HomeMy WebLinkAboutENCLAVE AT REDWOOD - FDP220014 - SUBMITTAL DOCUMENTS - ROUND 8 - ECS Report
EROSION AND SEDIMENT CONTROL REPORT
FOR
ENCLAVE AT REDWOOD
FORT COLLINS, CO 80524
April 8, 2024
Owner/Developer/Contractor:
Brian Bratcher
9555 S Kingston Ct, Suite 200
Englewood, CO 80112
Ph: 303-488-0061
Email: bbratcher@drhorton.com
Design Engineer:
Rachel Patton, P.E.
1120 Lincoln Street, Suite 1000
Denver, CO 80203
Ph: 303-623-6300, Fax: 303-623-6311
Email: rpatton@hkseng.com
Harris Kocher Smith Project No.: 201013
Erosion Control Administrator:
Stormwater Management Plan
Enclave at Redwood
Page 2 of 9
TABLE OF CONTENTS
I. Location .................................................................................................................... 3
II. Nature of Construction Activity ................................................................................. 3
III. Sequence of Major Activities .................................................................................... 3
IV. Estimates of Site Area .............................................................................................. 3
V. Summary of Existing Data ........................................................................................ 3
VI. Existing Vegetation ................................................................................................... 4
VII. Potential Pollution Sources ....................................................................................... 4
VIII. Potential Non-Stormwater Discharges ...................................................................... 6
IX. Receiving Water(s) ................................................................................................... 6
X. Construction Schedule ............................................................................................. 7
XI. Stormwater Management Considerations ................................................................ 7
XII. Erosion and Sediment Control Measures (BMP’s) ................................................... 7
XIII. SWMP Administrator ................................................................................................ 9
XIV. Final Stabilization and Long-Term Stormwater Management ................................... 9
XV. Inspection and Maintenance ..................................................................................... 9
XVI. Conclusion .............................................................................................................. 10
XVII. References ............................................................................................................. 10
APPENDIX A – Vicinity Map, FIRM Map ........................................................................... 11
APPENDIX B – NRCS Soils Report .................................................................................... 12
APPENDIX C – Standard Operating Procedures ................................................................ 13
APPENDIX D – Erosion Control Plan ................................................................................ 14
Stormwater Management Plan
Enclave at Redwood
Page 3 of 9
I. Location
The proposed Enclave at Redwood development (hereinafter referred to as “Site”) is located in the
southeast ¼ of Section 1, Township 7 north, Range 69 west of the sixth Principal Meridian, City of
Fort Collins, County of Larimer, State of Colorado. The Site is bounded by Redwood Street to the west
and East Suniga Road to the south. A small portion of the Site exists south of East Suniga Road.
Adjacent developments include the Meadows at Redwood PUD Phase 1 (Redwood Meadows) to the
west, Northfield to the east and southeast, and Evergreen Park 3rd (Evergreen) to the north. Lake
Canal exists as an irrigation ditch adjacent to the Site to the east and southeast, and Redwood
Channel lies adjacent to the Site to the north. The Site will connect to Redwood St to the southwest,
Lupine Dr in Redwood Meadows to the west, Steeley Dr in Northfield to the southeast, and Collamer
Dr in Northfield to the east.
The Site consists of approximately 29.66 acres of undeveloped land, more specifically, totally
undeveloped grassland.
The Vicinity Map is included in Appendix A for reference.
II. Nature of Construction Activity
The Site will be developed as multi-family residential housing, with a mix of 1-, 2- and 3-bedroom
units totaling 238 units among 40-1- and 2-story buildings. The proposed development will also
include a clubhouse with a pool, amenity courtyard, surface parking, public and private roads, and
the associated utilities.
III. Sequence of Major Activities
The proposed sequence for major activities is described in detail in the Stormwater Management
Considerations section below. Please note that stockpiling activities have been designed as a
separate permit due to a significant amount of import that is needed for the Site.
IV. Estimates of Site Area
The Site is approximately 29.66 acres. Areas that will be disturbed by demolition, excavation, grading,
utility installation and other construction activities include approximately 28.37 acres of on-Site work
and 4.59 acres of off-Site for a total of 32.96 acres. The exact limits of disturbance are shown on the
SWMP included in Appendix D.
V. Summary of Existing Data
Currently, the Site is comprised of undeveloped grassland covering approximately 98% of the Site
based on observation. There are no visible existing structures or foundations. There is an existing City
owned drainage swale along the northern portion of the Site. This ditch conveys water from the
Redwood Meadows Pond that is northwest of the Site and flows from west to east to the wetlands
area northeast of the Site. There is also an existing irrigation canal owned by the Lake Canal Reservoir
Company adjacent to the Site to the east and southeast, which flows from southwest to northeast.
The Site generally slopes from west to east at grades between roughly 0.3% and 1% towards Lake
Canal. The side slopes of the canal vary from 2:1 to 4:1. The thalweg slope of the canal is very flat.
During irrigation flows in the canal, the canal flows to the northeast along the east property
boundary. Perimeter silt fence will contain stormwater run-off onSite. There are currently no existing
stormwater or erosion control measures on-Site.
Stormwater Management Plan
Enclave at Redwood
Page 4 of 9
The Redwood Meadows Pond has existing wetlands area which is adjacent to the northwest corner
of the Site. The wetlands boundary is approximately 10’ feet away from the property line. The
wetlands area is approximately 0.53 acres. There is an additional pond to the northeast. This pond is
the Evergreen East Pond which has approximately 1.64 acres of wetland. The city owned ditch on the
north side of the Site connects these two wetland areas. Perimeter controls will be implemented
along the south edge of the city owned ditch to retain stormwater onSite. Impacts to the wetlands
are not anticipated at this time and erosion measures will be put in place to contain stockpiles and
protect the Redwood Meadows Pond and wetlands from any Site runoff.
