HomeMy WebLinkAboutH-25 MULTI-FAMILY - FDP210008 - SUBMITTAL DOCUMENTS - ROUND 1 - EROSION CONTROL LETTER/REPORT
Erosion Control Report
Harmony 25 Multi-Family Development
Parcel No. 8603000028
Fort Collins, Colorado
Date Submitted: April 6, 2021
Owner:
Post Modern Development, LLC
144 Mason North Mason Street, Ste 4
Fort Collins, Colorado 80524
JD Padilla
jd@postmoderndevelopment.com
Developer:
Harmony 25, LLC
144 Mason North Mason Street, Ste 4
Fort Collins, Colorado 80524
Jeff Jensen
(970) 227-0622
jeff@jensenlaplante.com
Contractor:
TBD
Design Engineer:
Sanderson Stewart
425 West Mulberry, Suite 201
Fort Collins, CO 80526
Charles Sonnier
(970) 488-0169
csonnier@sandersonstewart.com
Erosion Control Administrator:
TBD
2
CERTIFICATION STATEMENT:
I hereby certify that this Erosion Control Report for the removal of existing fill within the
floodway within Parcel No. 8603000028 was prepared by me (or under my direct supervision) in
accordance with the provisions of the City of Fort Collins Stormwater Criteria for the owners
thereof.
_______________________________________________
Charles Joseph Sonnier, Registered Professional Engineer
State of Colorado Registration No. 48403
4/7/21
3
Table of Contents
I. Project Description and Nature of Construction
II. Potential Pollutant Sources
III. Control Measures
IV. Installation and Removal Sequence of Control Measures
V. Maintenance and Inspection of Requirements
VI. Final Vegetation and Stability
Sanderson Stewart April 2021
Harmony 25 Parcel No. 8603000028 pg. 1
Project No. 19059.02
I. Project Description and Nature of Construction
Existing Site Location and Conditions:
The subject property (Parcel No. 8603000028, approximately 38 acres) is located in the
southeast corner of Harmony Road and Strauss Cabin Road in the west half of Section 3,
Township 6 North, Range 68 West, latitude 40.5228, longitude 104.9983. The site is
generally bounded by Strauss Cabin Road on the west, Harmony Road on the north,
Harmony Gardens landscape nursery on the east and Weitzel Pond on the south.
Surrounding properties include: the Arapaho Bend Natural Area and the Harmony Road
Transportation Transfer Center on the north side of Harmony Road, Island Lake Marina
and the Eagle View Natural Area on the south side of Kechter Road, the Chandler
property (now under Nine Bridges, LLC ownership) west of Strauss Cabin Road, the
Mountain Life Church and the Budurus properties located along Strauss Cabin Road
further to the south. East of the property is the I-25 interstate and the Town of Timnath.
The Fossil Creek Reservoir Inlet Ditch (FCRID) and the Boxelder Ditch are located along
the western side of the overall site with the FCRID being further to the west. The Boxelder
Ditch crosses Strauss Cabin Road and enters the site approximately 1700’ south of
Harmony Road.
This property is located within the Cache la Poudre watershed and City of Fort Collins
Poudre River drainage basin. This project site sits within the FEMA regulated floodway
and floodplain, per FEMA FIRM Maps 08069C0994F & 08069C1013F, dated December
19, 2006.
The site is mostly flat to minimally sloped. Generally, runoff from the site sheet flows to the
east and south to the existing floodway channel and travels south through a series of
existing large inactive gravel pits that have essentially become retention ponds for
stormwater. This drainage way outlets into two culverts under Kechter Road,
approximately a mile south from the project site and is assumed to be the historic
stormwater release location for this area. Flow then conveys south of Kechter Road and
into Island Lake then flows due east under I-25 and then south east approximately a half
mile to Fossil Creek Reservoir Outlet and then another half mile onto the Cache La
Poudre River.
According to the NRCS website, the site consists mainly of Caruso clay loam, 0 to 1
percent slope with a classification of Type C soils. Refer Appendix for soil property
information. This soil type has an erodibility factor of 0.32 which suggests a moderate
susceptibility to sheet and rill erosion by runoff.
Currently, the Site consists of mostly vegetative ground cover with mostly shrubbery and a
few trees , consisting of approximately 70% vegetative density. No impervious areas exist
within the project area and there are no structures. Groundwater depth is approximately
fifteen (15) feet below existing ground and no known ground contamination is present.
Also, no known riparian or sensitive areas are proximate to the project site.
Sanderson Stewart April 2021
Harmony 25 Parcel No. 8603000028 pg. 2
Project No. 19059.02
Proposed Construction Activities:
The proposed project will consist of 12 new multi-family buildings with 290 total units.
Proposed utility improvements will consist of storm sewer, sanitary sewer and waterline
improvements. Surface improvements will include driveway, parking lot, landscaped areas
and concrete sidewalk surrounding the buildings. Off-site improvements will mainly consist
of a sidewalk, a driveway connection, and an emergence access connection all along the
east side of Strauss Cabin Road.
Approximately 16 acres of the site is anticipated to be disturbed, which includes the area
of the proposed buildings and surface improvements. A summary of these areas is as
follows:
• Total Project Area: ±16 Acres
• Total Area of Disturbance: ±16 Acres
• Total Area of Staging/Storage: ±0.5 Acres
• Total Areas for Hauling: N/A
An existing dirt road access from Strauss Cabin Road will be utilized as the construction
access. BMPs will be established prior to construction. Silt fencing will be installed around
the construction limits and all silt fencing will remain in place until site is stabilized and
70% ground cover is established.
No known environmental impacts to wetland, streams and/or endangered species will
occur during this project. Permits used for this project will be a State Discharge Permit, a
Floodplain Use Permit and a Stockpile Permit.
