recreational trail connection. Current development plans indicate the only construction near the
property drainage and associated wetlands would be a pedestrian footbridge crossing of the drainage. All
other developments would be setback 50 feet from edge of wetlands as per on City of Fort Collins buffer
requirements for wetlands.
The objective of the delineation work is to fulfill the requirements of Section 404 of the Clean Water Act
regarding the delineation of wetlands and other Waters of the U. S. prior to potential development
activities.
The site can be reached by traveling north from Denver on I-25 and exiting west on the Prospect Street
exit. Continue west past South College Avenue, turn south on Shields Street, and then east on Hobbit
Street to its current dead end at the southwest corner of the project site.
Field Delineation Methodology
Wetland delineation and sampling work for the wetlands and open water features within the project area
were completed on April 5, 2019 using the methods and techniques specified for "routine on-site
delineations" in the publication Corps of Engineers Wetlands Delineation Manual (Department of the
Army 1987), supplemented by the document Regional Supplement to the Corps of Engineers Wetland
Delineation Manual: Great Plains Region (Version 2.0). The project area was evaluated and potential
wetland, transition zone, and upland vegetation communities were identified. Using the three-parameter
approach via test hole characteristics, the wetland/upland boundaries were flagged. Formal sample point
locations were then identified. Sample point locations were selected to represent typical wetland, upland,
and upland transition zone conditions on site.
At each sample point, percent total cover of dominant plant species was estimated. Species were then
classed as OBL (obligate wetland species), FACW (facultative wetland species), FAC (facultative
species), FACU (facultative upland species) or UPL (upland species). Soil and hydrologic data were also
collected to determine the presence or absence of wetlands at each sample point. Wetland soil indicators
potentially included the presence of a histic epipedon, thick dark surface, redox features, gleying,
depleted profile conditions, an aquic soil moisture regime, and high organic matter content and/or a
stripped matrix in sandy soils. Potential wetland hydrology indicators included geomorphic position,
Landmark Apartments Wetland Report
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presence of standing water and/or saturated soil profile conditions, drainage patterns, watermarks,
sediment deposits, and oxidized root channels in the upper 12 inches of the soil profile. Sample holes
were dug to a depth of from 12 to 14 inches. Formal field data sheets were completed for each sample
point evaluated (L-1 through L-3). Wetland / upland boundaries and sample points were flagged with pink
fluorescent tape and numbered orange pin flags tied with pink fluorescent tape, respectively, for
subsequent surveying work. The open water features were flagged with blue tape.
Adjunct test holes were also dug, where appropriate, to gain additional vegetation, soil, and hydrologic
information used to aid in the characterization of wetlands, uplands, and transition zones. Data sheets
were not completed for test holes.
The results of the field delineation are summarized in the following paragraphs. Table 1 is provided to
summarize the data sheets and support the text. A vicinity map is attached (see Figure 1) as well as
photos and copies of the data sheets completed during the survey. A wetland delineation map (prepared
by Northern Engineering is also attached.
Results – Uplands
Uplands occupy the vast majority of the project area. These uplands are comprised of gently sloping to
nearly level non-native grasslands north and south of the wetland drainage. Sample points L-1 and L-2
(see Table 1) were selected to represent the upland grasslands as well as the narrow upland transition
zone adjacent to the edge of the delineated wetland area, respectively. The dominant plant species is
smooth brome (Bromopsis inermis - UPL) at both sample sites, although lesser amounts of common
cattail (Typha latifolia - OBL) and reed canarygrass (Phalaris arundinacea - FACW) are present at sample
point L-2 in the upland transition zone. There were hydrology wetland indicators observed at L-1, and no
soil sample was taken since the site is dominated solely by upland plants. The upland transition zone
located along the lower terrace adjacent to the wetlands is dominated by smooth brome but reed
canarygrass is also present as a lesser dominant species. Although evidence of wetland hydrology is
present at L-2, neither hydric soils nor dominance by wetland vegetation was present at this sample site.
Photo 1 provides of view of sample points L-1 and L-2. A summary of the characteristics of these two
sample points is provided in Table 1.
Results - Vegetated Wetlands and Other Waters of the US
The wetlands located along project site drainage consist of a central cattail (Typha latifolia) community
established under flooded conditions (no sample point) bordered immediately upslope by saturated soils
supporting a vegetation community (sample point L-3) dominated by common cattail (Typha latifolia -
OBL) and reed canarygrass (Phalaroides arundinacea). Soils at this sample point had matrix colors of
10YR 3/1 and 4/1 with 2.5YR 4/8 mottles beginning at 5 inches. The soils were saturated at 8 inches,
and standing water was present at 12 inches. Photo 1 provides of view of sample point L-3. A summary
of the characteristics of this sample point is provided in Table 1.
Three open water channel features within the cattail-dominated drainage were delineated. Flowing,
open-water channels, with minimal cattail establishment, characterize these elements.
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TABLE 1: SUMMARY OF SAMPLE POINT CHARACTERISTICS
Sample Dominant Hydric Primary & Secondary Wetland COE
Point # Species Soil Indicator(s) Hydrology Indicator(s) Wetland
L-1 Bromus inermis -UPL None None No
L-2 Bromus inermis -UPL
Phalaris arundinacea -FACW None B3, B10 No
L-3 Typha latifolia - OBL
Phalaris arundinacea -FACW F3 A2, A3, B2 PEM1
Jurisdictional Considerations
The unnamed drainage in the project flows southeast into Spring Creek to the south, which in turn, flows
into the Cache la Poudre River.
Wetland Impacts
Based on current project development plans, the proposed pedestrian bridge will span the entire drainage
and abutments constructed for the bridge will be well outside of the delineated wetland and open water
boundaries. Therefore, there will be not fill impacts to possible jurisdictional wetlands and Other Waters
of the U.S. The U. S. Army Corp of Engineers will not review or comment on projects that would have no
impacts wetlands and Other Waters of the U.S and would not require a request for a Section 404 Permit.
As a result there is no need to file this report to the U. S. Army Corp of Engineers or request a Secion 404
Permit.
Sincerely,
CEDAR CREEK ASSOCIATES, INC.
Michael Phelan
Wetlands and Wildlife Consultant
pc: K. Turner, The Birdsall Group
D. Weber, Northern Engineering, Inc.