There are three soil types as identified by the Natural Resource Conservation Service (NRCS) Web
Soil Survey. Loveland Clay Loam, Nunn Clay Loam, and Nunn Clay Loam (wet). All soil on Site is
classified as hydrologic soil group C. These soils are cohesive and are moderately resistant to wind
and water erosion. A copy of the soil survey is included in Appendix B.
Ground water was also encountered during initial soil testing. Groundwater depths range from 8-12
feet from existing grade and will eventually be 8-17 feet under finished proposed grades.
Groundwater was not sampled and tested for any existing contamination. Soil testing did not show
any ground contamination.
The Site is shown on the Federal Emergency Agency’s (FEMA) Flood Insurance Rate Map (FIRM)
Community Panel Numbers 08069C0977G and 08069C0981G, effective June 17, 2008. Lake Canal is
partially located within Zone X (0.2% annual chance flood hazard) and therefore the Site is partially
within this zone. Because the development of the Site will not involve altering of Lake Canal, no
floodplain modifications are necessary. Please refer to Appendix A for more details.
VI. Existing Vegetation
Currently, the Site consists of mostly native grasses and vegetation. Vegetation covers approximately
98% of the Site. There is very little impervious area onSite, if any, in the current condition.
VII. Potential Pollution Sources
The construction activities associated with this project will have some potential to pollute the
storm water being discharged from the Site. If these erosion measures are not properly installed
off-Site sediment may occur with large stormwater flows. This has potential to damage the
surrounding wetlands. Below are the pollutants with a short description of each:
Disturbed and Stored Soils
Disturbed and stored soils are a potential pollution source for the Site. Implementing dust
mitigation, rock socks, and silt fence will control the disturbed and stored soils. Due to the large
amount of Import for this Site, a separate stockpile SWMP has been done. And all soil will be onSite
before commencement of other construction activities. Because of this temporary sediment control
measure such as silt fence, and rock socks will already be in place, and will remain until necessary
to remove.
Vehicle Tracking of Sediments
Vehicle tracking of sediments is a potential pollution source for the Site and will be controlled by a
vehicle tracking control pad(s) located at the construction entrance(s). Fencing will also limit vehicle
access to designated entry(s). Street sweeping will also be utilized to limit the tracking of sediment
off-Site.
Stormwater Management Plan
Enclave at Redwood
Page 5 of 9
Management of Contaminated Soils
The Contractor is responsible for monitoring for contaminated soils and notify the engineer and
Larimer County if discovered. Stockpiling activities will only grub topsoil. Material exposure is not
anticipated to be encountered at this time. On-Site soil samples did not contain any contamination.
It is the contractor’s responsibility to collect and legally dispose of contaminated soils.
Loading and Unloading Operations
Loading and unloading operations is a potential pollution source for the Site. Loading and
unloading operations shall take place within the stabilized staging area.
Vehicle and Equipment Maintenance and Fueling
Vehicle and equipment maintenance and fueling is a potential pollution source for the Site.
Measures shall also be taken to prevent spills or leaks of fuel, oils, lubricants, antifreeze, and other
contaminant fluids from construction vehicles to protect groundwater and stormwater runoff. All
equipment maintenance shall be performed in a designated area, and measures such as drip pans
shall be used to contain petroleum products. Spills of construction materials should be cleaned up
immediately and disposed of properly. The Contractor shall routinely inspect equipment for leaks
that could lead to discharge of petroleum products into surface runoff.
Outdoor Storage Activities
Outdoor storage activities are a potential pollution source for the Site. Materials sometimes used
at a construction Site present a potential for contamination of stormwater runoff. These may
include, but are not limited to building materials, fuel, oil, lubricants, paints, solvents, concrete
curing compounds, pesticides, fertilizers, chemicals, herbicides, etc. The contractor shall designate
an area where these products are stored in an enclosure, container, or lined earthen dike,
constructed to prevent discharge of these materials in runoff from the Site. These barriers will also
function to contain spilled materials from contact with surface runoff. Standard Operating
Procedures for material spill containment and clean-up are provided in Appendix C. Material other
than soil is not anticipated to be stored during stock piling activities.
Routine Maintenance Activities (Fertilizers, Pesticides, Detergents, Fuels, Solvents, and Oils)
Routine maintenance activities are a potential pollution source for this Site. Fertilizers and
pesticides will be used during this project when healthy vegetation is being established. These
products are highly soluble and can combine with stormwater if applied during or just before a
precipitation event. Contractor shall apply product per manufacturers recommendation and
designate an area where these products will be stored in an enclosure, container, or lined earthen
dike to prevent discharge of these materials to runoff from the Site. Detergents, fuels, solvents, and
oils will also likely be used on this Site. These contaminants are typically noticeable when mixed
with water by discoloration. Contractor shall keep an eye out for contamination and dispose of the
contaminated liquid right way. These products shall be stored within an enclosure, container,
trailer, or other method.
Dust or Particulate Generating Processes
Significant dust or particulate generating processes are a potential pollution source for the Site.
Dust mitigation, surface roughening, and seeding and mulching shall be implemented to mitigate
airborne dust pollutants. These activities will be need to be conducted in accordance with the City
of Fort Collins Fugitive Dust Ordinances. The Dust Control Manual can be found at
www.fcgov.com/dust
Stormwater Management Plan
Enclave at Redwood
Page 6 of 9
On-Site Waste Management Practices
On-Site waste management practices (waste piles, liquid wastes, dumpsters, etc.) are not a
potential pollution source for the Site during stockpile activities.