II. Potential Pollutant Sources
The following is a list of potential sources of pollutants and the associated prescribed
control measures:
1. ALL DISTURBED AND STORED SOILS
Yes - Approximately 14.63 acres are anticipated to be disturbed. Topsoil will
be stripped and stockpiled in area along the southside of the project area.
Some excavated soils will be temporarily stockpiled on site. Appropriate BMP
measures, such as silt fencing, seeding and mulch will be implemented to
contain pollutants and stabilize disturbed and stockpile areas.
2. VEHICLE TRACKING OF SEDIMENTS
Yes - Sediment tracked onto existing pavements will receive ongoing sweeping
and/or scraping and collected for haul off. Equipment that requires washing will
either be washed inside the property or be loaded directly onto a trailer and
washed off-site. Vehicle tracking control will be implemented to help reduce
erosion and to minimize sediment from entering adjacent streets. Rock socks
Sanderson Stewart April 2021
Harmony 25 Parcel No. 8603000028 pg. 3
Project No. 19059.02
and inlet protection shall be installed downstream within Strauss Cabin Road
to intercept and filter any pollutants prior to escaping the site.
3. MANAGEMENT OF CONTAMINATED SOILS
No - There are no contaminated soils anticipated on this site.
4. LOADING & UNLOADING OPERATIONS
Yes - Workers will have sufficient parking within the western portion of the
property just east of Strauss Cabin Road thereby minimizing the on-site
through traffic. Equipment may be loaded and unloaded on-site to reduce soil
transport off the site. Any loading of material will be done directly from the
machine to the haul truck with appropriate containment BMP’s and clean up
measures in place.
5. OUTDOOR STORAGE OF CONSTRUCTION MATERIALS, BUILDING
MATERIALS, FERTILIZERS AND CHEMICALS
Yes/Possibly - There are no building materials anticipated for this project.
Although fertilizers may be used in the final stage of the project for stabilizing
vegetation, they will not be stored onsite due to the short duration of the
project. Materials that are not anticipated to generate pollutants along with on-
site construction vehicles will be stored/parked in a Stabilized Staging Area
located at the west of the site, approximately 600 feet from the floodway and
main grading operations.
6. BULK STORAGE OF MATERIALS
No - There are no bulk liquid chemicals or storage structures anticipated for
this project.
7. VEHICLE AND EQUIPMENT MAINTENANCE AND FUELING
Yes/Possibly - It is the intention that most, if not all, equipment requiring repair
shall be loaded onto a trailer and repaired off-site in a proper facility. If
necessary, all on-site equipment repair shall be performed within the Stabilized
Storage Area where potential chemical discharge will be contained and hauled
off.
8. SIGNIFICANT DUST OR PARTICULATE GENERATION PROCESSES
Yes - This project is not anticipated to generate much atmospheric pollution,
however, water trucks will be utilized, as needed, and vehicle speeds will be
limited to minimize dust emissions. Seeding of the disturbed area shall be
implemented upon completion of the improvements to that area. If needed, silt
Sanderson Stewart April 2021
Harmony 25 Parcel No. 8603000028 pg. 4
Project No. 19059.02
fence shall be installed as a wind break. The project will follow all requirements
described in the Fugitive Dust Control Ordinance No. 004, 2016, Section 12-150
through 12-160.
9. ROUTINE MAINTENANCE ACTIVITIES INVOLVING FERILIZERS,
PESTICIDES, DETERGENTS, FUELS, SOLVENTS, OILS, ETC.
Yes/Possibly - No routine maintenance is anticipated. If it’s needed, however, it
is the intention that equipment shall be maintenance off-site in a proper facility.
Any emergency on-site equipment maintenance shall be performed within the
Stabilized Storage Area at the west end of the site. Although the other
referenced chemicals may be used during the project, they will not be stored
onsite due to the short duration of the project.
10. ON-SITE WASTE MANAGEMENT PRACTICES
Yes - Any solid waste disposal will be collected and hauled off-site daily. Any
waste types to be disposed of at the end of each day will be temporarily stored
within the Stabilized Storage Area at the west end of the property.
11. CONCRETE TRUCK/EQUIPMENT WASHING
Yes – A concrete washout area is located near the construction access and
appropriate containment BMP’s and clean up measures will be utilized.
12. DEDICATED ASPHALT AND CONCRETE BATCH PLANTS
No dedicated batch plants are proposed.
13. NON-INDUSTRIAL WASTE SOURCES
Yes - A portable toilet will be utilized for non-industrial waste on-site. These
receptacles will be located a minimum of 50 feet from any inlet structure and
watercourse. Generated worker trash will be collected and transported off-site
daily.
14. SAW CUTTING AND GRINDING
Yes - Saw cutting and grinding will be performed along existing Strauss Cabin
Road for access improvements to the project site. Appropriate downstream
BMPs along curb lines and inlet protection will be implemented along with street
sweeping.
Sanderson Stewart April 2021
Harmony 25 Parcel No. 8603000028 pg. 5
Project No. 19059.02
15. OTHER NON-STORMWATER DISCHARGES
No - No other discharges, such as dewatering and/or wash water is anticipated
for this project.
16. OTHER POTENTIAL SPILL SOURCES
No - No other procedures or areas of potential spill sources are anticipated.
III. Control Measures
Installation and maintenance of temporary construction and permanent BMPs
(structural and non-structural) shall be performed in accordance with the detail
specification shown on the Erosion Control Detail Sheets in the H-25 Multi Family
Development Final Plan Set and the specifications contained within the Urban Storm
Drainage Criteria Manual, Volume 3, Chapter 6 & 7.
Structural Practices:
1. Silt Fencing – Silt fencing will be utilized as part of perimeter controls to
prevent sediment from leaving the project site. Silt fencing will be used
around the construction limits and the area to receive earthwork.