Saw Cutting and Grinding
Saw cutting and grinding are a potential pollution source for this Site. Cutting of existing streets will
be done on this Site, and the saws used can generate a significant amount of dust. Watering the
cutting surface to prevent airborne particulates is required per the Fort Collins Fugitive Dust
Manual. Contractor to prevent slurry from entering stormwater via vacuum or air drying and
sweeping after cutting has been finished.
Concrete Truck/Equipment Washing
Concrete truck and equipment washing is not a potential pollution source for the Site and should
only occur at the designated Concrete Washout Area shown on the SWMP.
Dedicated Asphalt and Concrete Batch Plans
Dedicated asphalt and concrete batch plants are not a potential pollution source for the Site. There
will not be any dedicated concrete or asphalt batch plants on Site.
Non-Industrial Waste Sources
Non-industrial waste sources such as worker trash and portable toilets are not potential pollution
source for the Site.
Other Areas or Procedures Where Potential Spills Can Occur
Other areas or procedures where potential spills can occur are not a potential pollution source for
the Site.
VIII. Potential Non-Stormwater Discharges
Non-stormwater components of discharge, such as condensate from construction trailers,
underground springs and landscape irrigation return flow are not anticipated to occur with this
development. However, the contractor shall be responsible to monitor for such discharges and notify
the engineer in such an event. If construction dewatering is necessary, the contractor shall be
responsible for ensuring a construction dewatering permit is obtained prior to discharging water to
surface water or storm sewer systems.
IX. Receiving Water(s)
During high stormwater events, the Site currently drains to the lake canal ditch, city owned ditch and
some minor flow may make its way into the Redwood Meadows Pond. There are no controls on Site
to direct run off in any concentrated direction. According to the EPA, there are two receiving waters
for this Site; Dry Creek which is the receiving water for the North East College Corridor Outfall
(NECCO) and Timnath Reservoir which receives irrigation water from Lake Canal Reservoir Company.
The NECCO storm line outfalls into Dry Creek just south of E Vine Dr. The runoff then travels
approximately 7,000 ft southeast, then runs approximately 2,500 ft south where it will ultimately end
up in the Poudre River.
Stormwater Management Plan
Enclave at Redwood
Page 7 of 9
X. Construction Schedule
Construction activities on this Project is scheduled to commence spring of 2024 with anticipated
completion will be in the fall of 2026. Construction BMPs for the entire Site shall be installed
according to the SWMP in Appendix E.
XI. Stormwater Management Considerations
Stormwater management for the Site will be accomplished in the following Phases:
Phase 1 - Prior to earth disturbances
Construction Fence (CF)
Vehicle tracking control (VTC)
Silt Fence (SF) installation
Inlet Protection (IP) at the existing inlets (Refer to Stormwater Management Plan)
Stabilized Staging Area installation
Phase 2 - During and immediately after earth disturbances
Maintenance of the previously installed measures
Roadway inspection and any necessary cleanup each day
Sediment basin (SB) installation
Concrete washout area (CWA) installation
Surface roughening where necessary
Temporary Soil Stockpile (SP) area installation
Seeding and Mulching
Phase 3 - After paving, foundation construction and underground utility construction
Maintenance of the previously installed measures
Installation of inlet protection on new storm inlets
Removal of sediment basin
Removal of concrete washout area
Phase 4 - Final
Maintenance of the previously installed measures
Installation of formal landscaping
Request for final inspection
Upon inspection approval, removal of temporary measures
XII. Erosion and Sediment Control Measures (BMP’s)
The following Best Management Practices (BMPs) shall be implemented as indicated, prior to and
during construction activities on the Site. The information shown below describes the BMP, when it
is estimated to be installed, and the maintenance requirements of the BMP. The Plan Set in
Appendix D displays the locations of the BMPs. The associated City of Fort Collins details can be
seen in Appendix D for BMP installation and maintenance.
Silt Fence (SF)
A woven geotextile fabric attached to wooden posts and trenched into the ground. It is used to
intercept sheet flow runoff from disturbed areas. The silt fence shall be installed prior to all land
disturbing activities. The contractor shall inspect and maintain all silt fence throughout
construction. Any section of silt fence that has a tear, hole, slumping, undercutting or has been
Stormwater Management Plan
Enclave at Redwood
Page 8 of 9
bypassed should be replaced with a new section. Accumulated sediment should be removed before
it reached a depth of 50% the height of the silt fence.
Vehicle Control Tracking (VTC)
A stabilized construction Site access where vehicles exit the Site onto paved public roads. It helps
removed sediment from vehicles, reducing tacking onto the paved surface. The vehicle control
tracking shall be installed prior to any land disturbing activities. Vehicle tracking control shall be
inspected and maintained throughout construction. Replace aggregate or material used for
stabilization at entrance/exit as needed. Ensure drainage ways are not blocked by vehicle tracking
control.
Stockpile Management (SP)
Area on Site where soils and other erodible materials are stored. Includes measures to minimize
erosion and sediment transport from soil stockpiles. The stockpile management area shall be
installed prior to any land disturbing activities. Stockpiles shall be inspected and maintained
throughout construction activities.
Inlet Protection (IP)
Permeable barriers installed around an inlet to filter runoff and remove sediment prior to entering
a storm drain inlet. These can be constructed from rock socks, sediment control logs, silt fence,
block and rock socks, or other materials approved by Commerce City. Area inlets can also be
protected by over-excavating around the inlet to form a sediment trap. Inlet protection shall be
installed prior to any land disturbing activities. Inlet protection shall be inspected and maintained
throughout construction activities. Ensure that flows do not bypass the inlet protection when
flowing to the storm drainage system. Accumulated sediment should be removed before it reaches
a depth of 50% the height of the inlet protection.
Rock Sock (RS)
Gravel that has been wrapped by wire mesh or a geotextile to form an elongated cylindrical filter.