2. Rock/curb Socks – Rock socks shall be installed along the curb line of
Strauss Cabin Road, between the access to the project site and the
existing downstream curb inlet, to capture potential sediment tracked
within the roadway.
3. Inlet Protection – Inlet protection shall be implemented to protect the
installed inlets on site. Inlet protection will also be utilized on inlets
downstream in Strauss Cabin Road from potential sediment that is
tracked within the roadway.
4. Stabilized Staging Area – This BMP will be used to contain any on-site
construction parking, portable toilet and any non-pollutant generating
materials. This will be located toward the west end of the property and
proximate to the access off of Strauss Cabin Road and adjacent to the
existing dirt road within the property.
5. Vehicle Tracking Control – A vehicle tracking control pad shall be
provided at the entrance of the site to minimize the tracking of mud and
sediment onto the adjacent paved surfaces.
6. Stockpile Management – The stockpiled material will be stabilized
through this BMP utilizing silt fencing to contain potential sediment
transport and stabilize the material through seeding and mulching.
Sanderson Stewart April 2021
Harmony 25 Parcel No. 8603000028 pg. 6
Project No. 19059.02
Non-Structural Practices:
1. Permanent Seeding –Permanent seeding will be used to re-establish
vegetation within the graded areas and stabilization of the stockpiled
material. See seeding instructions below.
2. Mulch – Mulch may be used, as needed, to assist in the taking of the
seed by protecting the seedbed and stabilizing the soil by increasing
infiltration and reducing runoff. Utilize hydromulch on graded 4H:1V or
steeper slopes after seeding. Refer to Section VI of this report.
3. Street Sweeping – Strauss Cabin Road and Harmony Road shall be
kept free of sediment that has been tracked onto it through construction
activities. Sweeping or vacuuming should be conducted when there is
noticeable sediment accumulation on the roadway, adjacent to and
surrounding the construction site.
IV. Installation and Removal Sequence of Control Measures
The anticipated construction dates are as follows:
• Approximate Start Date: November 1, 2021
• Approximate Completion Date: September 1, 2022
• Final Stabilization Anticipated By: November 1, 2022
The following sequence of construction, land disturbing activities, and BMP
implementation are anticipated:
1. Obtain and ensure all necessary permits are in place.
2. Mobilization and perimeter erosion control installation:
a. Install Rock Socks and Inlet Protection within Strauss Cabin Road.
b. Install Vehicle Tracking Control.
c. Install Stabilized Staging Area with Portable Toilet.
d. Perimeter Silt Fencing to be installed around areas to be graded and limits
of construction area.
3. Construction Staking and Earthwork:
a. Perform construction staking.
b. Perform grubbing and stripping of topsoil.
c. Perform earthwork, grading and stockpiling.
d. Stockpile topsoil and stabilize.
4. Install Utilities, Pavement and Remaining Improvements:
a. Excavation for roadway subgrades and foundations
b. Stabilize any excess stockpiled material.
Sanderson Stewart April 2021
Harmony 25 Parcel No. 8603000028 pg. 7
Project No. 19059.02
5. Stabilize
a. Install silt fence around stockpiled material.
b. Seed and mulch newly graded areas, stockpiled material and disturbed
areas.
6. Removal of Temporary BMPs
a. Remove all BMPs except for the silt fencing.
b. Remove silt fencing upon achieving 70% minimum vegetated ground
cover. Re-seeding and additional mulch may be necessary along with
other methods implemented to establish vegetation such as erosion
control blanket and soil binders.
All temporary perimeter controls necessary to prevent sediment and/or pollutants from
leaving the site are to be installed prior to the commencement of construction activities.
V. Maintenance and Inspection of Requirements
BMP Inspections:
Routine and post-storm inspections of BMPs are essential to identify maintenance
necessary for the BMPs to remain in effective operating conditions. The frequency of
inspections is typically influenced by multiple factors including the weather, the phase of
construction, activities on site, and the types of BMPs.
In Colorado, the CDPS General Permit requires documented inspections on a biweekly
basis and within 24 hours of a storm event, with some limited, temporary exceptions for
inactive sites. UDFCD recommends spot-checking BMPs every workday. This is
typically reasonable to achieve and can help to ensure that the BMPs remain in good
working condition.
When the site or portions of the site are awaiting final stabilization (e.g., vegetative
cover), where construction is essentially complete, the recommended frequency of
inspection is at least once every month. Be sure that this change is documented and in
accordance with relevant permit requirements prior to reducing the inspection schedule.
Maintenance:
Proactive maintenance is fundamental to effective BMP performance. Rather than
maintaining the BMP in a reactive manner following failure, provide proactive
maintenance that may help to reduce the likelihood of failure. The types and frequencies
of maintenance are BMP-specific.
Maintain BMPs so that they function as intended. This includes removing accumulated
sediment before it limits the effectiveness of the BMP. Identify needed maintenance
activities during site inspections or during general observations of site conditions. Where
Sanderson Stewart April 2021
Harmony 25 Parcel No. 8603000028 pg. 8
Project No. 19059.02
BMPs have failed, repairs or changes should be initiated as soon as practical, to
minimize the discharge of pollutants.
Where the BMPs specified in the SWMP are not functioning effectively at the site,
modifications should be made that may include different or additional layers of BMPs.
When new BMPs are installed or BMPs are replaced, check the permit for
documentation requirements. This may require communication with the owner and/or
engineer and, at a minimum, should be documented in the inspection and maintenance
records (logbook).
The following is an abbreviated summary regarding inspection and maintenance for
BMPs proposed for this project (also refer to erosion control details in the construction
plans):
1. Silt Fencing – Inspect each work day and as soon as possible (always
within 24-hours) following a storm that causes surface erosion. Repair or
replacement shall occur immediately upon discovery of any failures.
Upstream accumulated sediment (at approximately 6-inches) shall be
removed, as needed to maintain the functionality of the BMP.
2. Construction Fencing – Inspect fences daily for damage and repair or
replace as necessary. Fencing should be tight and not slumping. Post
should be standing straight and secure in the ground.
3. Rock/curb Socks - Inspect each work day and as soon as possible
(always within 24-hours) following a storm that causes surface erosion.
Rock socks should be replaced if heavily soiled or damaged beyond
repair. Accumulated upstream sediment should be removed when
sediment is approximately ½ of the rock sock height.
4. Inlet Protection - Inspect each work day and as soon as possible
(always within 24-hours) following a storm that causes surface erosion.
Accumulated upstream sediment should be removed when sediment is
approximately ½ of the rock sock height in front of inlet opening.
5. Staked Sediment Control Logs – Logs shall be staked along the back of
the installed curb to help prevent sediment from running off the disturbed
ground onto the paved roads and gutters. Sediment buildup shall be
removed as needed. Sediment logs will be replaced and reinstalled to
maintain their effectiveness.
6. Stabilized Staging Area – Inspect each work day and as soon as
possible (always within 24-hours) following a storm that causes surface
erosion. Maintain them in effective operating condition with a stable
surface cover of gravel, repair perimeter silt fence as necessary and
follow good housekeeping practices. Rock shall be reapplied or
Sanderson Stewart April 2021
Harmony 25 Parcel No. 8603000028 pg. 9
Project No. 19059.02
regraded as necessary if rutting or underlying subgrade becomes
exposed.
7. Vehicle Tracking Control – Inspect each work day and as soon as
possible (always within 24-hours) following a storm that causes surface
erosion. Rock shall be reapplied or regraded as necessary to maintain a
consistent depth.
8. Concrete Washout Area – The washout area shall be installed before
concrete placement begin. Signage shall be posted that clearly
designates the washout area. Concrete waste shall be removed and
disposed of as needed.
9. Stockpile Management – Inspect each workday and as soon as possible
(always within 24-hours) following a storm that causes surface erosion.
Repair perimeter silt fence as necessary. If perimeter protection needs
to be removed to access stockpile, replace perimeter controls by end of
workday.
VI. Final Vegetation and Stability
Usable stripped topsoil will be re-distributed over the exposed dirt in areas where fill was
removed and areas of grading. Areas to receive seeding and mulching per the seeding
instructions below shall be the following:
• Exposed ground where construction activities are completed.
• Stockpiled material for 60 days or more.
• Other disturbed bare ground areas such as in the removed Stabilized Staging
Area and areas that received construction traffic and general operations.
Refer to the Final Stabilization and Project Completion notes on Sheet No. 2 of the
construction plans associated with this report.
Seeding Instructions:
Per the City of Fort Collins Land Use Code, Section 12-132, Soil shall be thoroughly
loosened to a depth of not less than eight (8) inches and soil amendment shall be
thoroughly incorporated into the soil to a depth of at least six (6) inches by tilling,
discing, or other suitable method, at a rate of at least three (3) cubic yards of soil
amendment per one thousand (1,000) square feet of area to be seeded, unless at
least four (4) inches of loose top soil has been placed on the area after completion of
construction activity on top of not less than four (4) inches of loosened subgrade
soils. Seed shall be applied to a depth of ¼” to ½” and conform to the standards
outlined in the seeding notes and details on Sheet Nos. 2 and 4 of the construction
plans associated with this report.
Sanderson Stewart April 2021
Harmony 25 Parcel No. 8603000028 pg. 10
Project No. 19059.02
Seeded areas to be mulched and crimped per Note No. 55 on Sheet No. 2 of the
construction plans associated with this report. Crimped mulch shall be applied to a
depth of 2” to 3”. Utilize hydromulch application on graded 4H:1V or steeper slopes
after seeding.
At the point the vegetation has reached 70% density and confirmed by the City of
Fort Collins, the warranty period for Erosion Control will begin and any temporary
Control Measures will be removed.
References
1. City of Fort Collins, December 2018, Fort Collins Stormwater Criteria Manual.
2. City of Fort Collins, December 2019, Fort Collins City Land Use Code.
3. Mile High Flood District, 2001 (November 2010 with some sections updated April 2018),
Urban Storm Drainage Criteria Manual, Volume 3, Stormwater Quality.
4. United States Department of Agriculture Natural Resources Conservation Service; Web Soil
Survey; accessed on-line September 2019.
5. Federal Emergency Management Agency; FEMA Flood Map Service Center; accessed on-
line September 2019.
APPENDIX
1. NRCS Soils Data
2. Erosion Control Plan
3. Erosion Control Notes
4. Erosion Control Details
(Escrow/Security Calculation Spreadsheet to be provided upon approval of this
report and the associated Erosion Control Plan)
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Engineering Properties
This table gives the engineering classifications and the range of engineering
properties for the layers of each soil in the survey area.
Hydrologic soil group is a group of soils having similar runoff potential under
similar storm and cover conditions. The criteria for determining Hydrologic soil
group is found in the National Engineering Handbook, Chapter 7 issued May
2007(http://directives.sc.egov.usda.gov/OpenNonWebContent.aspx?
content=17757.wba). Listing HSGs by soil map unit component and not by soil
series is a new concept for the engineers. Past engineering references contained
lists of HSGs by soil series. Soil series are continually being defined and
redefined, and the list of soil series names changes so frequently as to make the
task of maintaining a single national list virtually impossible. Therefore, the
criteria is now used to calculate the HSG using the component soil properties
and no such national series lists will be maintained. All such references are
obsolete and their use should be discontinued. Soil properties that influence
runoff potential are those that influence the minimum rate of infiltration for a bare
soil after prolonged wetting and when not frozen. These properties are depth to a
seasonal high water table, saturated hydraulic conductivity after prolonged
wetting, and depth to a layer with a very slow water transmission rate. Changes
in soil properties caused by land management or climate changes also cause the
hydrologic soil group to change. The influence of ground cover is treated
independently. There are four hydrologic soil groups, A, B, C, and D, and three
dual groups, A/D, B/D, and C/D. In the dual groups, the first letter is for drained
areas and the second letter is for undrained areas.