Used either as a perimeter control or as part of inlet protection. These are intended to trap
sediment from storm water runoff that flows onto roadways because of construction activities.
Rock socks shall be installed prior to any land disturbing activities. Rock socks shall be inspected and
maintained throughout construction activities. Accumulated sediment should be removed before it
reaches a depth of 50% the height of the rock sock.
Construction Fence (CF)
Fence that restricts Site access to designated entrances and exits, delineates construction Site
boundaries and keeps construction out of sensitive areas such as natural areas to be preserved as
open space, wetlands and riparian areas. These may be chain link or plastic mesh. Construction
fence shall be installed prior to any construction activities. Construction fencing shall be inspected
and maintained through construction activities.
Seeding and Mulching (SM)
Measures that include means to return the exposed dirt to a stabilized condition, one what will not
continue to result in erosion or sediment transport. A City approved seed mix will be applied to
stabilize the stock pile until final grading activities have commenced.
Stormwater Management Plan
Enclave at Redwood
Page 9 of 9
Street Sweeping (SS)
Street sweeping and vacuuming is to remove sediment that has been tracked onto roadways to
reduce sediment transport into storm drain systems or a surface waterway. This can be done
manually or with specific vehicles designed for this purpose. Street sweeping should be performed
in periodic intervals and when there is noticeable sediment accumulation.
XIII. SWMP Administrator
The stormwater management plan (SWMP) administrator shall be the Construction Site
Superintendent.
The Site superintendent is responsible for implementing and maintaining the Stormwater
Management Plan.
The SWMP administrator shall contact the engineer of record for development and revisions of
the SWMP.
The SWMP administrator shall be responsible for reporting spills.
The SWMP administrator shall conduct Site inspections and shall verify that repairs to the BMPs
have been completed and certify corrections.
The SWMP administrator shall conduct BMP training.
XIV. Final Stabilization and Long-Term Stormwater Management
Upon the completion of stockpiling activities, proper stabilization and vegetation will be established
with a native seed mix. Disturbed open space areas and the stock pile area will be planted with Native
Seed. Disturbances are to be minimized, especially on slopes greater than 4:1. Final stabilization is
reached when all soil-disturbing activities at the Site have been completed, and uniform vegetative
cover has been established with a density of at least seventy percent of pre-disturbance levels or
equivalent permanent, physical erosion reduction methods have been employed. Soil compaction
will be minimized for areas where final stabilization will be achieved through vegetative cover or an
infiltration control measure. Areas where sod will be installed as designed, will require soil
perpetration and amending per City of Fort Collins Municipal Code Section 12-132.
Seeding needs to comply with City of Fort Collins landscape standards. See Stockpile plan notes and
approved landscape plans by others to establish proper native seed application and acceptance. All
seeded areas will be crimped and mulched same day or next day after seeding in accordance with
the Temporary and Permanent Seeding Details associated with this project as seen in the appendix,
and in accordance with the City of Fort Collins Erosion Control Criteria. Once installed there will be
no temporary irrigation system so all seeding will be monitored until the Site has reached a vegetative
cover (density) of 70%. It is anticipated that this Site will be seeded in the spring of 2023 and will be
fully established in the fall of 2026. 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, all
stormwater infrastructure will be cleaned with any sediment deposits being removed and disposed
of properly and then remaining temporary Control Measures will be removed.
XV. Inspection and Maintenance
At a minimum, the Permittee or contractor shall produce and retain weekly written inspection
records for all BMP’s and after significant precipitation events. All necessary maintenance and
repair shall be completed immediately. However, street sweeping is to be completed by the close
of the business day or on an as needed basis. It is the responsibility of the contractor to have all
erosion control devices in place and effective, prior to a storm event. Permittee or Contractor shall
produce written inspection records every seven (7) days and after significant precipitation events.
Stormwater Management Plan
Enclave at Redwood
Page 10 of 9
The SWMP Administrator must maintain a record of inspection results for a period of three (3)
years following expiration or inactivation of permit coverage.
Record Keeping and Documenting Inspections
The following items, at a minimum, must be documented as a part of the Site inspections:
i. The inspection date;
ii. Name(s) and Title(s) of personnel making the inspection;
iii. Weather conditions at the time of inspection;
iv. Phase of construction at the time of inspection;
v. Estimated acreage of disturbance at the time of inspection;
vi. Location(s) of discharges of sediment or other pollutants from the Site;
vii. Location(s) of control measures requiring routine maintenance;
viii. Location(s) and identification of inadequate control measures requiring corrective actions;
ix. Location(s) and identification of additional control measures need that were not in place at the
time of inspection;
x. Description of the minimum inspection frequency and any deviations from the minimum
inspection schedule
After adequate corrective action(s) has been taken, or where a report does not identify any incidents
requiring corrective action or maintenance, the report shall contain a signed statement indicating
the Site is in compliance with the permit to the best of the signer’s knowledge and belief.
XVI. Conclusion
This Stormwater Management Plan is in conformance with the State of Colorado Stormwater
Management Plan Preparation Guidance. Additional grading, erosion and sediment control
measures may be required of the owner or his/her agents, due to unforeseen erosion problems or
if the submitted plan does not function as intended. The requirements of this plan shall be the
obligation of the landowner and/or his successors or heirs; until such time as the plan is properly
completed, modified, or voided.
XVII. References
1. Fort Collins Amendment Manual Volume 3 Chapter 12; City Council of the City of Fort Collins.
2. Fort Collins Stormwater Criteria Manual; City Council of the City of Fort Collins; Revised December,
2018.
3. Urban Storm Drainage Criteria Manual: Volume 3; Urban Drainage and Flood Control District;
Updated April 2018.