The four hydrologic soil groups are described in the following paragraphs:
Group A. Soils having a high infiltration rate (low runoff potential) when
thoroughly wet. These consist mainly of deep, well drained to excessively
drained sands or gravelly sands. These soils have a high rate of water
transmission.
Group B. Soils having a moderate infiltration rate when thoroughly wet. These
consist chiefly of moderately deep or deep, moderately well drained or well
drained soils that have moderately fine texture to moderately coarse texture.
These soils have a moderate rate of water transmission.
Group C. Soils having a slow infiltration rate when thoroughly wet. These consist
chiefly of soils having a layer that impedes the downward movement of water or
soils of moderately fine texture or fine texture. These soils have a slow rate of
water transmission.
Group D. Soils having a very slow infiltration rate (high runoff potential) when
thoroughly wet. These consist chiefly of clays that have a high shrink-swell
potential, soils that have a high water table, soils that have a claypan or clay
layer at or near the surface, and soils that are shallow over nearly impervious
material. These soils have a very slow rate of water transmission.
Depth to the upper and lower boundaries of each layer is indicated.
Engineering Properties---Larimer County Area, Colorado
Natural Resources
Conservation Service
Web Soil Survey
National Cooperative Soil Survey
1/14/2020
Page 1 of 5
Texture is given in the standard terms used by the U.S. Department of
Agriculture. These terms are defined according to percentages of sand, silt, and
clay in the fraction of the soil that is less than 2 millimeters in diameter. "Loam,"
for example, is soil that is 7 to 27 percent clay, 28 to 50 percent silt, and less than
52 percent sand. If the content of particles coarser than sand is 15 percent or
more, an appropriate modifier is added, for example, "gravelly."
Classification of the soils is determined according to the Unified soil classification
system (ASTM, 2005) and the system adopted by the American Association of
State Highway and Transportation Officials (AASHTO, 2004).
The Unified system classifies soils according to properties that affect their use as
construction material. Soils are classified according to particle-size distribution of
the fraction less than 3 inches in diameter and according to plasticity index, liquid
limit, and organic matter content. Sandy and gravelly soils are identified as GW,
GP, GM, GC, SW, SP, SM, and SC; silty and clayey soils as ML, CL, OL, MH,
CH, and OH; and highly organic soils as PT. Soils exhibiting engineering
properties of two groups can have a dual classification, for example, CL-ML.
The AASHTO system classifies soils according to those properties that affect
roadway construction and maintenance. In this system, the fraction of a mineral
soil that is less than 3 inches in diameter is classified in one of seven groups
from A-1 through A-7 on the basis of particle-size distribution, liquid limit, and
plasticity index. Soils in group A-1 are coarse grained and low in content of fines
(silt and clay). At the other extreme, soils in group A-7 are fine grained. Highly
organic soils are classified in group A-8 on the basis of visual inspection.
If laboratory data are available, the A-1, A-2, and A-7 groups are further
classified as A-1-a, A-1-b, A-2-4, A-2-5, A-2-6, A-2-7, A-7-5, or A-7-6. As an
additional refinement, the suitability of a soil as subgrade material can be
indicated by a group index number. Group index numbers range from 0 for the
best subgrade material to 20 or higher for the poorest.
Percentage of rock fragments larger than 10 inches in diameter and 3 to 10
inches in diameter are indicated as a percentage of the total soil on a dry-weight
basis. The percentages are estimates determined mainly by converting volume
percentage in the field to weight percentage. Three values are provided to
identify the expected Low (L), Representative Value (R), and High (H).
Percentage (of soil particles) passing designated sieves is the percentage of the
soil fraction less than 3 inches in diameter based on an ovendry weight. The
sieves, numbers 4, 10, 40, and 200 (USA Standard Series), have openings of
4.76, 2.00, 0.420, and 0.074 millimeters, respectively. Estimates are based on
laboratory tests of soils sampled in the survey area and in nearby areas and on
estimates made in the field. Three values are provided to identify the expected
Low (L), Representative Value (R), and High (H).
Liquid limit and plasticity index (Atterberg limits) indicate the plasticity
characteristics of a soil. The estimates are based on test data from the survey
area or from nearby areas and on field examination. Three values are provided to
identify the expected Low (L), Representative Value (R), and High (H).
References:
American Association of State Highway and Transportation Officials (AASHTO).
2004. Standard specifications for transportation materials and methods of
sampling and testing. 24th edition.
Engineering Properties---Larimer County Area, Colorado
Natural Resources
Conservation Service
Web Soil Survey
National Cooperative Soil Survey
1/14/2020
Page 2 of 5
Report—Engineering Properties
Absence of an entry indicates that the data were not estimated. The asterisk '*' denotes the representative texture; other
possible textures follow the dash. The criteria for determining the hydrologic soil group for individual soil components is
found in the National Engineering Handbook, Chapter 7 issued May 2007(http://directives.sc.egov.usda.gov/
OpenNonWebContent.aspx?content=17757.wba). Three values are provided to identify the expected Low (L),
Representative Value (R), and High (H).