APPENDIX A – Vicinity Map, FIRM Map
SHEET NUMBER
PROJECT #:
1120 Lincoln Street, Suite 1000
Denver, Colorado 80203
P: 303.623.6300 F: 303.623.6311
HarrisKocherSmith.com
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201013
ENCLAVE AT REDWOOD - VICINTY MAP
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DHI COMMUNITIES
NO CHANGES ARE TO BE MADE TO THIS DRAWING WITHOUT WRITTEN PERMISSION OF HARRIS KOCHER SM
0
SCALE: 1" =
800 800 1600
800'
APPENDIX B – NRCS Soils Report
United States
Department of
Agriculture
A product of the National
Cooperative Soil Survey,
a joint effort of the United
States Department of
Agriculture and other
Federal agencies, State
agencies including the
Agricultural Experiment
Stations, and local
participants
Custom Soil Resource
Report for
Larimer County
Area, ColoradoNatural
Resources
Conservation
Service
March 8, 2022
Preface
Soil surveys contain information that affects land use planning in survey areas.
They highlight soil limitations that affect various land uses and provide information
about the properties of the soils in the survey areas. Soil surveys are designed for
many different users, including farmers, ranchers, foresters, agronomists, urban
planners, community officials, engineers, developers, builders, and home buyers.
Also, conservationists, teachers, students, and specialists in recreation, waste
disposal, and pollution control can use the surveys to help them understand,
protect, or enhance the environment.
Various land use regulations of Federal, State, and local governments may impose
special restrictions on land use or land treatment. Soil surveys identify soil
properties that are used in making various land use or land treatment decisions.
The information is intended to help the land users identify and reduce the effects of
soil limitations on various land uses. The landowner or user is responsible for
identifying and complying with existing laws and regulations.
Although soil survey information can be used for general farm, local, and wider area
planning, onsite investigation is needed to supplement this information in some
cases. Examples include soil quality assessments (http://www.nrcs.usda.gov/wps/
portal/nrcs/main/soils/health/) and certain conservation and engineering
applications. For more detailed information, contact your local USDA Service Center
(https://offices.sc.egov.usda.gov/locator/app?agency=nrcs) or your NRCS State Soil
Scientist (http://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/contactus/?
cid=nrcs142p2_053951).
Great differences in soil properties can occur within short distances. Some soils are
seasonally wet or subject to flooding. Some are too unstable to be used as a
foundation for buildings or roads. Clayey or wet soils are poorly suited to use as
septic tank absorption fields. A high water table makes a soil poorly suited to
basements or underground installations.
The National Cooperative Soil Survey is a joint effort of the United States
Department of Agriculture and other Federal agencies, State agencies including the
Agricultural Experiment Stations, and local agencies. The Natural Resources
Conservation Service (NRCS) has leadership for the Federal part of the National
Cooperative Soil Survey.
Information about soils is updated periodically. Updated information is available
through the NRCS Web Soil Survey, the site for official soil survey information.
The U.S. Department of Agriculture (USDA) prohibits discrimination in all its
programs and activities on the basis of race, color, national origin, age, disability,
and where applicable, sex, marital status, familial status, parental status, religion,
sexual orientation, genetic information, political beliefs, reprisal, or because all or a
part of an individual's income is derived from any public assistance program. (Not
all prohibited bases apply to all programs.) Persons with disabilities who require
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alternative means for communication of program information (Braille, large print,
audiotape, etc.) should contact USDA's TARGET Center at (202) 720-2600 (voice
and TDD). To file a complaint of discrimination, write to USDA, Director, Office of
Civil Rights, 1400 Independence Avenue, S.W., Washington, D.C. 20250-9410 or
call (800) 795-3272 (voice) or (202) 720-6382 (TDD). USDA is an equal opportunity
provider and employer.
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Contents
Preface....................................................................................................................2
How Soil Surveys Are Made..................................................................................5
Soil Map..................................................................................................................8
Soil Map................................................................................................................9
Legend................................................................................................................10
Map Unit Legend................................................................................................11
Map Unit Descriptions.........................................................................................11
Larimer County Area, Colorado......................................................................13
22—Caruso clay loam, 0 to 1 percent slope...............................................13
64—Loveland clay loam, 0 to 1 percent slopes...........................................14
73—Nunn clay loam, 0 to 1 percent slopes.................................................15
76—Nunn clay loam, wet, 1 to 3 percent slopes.........................................16
References............................................................................................................19
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How Soil Surveys Are Made
Soil surveys are made to provide information about the soils and miscellaneous
areas in a specific area. They include a description of the soils and miscellaneous
areas and their location on the landscape and tables that show soil properties and
limitations affecting various uses. Soil scientists observed the steepness, length,
and shape of the slopes; the general pattern of drainage; the kinds of crops and
native plants; and the kinds of bedrock. They observed and described many soil
profiles. A soil profile is the sequence of natural layers, or horizons, in a soil. The
profile extends from the surface down into the unconsolidated material in which the
soil formed or from the surface down to bedrock. The unconsolidated material is
devoid of roots and other living organisms and has not been changed by other
biological activity.
Currently, soils are mapped according to the boundaries of major land resource
areas (MLRAs). MLRAs are geographically associated land resource units that
share common characteristics related to physiography, geology, climate, water
resources, soils, biological resources, and land uses (USDA, 2006). Soil survey
areas typically consist of parts of one or more MLRA.
The soils and miscellaneous areas in a survey area occur in an orderly pattern that
is related to the geology, landforms, relief, climate, and natural vegetation of the
area. Each kind of soil and miscellaneous area is associated with a particular kind
of landform or with a segment of the landform. By observing the soils and
miscellaneous areas in the survey area and relating their position to specific
segments of the landform, a soil scientist develops a concept, or model, of how they
were formed. Thus, during mapping, this model enables the soil scientist to predict
with a considerable degree of accuracy the kind of soil or miscellaneous area at a
specific location on the landscape.