Engineering Properties–Larimer County Area, Colorado
Map unit symbol and
soil name
Pct. of
map
unit
Hydrolo
gic
group
Depth USDA texture Classification Pct Fragments Percentage passing sieve number—Liquid
limit
Plasticit
y index
Unified AASHTO >10
inches
3-10
inches
4 10 40 200
In L-R-H L-R-H L-R-H L-R-H L-R-H L-R-H L-R-H L-R-H
5—Aquepts, loamy
Aquepts 80 A/D 0-60 Variable ——————————
22—Caruso clay
loam, 0 to 1 percent
slope
Caruso 85 D 0-35 Clay loam CL A-6 0- 0- 0 0- 0- 0 95-98-1
00
95-98-1
00
90-93-
95
70-75-
80
30-33
-35
10-13-1
5
35-44 Fine sandy loam,
sandy loam
SC-SM,
SM
A-2, A-4 0- 3- 5 0- 3- 5 85-90-
95
65-75-
85
40-60-
80
25-40-
55
20-23
-25
NP-3 -5
44-60 Sand, gravelly sand SP-SM,
SW-SM
A-1 0- 3- 5 0- 5- 10 60-75-
90
55-58-
60
30-38-
45
5-10- 15 —NP
64—Loveland clay
loam, 0 to 1 percent
slopes
Loveland 90 C 0-15 Clay loam CL A-6 0- 3- 5 0- 3- 5 90-95-1
00
85-93-1
00
80-85-
90
60-70-
80
30-35
-40
10-15-2
0
15-32 Clay loam, silty clay
loam, loam
CL, CL-
ML
A-4, A-6 0- 3- 5 0- 3- 5 90-95-1
00
85-93-1
00
80-85-
90
50-68-
85
25-30
-35
5-10-15
32-60 Very gravelly sand,
gravelly sand,
gravelly coarse
sand
GP, SP A-1 0- 3- 5 0- 5- 10 40-60-
80
30-50-
70
20-30-
40
0- 3- 5 —NP
Engineering Properties---Larimer County Area, Colorado
Natural Resources
Conservation Service
Web Soil Survey
National Cooperative Soil Survey
1/14/2020
Page 4 of 5
Physical Soil Properties
This table shows estimates of some physical characteristics and features that
affect soil behavior. These estimates are given for the layers of each soil in the
survey area. The estimates are based on field observations and on test data for
these and similar soils.
Depth to the upper and lower boundaries of each layer is indicated.
Particle size is the effective diameter of a soil particle as measured by
sedimentation, sieving, or micrometric methods. Particle sizes are expressed as
classes with specific effective diameter class limits. The broad classes are sand,
silt, and clay, ranging from the larger to the smaller.
Sand as a soil separate consists of mineral soil particles that are 0.05 millimeter
to 2 millimeters in diameter. In this table, the estimated sand content of each soil
layer is given as a percentage, by weight, of the soil material that is less than 2
millimeters in diameter.
Silt as a soil separate consists of mineral soil particles that are 0.002 to 0.05
millimeter in diameter. In this table, the estimated silt content of each soil layer is
given as a percentage, by weight, of the soil material that is less than 2
millimeters in diameter.
Clay as a soil separate consists of mineral soil particles that are less than 0.002
millimeter in diameter. In this table, the estimated clay content of each soil layer
is given as a percentage, by weight, of the soil material that is less than 2
millimeters in diameter.
The content of sand, silt, and clay affects the physical behavior of a soil. Particle
size is important for engineering and agronomic interpretations, for determination
of soil hydrologic qualities, and for soil classification.
The amount and kind of clay affect the fertility and physical condition of the soil
and the ability of the soil to adsorb cations and to retain moisture. They influence
shrink-swell potential, saturated hydraulic conductivity (Ksat), plasticity, the ease
of soil dispersion, and other soil properties. The amount and kind of clay in a soil
also affect tillage and earthmoving operations.
Moist bulk density is the weight of soil (ovendry) per unit volume. Volume is
measured when the soil is at field moisture capacity, that is, the moisture content
at 1/3- or 1/10-bar (33kPa or 10kPa) moisture tension. Weight is determined after
the soil is dried at 105 degrees C. In the table, the estimated moist bulk density
of each soil horizon is expressed in grams per cubic centimeter of soil material
that is less than 2 millimeters in diameter. Bulk density data are used to compute
linear extensibility, shrink-swell potential, available water capacity, total pore
space, and other soil properties. The moist bulk density of a soil indicates the
pore space available for water and roots. Depending on soil texture, a bulk
density of more than 1.4 can restrict water storage and root penetration. Moist
bulk density is influenced by texture, kind of clay, content of organic matter, and
soil structure.
Physical Soil Properties---Larimer County Area, Colorado
Natural Resources
Conservation Service
Web Soil Survey
National Cooperative Soil Survey
1/14/2020
Page 1 of 6
Saturated hydraulic conductivity (Ksat) refers to the ease with which pores in a
saturated soil transmit water. The estimates in the table are expressed in terms
of micrometers per second. They are based on soil characteristics observed in
the field, particularly structure, porosity, and texture. Saturated hydraulic
conductivity (Ksat) is considered in the design of soil drainage systems and
septic tank absorption fields.
Available water capacity refers to the quantity of water that the soil is capable of
storing for use by plants. The capacity for water storage is given in inches of
water per inch of soil for each soil layer. The capacity varies, depending on soil
properties that affect retention of water. The most important properties are the
content of organic matter, soil texture, bulk density, and soil structure. Available
water capacity is an important factor in the choice of plants or crops to be grown
and in the design and management of irrigation systems. Available water
capacity is not an estimate of the quantity of water actually available to plants at
any given time.
Linear extensibility refers to the change in length of an unconfined clod as
moisture content is decreased from a moist to a dry state. It is an expression of
the volume change between the water content of the clod at 1/3- or 1/10-bar
tension (33kPa or 10kPa tension) and oven dryness. The volume change is
reported in the table as percent change for the whole soil. The amount and type
of clay minerals in the soil influence volume change.