Commonly, individual soils on the landscape merge into one another as their
characteristics gradually change. To construct an accurate soil map, however, soil
scientists must determine the boundaries between the soils. They can observe only
a limited number of soil profiles. Nevertheless, these observations, supplemented
by an understanding of the soil-vegetation-landscape relationship, are sufficient to
verify predictions of the kinds of soil in an area and to determine the boundaries.
Soil scientists recorded the characteristics of the soil profiles that they studied. They
noted soil color, texture, size and shape of soil aggregates, kind and amount of rock
fragments, distribution of plant roots, reaction, and other features that enable them
to identify soils. After describing the soils in the survey area and determining their
properties, the soil scientists assigned the soils to taxonomic classes (units).
Taxonomic classes are concepts. Each taxonomic class has a set of soil
characteristics with precisely defined limits. The classes are used as a basis for
comparison to classify soils systematically. Soil taxonomy, the system of taxonomic
classification used in the United States, is based mainly on the kind and character
of soil properties and the arrangement of horizons within the profile. After the soil
5
scientists classified and named the soils in the survey area, they compared the
individual soils with similar soils in the same taxonomic class in other areas so that
they could confirm data and assemble additional data based on experience and
research.
The objective of soil mapping is not to delineate pure map unit components; the
objective is to separate the landscape into landforms or landform segments that
have similar use and management requirements. Each map unit is defined by a
unique combination of soil components and/or miscellaneous areas in predictable
proportions. Some components may be highly contrasting to the other components
of the map unit. The presence of minor components in a map unit in no way
diminishes the usefulness or accuracy of the data. The delineation of such
landforms and landform segments on the map provides sufficient information for the
development of resource plans. If intensive use of small areas is planned, onsite
investigation is needed to define and locate the soils and miscellaneous areas.
Soil scientists make many field observations in the process of producing a soil map.
The frequency of observation is dependent upon several factors, including scale of
mapping, intensity of mapping, design of map units, complexity of the landscape,
and experience of the soil scientist. Observations are made to test and refine the
soil-landscape model and predictions and to verify the classification of the soils at
specific locations. Once the soil-landscape model is refined, a significantly smaller
number of measurements of individual soil properties are made and recorded.
These measurements may include field measurements, such as those for color,
depth to bedrock, and texture, and laboratory measurements, such as those for
content of sand, silt, clay, salt, and other components. Properties of each soil
typically vary from one point to another across the landscape.
Observations for map unit components are aggregated to develop ranges of
characteristics for the components. The aggregated values are presented. Direct
measurements do not exist for every property presented for every map unit
component. Values for some properties are estimated from combinations of other
properties.
While a soil survey is in progress, samples of some of the soils in the area generally
are collected for laboratory analyses and for engineering tests. Soil scientists
interpret the data from these analyses and tests as well as the field-observed
characteristics and the soil properties to determine the expected behavior of the
soils under different uses. Interpretations for all of the soils are field tested through
observation of the soils in different uses and under different levels of management.
Some interpretations are modified to fit local conditions, and some new
interpretations are developed to meet local needs. Data are assembled from other
sources, such as research information, production records, and field experience of
specialists. For example, data on crop yields under defined levels of management
are assembled from farm records and from field or plot experiments on the same
kinds of soil.
Predictions about soil behavior are based not only on soil properties but also on
such variables as climate and biological activity. Soil conditions are predictable over
long periods of time, but they are not predictable from year to year. For example,
soil scientists can predict with a fairly high degree of accuracy that a given soil will
have a high water table within certain depths in most years, but they cannot predict
that a high water table will always be at a specific level in the soil on a specific date.
After soil scientists located and identified the significant natural bodies of soil in the
survey area, they drew the boundaries of these bodies on aerial photographs and
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identified each as a specific map unit. Aerial photographs show trees, buildings,
fields, roads, and rivers, all of which help in locating boundaries accurately.
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Soil Map
The soil map section includes the soil map for the defined area of interest, a list of
soil map units on the map and extent of each map unit, and cartographic symbols
displayed on the map. Also presented are various metadata about data used to
produce the map, and a description of each soil map unit.
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Custom Soil Resource Report
Soil Map
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494200 494300 494400 494500 494600 494700 494800 494900 495000
494200 494300 494400 494500 494600 494700 494800 494900 495000
40° 36' 12'' N
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Map projection: Web Mercator Corner coordinates: WGS84 Edge tics: UTM Zone 13N WGS84
0 200 400 800 1200
Feet
0 50 100 200 300
Meters
Map Scale: 1:4,330 if printed on A landscape (11" x 8.5") sheet.
Soil Map may not be valid at this scale.
MAP LEGEND MAP INFORMATION
Area of Interest (AOI)
Area of Interest (AOI)
Soils
Soil Map Unit Polygons
Soil Map Unit Lines
Soil Map Unit Points
Special Point Features
Blowout
Borrow Pit
Clay Spot
Closed Depression
Gravel Pit
Gravelly Spot
Landfill
Lava Flow
Marsh or swamp
Mine or Quarry
Miscellaneous Water
Perennial Water
Rock Outcrop
Saline Spot
Sandy Spot
Severely Eroded Spot
Sinkhole
Slide or Slip
Sodic Spot
Spoil Area
Stony Spot
Very Stony Spot
Wet Spot
Other
Special Line Features
Water Features
Streams and Canals
Transportation
Rails
Interstate Highways
US Routes
Major Roads
Local Roads
Background
Aerial Photography
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 beyond 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: Larimer County Area, Colorado
Survey Area Data: Version 16, Sep 2, 2021
Soil map units are labeled (as space allows) for map scales
1:50,000 or larger.
Date(s) aerial images were photographed: Aug 11, 2018—Aug
12, 2018
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.