Linear extensibility is used to determine the shrink-swell potential of soils. The
shrink-swell potential is low if the soil has a linear extensibility of less than 3
percent; moderate if 3 to 6 percent; high if 6 to 9 percent; and very high if more
than 9 percent. If the linear extensibility is more than 3, shrinking and swelling
can cause damage to buildings, roads, and other structures and to plant roots.
Special design commonly is needed.
Organic matter is the plant and animal residue in the soil at various stages of
decomposition. In this table, the estimated content of organic matter is expressed
as a percentage, by weight, of the soil material that is less than 2 millimeters in
diameter. The content of organic matter in a soil can be maintained by returning
crop residue to the soil.
Organic matter has a positive effect on available water capacity, water infiltration,
soil organism activity, and tilth. It is a source of nitrogen and other nutrients for
crops and soil organisms.
Erosion factors are shown in the table as the K factor (Kw and Kf) and the T
factor. Erosion factor K indicates the susceptibility of a soil to sheet and rill
erosion by water. Factor K is one of six factors used in the Universal Soil Loss
Equation (USLE) and the Revised Universal Soil Loss Equation (RUSLE) to
predict the average annual rate of soil loss by sheet and rill erosion in tons per
acre per year. The estimates are based primarily on percentage of silt, sand, and
organic matter and on soil structure and Ksat. Values of K range from 0.02 to
0.69. Other factors being equal, the higher the value, the more susceptible the
soil is to sheet and rill erosion by water.
Erosion factor Kw indicates the erodibility of the whole soil. The estimates are
modified by the presence of rock fragments.
Erosion factor Kf indicates the erodibility of the fine-earth fraction, or the material
less than 2 millimeters in size.
Physical Soil Properties---Larimer County Area, Colorado
Natural Resources
Conservation Service
Web Soil Survey
National Cooperative Soil Survey
1/14/2020
Page 2 of 6
Erosion factor T is an estimate of the maximum average annual rate of soil
erosion by wind and/or water that can occur without affecting crop productivity
over a sustained period. The rate is in tons per acre per year.
Wind erodibility groups are made up of soils that have similar properties affecting
their susceptibility to wind erosion in cultivated areas. The soils assigned to
group 1 are the most susceptible to wind erosion, and those assigned to group 8
are the least susceptible. The groups are described in the "National Soil Survey
Handbook."
Wind erodibility index is a numerical value indicating the susceptibility of soil to
wind erosion, or the tons per acre per year that can be expected to be lost to
wind erosion. There is a close correlation between wind erosion and the texture
of the surface layer, the size and durability of surface clods, rock fragments,
organic matter, and a calcareous reaction. Soil moisture and frozen soil layers
also influence wind erosion.
Reference:
United States Department of Agriculture, Natural Resources Conservation
Service. National soil survey handbook, title 430-VI. (http://soils.usda.gov)
Physical Soil Properties---Larimer County Area, Colorado
Natural Resources
Conservation Service
Web Soil Survey
National Cooperative Soil Survey
1/14/2020
Page 3 of 6
Report—Physical Soil Properties
Three values are provided to identify the expected Low (L), Representative Value (R), and High (H).
Physical Soil Properties–Larimer County Area, Colorado
Map symbol
and soil name
Depth Sand Silt Clay Moist
bulk
density
Saturated
hydraulic
conductivity
Available
water
capacity
Linear
extensibility
Organic
matter
Erosion
factors
Wind
erodibility
group
Wind
erodibility
index
Kw Kf T
In Pct Pct Pct g/cc micro m/sec In/In Pct Pct
5—Aquepts,
loamy
Aquepts 0-60 ————4.23-364.61-70
5.00
———5
22—Caruso
clay loam, 0
to 1 percent
slope
Caruso 0-35 -35--34-27-31- 35 1.25-1.30
-1.35
0.42-0.92-1.41 0.18-0.20-0.
21
0.0- 1.5- 2.9 1.0- 1.5-
2.0
.32 .32 4 6 48
35-44 -64--27-5- 9- 13 1.35-1.43
-1.50
14.11-28.22-42.
34
0.06-0.10-0.
13
0.0- 1.5- 2.9 0.5- 0.8-
1.0
.32 .32
44-60 -97-- 2-0- 2- 3 1.45-1.53
-1.60
141.14-423.07-
705.00
0.02-0.03-0.
04
0.0- 1.5- 2.9 0.0- 0.3-
0.5
.02 .05
64—Loveland
clay loam, 0
to 1 percent
slopes
Loveland 0-15 -33--32-30-35- 40 1.20-1.23
-1.25
1.41-2.82-4.23 0.18-0.19-0.
20
3.0- 4.5- 5.9 1.0- 2.0-
3.0
.20 .20 3 6 48
15-32 -35--38-18-27- 35 1.35-1.40
-1.45
4.23-9.17-14.11 0.18-0.19-0.
20
0.0- 1.5- 2.9 1.0- 1.5-
2.0
.32 .32
32-60 -96-- 2-0- 3- 5 1.55-1.60
-1.65
141.14-423.07-
705.00
0.03-0.05-0.
06
0.0- 1.5- 2.9 0.0- 0.3-
0.5
.02 .05
Physical Soil Properties---Larimer County Area, Colorado
Natural Resources
Conservation Service
Web Soil Survey
National Cooperative Soil Survey
1/14/2020
Page 4 of 6
RUSLE2 Related Attributes
This report summarizes those soil attributes used by the Revised Universal Soil
Loss Equation Version 2 (RUSLE2) for the map units in the selected area. The
report includes the map unit symbol, the component name, and the percent of
the component in the map unit. Soil property data for each map unit component
include the hydrologic soil group, erosion factor Kf for the surface horizon,
erosion factor T, and the representative percentage of sand, silt, and clay in the
mineral surface horizon. Missing surface data may indicate the presence of an
organic layer.