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Map Unit Legend
Map Unit Symbol Map Unit Name Acres in AOI Percent of AOI
22 Caruso clay loam, 0 to 1
percent slope
0.0 0.0%
64 Loveland clay loam, 0 to 1
percent slopes
6.7 26.3%
73 Nunn clay loam, 0 to 1 percent
slopes
11.8 46.2%
76 Nunn clay loam, wet, 1 to 3
percent slopes
7.0 27.4%
Totals for Area of Interest 25.6 100.0%
Map Unit Descriptions
The map units delineated on the detailed soil maps in a soil survey represent the
soils or miscellaneous areas in the survey area. The map unit descriptions, along
with the maps, can be used to determine the composition and properties of a unit.
A map unit delineation on a soil map represents an area dominated by one or more
major kinds of soil or miscellaneous areas. A map unit is identified and named
according to the taxonomic classification of the dominant soils. Within a taxonomic
class there are precisely defined limits for the properties of the soils. On the
landscape, however, the soils are natural phenomena, and they have the
characteristic variability of all natural phenomena. Thus, the range of some
observed properties may extend beyond the limits defined for a taxonomic class.
Areas of soils of a single taxonomic class rarely, if ever, can be mapped without
including areas of other taxonomic classes. Consequently, every map unit is made
up of the soils or miscellaneous areas for which it is named and some minor
components that belong to taxonomic classes other than those of the major soils.
Most minor soils have properties similar to those of the dominant soil or soils in the
map unit, and thus they do not affect use and management. These are called
noncontrasting, or similar, components. They may or may not be mentioned in a
particular map unit description. Other minor components, however, have properties
and behavioral characteristics divergent enough to affect use or to require different
management. These are called contrasting, or dissimilar, components. They
generally are in small areas and could not be mapped separately because of the
scale used. Some small areas of strongly contrasting soils or miscellaneous areas
are identified by a special symbol on the maps. If included in the database for a
given area, the contrasting minor components are identified in the map unit
descriptions along with some characteristics of each. A few areas of minor
components may not have been observed, and consequently they are not
mentioned in the descriptions, especially where the pattern was so complex that it
was impractical to make enough observations to identify all the soils and
miscellaneous areas on the landscape.
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The presence of minor components in a map unit in no way diminishes the
usefulness or accuracy of the data. The objective of mapping is not to delineate
pure taxonomic classes but rather to separate the landscape into landforms or
landform segments that have similar use and management requirements. The
delineation of such segments on the map provides sufficient information for the
development of resource plans. If intensive use of small areas is planned, however,
onsite investigation is needed to define and locate the soils and miscellaneous
areas.
An identifying symbol precedes the map unit name in the map unit descriptions.
Each description includes general facts about the unit and gives important soil
properties and qualities.
Soils that have profiles that are almost alike make up a soil series. Except for
differences in texture of the surface layer, all the soils of a series have major
horizons that are similar in composition, thickness, and arrangement.
Soils of one series can differ in texture of the surface layer, slope, stoniness,
salinity, degree of erosion, and other characteristics that affect their use. On the
basis of such differences, a soil series is divided into soil phases. Most of the areas
shown on the detailed soil maps are phases of soil series. The name of a soil phase
commonly indicates a feature that affects use or management. For example, Alpha
silt loam, 0 to 2 percent slopes, is a phase of the Alpha series.
Some map units are made up of two or more major soils or miscellaneous areas.
These map units are complexes, associations, or undifferentiated groups.
A complex consists of two or more soils or miscellaneous areas in such an intricate
pattern or in such small areas that they cannot be shown separately on the maps.
The pattern and proportion of the soils or miscellaneous areas are somewhat similar
in all areas. Alpha-Beta complex, 0 to 6 percent slopes, is an example.
An association is made up of two or more geographically associated soils or
miscellaneous areas that are shown as one unit on the maps. Because of present
or anticipated uses of the map units in the survey area, it was not considered
practical or necessary to map the soils or miscellaneous areas separately. The
pattern and relative proportion of the soils or miscellaneous areas are somewhat
similar. Alpha-Beta association, 0 to 2 percent slopes, is an example.
An undifferentiated group is made up of two or more soils or miscellaneous areas
that could be mapped individually but are mapped as one unit because similar
interpretations can be made for use and management. The pattern and proportion
of the soils or miscellaneous areas in a mapped area are not uniform. An area can
be made up of only one of the major soils or miscellaneous areas, or it can be made
up of all of them. Alpha and Beta soils, 0 to 2 percent slopes, is an example.
Some surveys include miscellaneous areas. Such areas have little or no soil
material and support little or no vegetation. Rock outcrop is an example.
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Larimer County Area, Colorado
22—Caruso clay loam, 0 to 1 percent slope
Map Unit Setting
National map unit symbol: jpvt
Elevation: 4,800 to 5,500 feet
Mean annual precipitation: 13 to 15 inches
Mean annual air temperature: 48 to 50 degrees F
Frost-free period: 135 to 150 days
Farmland classification: Prime farmland if irrigated
Map Unit Composition
Caruso and similar soils:85 percent
Minor components:15 percent
Estimates are based on observations, descriptions, and transects of the mapunit.