Report—RUSLE2 Related Attributes
Soil properties and interpretations for erosion runoff calculations. The surface
mineral horizon properties are displayed or the first mineral horizon below an
organic surface horizon. Organic horizons are not displayed.
RUSLE2 Related Attributes–Larimer County Area, Colorado
Map symbol and soil name Pct. of
map unit
Slope
length
(ft)
Hydrologic group Kf T factor Representative value
% Sand % Silt % Clay
22—Caruso clay loam, 0 to 1
percent slope
Caruso 85 —D .32 4 35.4 33.6 31.0
64—Loveland clay loam, 0 to 1
percent slopes
Loveland 90 —C .20 3 33.3 31.7 35.0
81—Paoli fine sandy loam, 0 to
1 percent slopes
Paoli 85 —A .15 5 65.4 19.6 15.0
103—Stoneham loam, 5 to 9
percent slopes
Stoneham 85 —B .28 5 41.6 37.4 21.0
105—Table Mountain loam, 0
to 1 percent slopes
Table Mountain 85 —B .37 5 44.3 40.7 15.0
Data Source Information
Soil Survey Area: Larimer County Area, Colorado
Survey Area Data: Version 14, Sep 13, 2019
RUSLE2 Related Attributes---Larimer County Area, Colorado
Natural Resources
Conservation Service
Web Soil Survey
National Cooperative Soil Survey
1/14/2020
Page 1 of 1
FINAL DEVELOPMENT PLANFILE:PROJECT NO:CAD:QUALITY ASSURANCE:DRAWING HISTORYDATE DESCRIPTIONHARMONY & STRAUSS CABIN ROADEROSION CONTROL NOTESH-25 MULTI FAMILY DEVELOPMENT FORT COLLINS, COC7.1 CJS19059.02_DETAIL_PROD.DWGRS/EB/VJG2/19/201ST PDP SUBMITTAL7/01/209/30/2010/26/204/07/21--2ND PDP SUBMITTAL3RD PDP SUBMITTAL4TH PDP SUBMITTAL1ST FDP SUBMITTAL----19059.02“”
“”
CITY OF FORT COLLINS, COLORADO
UTILITY PLAN APPROVAL
APPROVED:
CHECKED BY:
CHECKED BY:
CHECKED BY:
CHECKED BY:
CITY ENGINEER DATE
STORMWATER UTILITY DATE
PARKS & RECREATION DATE
TRAFFIC ENGINEER DATE
ENVIRONMENTAL PLANNER DATE
FINAL DEVELOPMENT PLANFILE:PROJECT NO:CAD:QUALITY ASSURANCE:DRAWING HISTORYDATE DESCRIPTIONHARMONY & STRAUSS CABIN ROADEROSION CONTROL DETAILSH-25 MULTI FAMILY DEVELOPMENT FORT COLLINS, COC7.2 CJS19059.02_DETAIL_PROD.DWGRS/EB/VJG2/19/201ST PDP SUBMITTAL7/01/209/30/2010/26/204/07/21--2ND PDP SUBMITTAL3RD PDP SUBMITTAL4TH PDP SUBMITTAL1ST FDP SUBMITTAL----19059.02CITY OF FORT COLLINS, COLORADO
UTILITY PLAN APPROVAL
APPROVED:
CHECKED BY:
CHECKED BY:
CHECKED BY:
CHECKED BY:
CITY ENGINEER DATE
STORMWATER UTILITY DATE
PARKS & RECREATION DATE
TRAFFIC ENGINEER DATE
ENVIRONMENTAL PLANNER DATE
FINAL DEVELOPMENT PLANFILE:PROJECT NO:CAD:QUALITY ASSURANCE:DRAWING HISTORYDATE DESCRIPTIONHARMONY & STRAUSS CABIN ROADEROSION CONTROL DETAILSH-25 MULTI FAMILY DEVELOPMENT FORT COLLINS, COC7.3 CJS19059.02_DETAIL_PROD.DWGRS/EB/VJG2/19/201ST PDP SUBMITTAL7/01/209/30/2010/26/204/07/21--2ND PDP SUBMITTAL3RD PDP SUBMITTAL4TH PDP SUBMITTAL1ST FDP SUBMITTAL----19059.02CITY OF FORT COLLINS, COLORADO
UTILITY PLAN APPROVAL
APPROVED:
CHECKED BY:
CHECKED BY:
CHECKED BY:
CHECKED BY:
CITY ENGINEER DATE
STORMWATER UTILITY DATE
PARKS & RECREATION DATE
TRAFFIC ENGINEER DATE
ENVIRONMENTAL PLANNER DATE
FINAL DEVELOPMENT PLANFILE:PROJECT NO:CAD:QUALITY ASSURANCE:DRAWING HISTORYDATE DESCRIPTIONHARMONY & STRAUSS CABIN ROADEROSION CONTROL DETAILSH-25 MULTI FAMILY DEVELOPMENT FORT COLLINS, COC7.4 CJS19059.02_DETAIL_PROD.DWGRS/EB/VJG2/19/201ST PDP SUBMITTAL7/01/209/30/2010/26/204/07/21--2ND PDP SUBMITTAL3RD PDP SUBMITTAL4TH PDP SUBMITTAL1ST FDP SUBMITTAL----19059.02CITY OF FORT COLLINS, COLORADO
UTILITY PLAN APPROVAL
APPROVED:
CHECKED BY:
CHECKED BY:
CHECKED BY:
CHECKED BY:
CITY ENGINEER DATE
STORMWATER UTILITY DATE
PARKS & RECREATION DATE
TRAFFIC ENGINEER DATE
ENVIRONMENTAL PLANNER DATE