Description of Caruso
Setting
Landform:Flood-plain steps, stream terraces
Landform position (three-dimensional):Tread
Down-slope shape:Linear
Across-slope shape:Linear
Parent material:Mixed alluvium
Typical profile
H1 - 0 to 35 inches: clay loam
H2 - 35 to 44 inches: fine sandy loam
H3 - 44 to 60 inches: gravelly sand
Properties and qualities
Slope:0 to 1 percent
Depth to restrictive feature:More than 80 inches
Drainage class:Somewhat poorly drained
Runoff class: High
Capacity of the most limiting layer to transmit water (Ksat):Moderately low to
moderately high (0.06 to 0.20 in/hr)
Depth to water table:About 24 to 48 inches
Frequency of flooding:NoneOccasional
Frequency of ponding:None
Calcium carbonate, maximum content:5 percent
Maximum salinity:Nonsaline to very slightly saline (0.0 to 2.0 mmhos/cm)
Available water supply, 0 to 60 inches: Moderate (about 8.4 inches)
Interpretive groups
Land capability classification (irrigated): 3w
Land capability classification (nonirrigated): 5w
Hydrologic Soil Group: D
Ecological site: R067BY036CO - Overflow
Hydric soil rating: No
Minor Components
Loveland
Percent of map unit:9 percent
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Landform:Terraces
Ecological site:R067BY036CO - Overflow
Hydric soil rating: Yes
Fluvaquents
Percent of map unit:6 percent
Landform:Terraces
Hydric soil rating: Yes
64—Loveland clay loam, 0 to 1 percent slopes
Map Unit Setting
National map unit symbol: jpx9
Elevation: 4,800 to 5,500 feet
Mean annual precipitation: 13 to 15 inches
Mean annual air temperature: 48 to 50 degrees F
Frost-free period: 135 to 150 days
Farmland classification: Prime farmland if irrigated
Map Unit Composition
Loveland and similar soils:90 percent
Minor components:10 percent
Estimates are based on observations, descriptions, and transects of the mapunit.
Description of Loveland
Setting
Landform:Stream terraces, flood plains
Landform position (three-dimensional):Tread
Down-slope shape:Linear
Across-slope shape:Linear
Parent material:Alluvium
Typical profile
H1 - 0 to 15 inches: clay loam
H2 - 15 to 32 inches: loam
H3 - 32 to 60 inches: very gravelly sand
Properties and qualities
Slope:0 to 1 percent
Depth to restrictive feature:More than 80 inches
Drainage class:Poorly drained
Runoff class: Medium
Capacity of the most limiting layer to transmit water (Ksat):Moderately high (0.20
to 0.60 in/hr)
Depth to water table:About 18 to 36 inches
Frequency of flooding:NoneOccasional
Frequency of ponding:None
Calcium carbonate, maximum content:15 percent
Maximum salinity:Very slightly saline to slightly saline (2.0 to 4.0 mmhos/cm)
Available water supply, 0 to 60 inches: Moderate (about 7.5 inches)
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Interpretive groups
Land capability classification (irrigated): 3w
Land capability classification (nonirrigated): 3w
Hydrologic Soil Group: C
Ecological site: R067BY036CO - Overflow
Hydric soil rating: No
Minor Components
Aquolls
Percent of map unit:5 percent
Landform:Swales
Hydric soil rating: Yes
Poudre
Percent of map unit:5 percent
Ecological site:R067BY036CO - Overflow
Hydric soil rating: No
73—Nunn clay loam, 0 to 1 percent slopes
Map Unit Setting
National map unit symbol: 2tlng
Elevation: 4,100 to 5,700 feet
Mean annual precipitation: 14 to 15 inches
Mean annual air temperature: 48 to 52 degrees F
Frost-free period: 135 to 152 days
Farmland classification: Prime farmland if irrigated
Map Unit Composition
Nunn and similar soils:85 percent
Minor components:15 percent
Estimates are based on observations, descriptions, and transects of the mapunit.
Description of Nunn
Setting
Landform:Terraces
Landform position (three-dimensional):Tread
Down-slope shape:Linear
Across-slope shape:Linear
Parent material:Pleistocene aged alluvium and/or eolian deposits
Typical profile
Ap - 0 to 6 inches: clay loam
Bt1 - 6 to 10 inches: clay loam
Bt2 - 10 to 26 inches: clay loam
Btk - 26 to 31 inches: clay loam
Bk1 - 31 to 47 inches: loam
Bk2 - 47 to 80 inches: loam
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Properties and qualities
Slope:0 to 1 percent
Depth to restrictive feature:More than 80 inches
Drainage class:Well drained
Runoff class: Medium
Capacity of the most limiting layer to transmit water (Ksat):Moderately low to
moderately high (0.06 to 0.20 in/hr)
Depth to water table:More than 80 inches
Frequency of flooding:None
Frequency of ponding:None
Calcium carbonate, maximum content:7 percent
Maximum salinity:Nonsaline (0.1 to 1.0 mmhos/cm)
Sodium adsorption ratio, maximum:0.5
Available water supply, 0 to 60 inches: High (about 9.1 inches)
Interpretive groups
Land capability classification (irrigated): 3e
Land capability classification (nonirrigated): 4e
Hydrologic Soil Group: C
Ecological site: R067BY042CO - Clayey Plains
Hydric soil rating: No
Minor Components
Heldt
Percent of map unit:10 percent
Landform:Terraces
Landform position (three-dimensional):Tread
Down-slope shape:Linear
Across-slope shape:Linear
Ecological site:R067BY042CO - Clayey Plains
Hydric soil rating: No
Wages
Percent of map unit:5 percent
Landform:Terraces
Landform position (three-dimensional):Tread
Down-slope shape:Linear
Across-slope shape:Linear
Ecological site:R067BY002CO - Loamy Plains
Hydric soil rating: No
76—Nunn clay loam, wet, 1 to 3 percent slopes
Map Unit Setting
National map unit symbol: jpxq
Elevation: 4,800 to 5,600 feet
Mean annual precipitation: 13 to 15 inches
Mean annual air temperature: 48 to 50 degrees F
Frost-free period: 135 to 150 days
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Farmland classification: Prime farmland if irrigated
Map Unit Composition
Nunn, wet, and similar soils:90 percent
Minor components:10 percent
Estimates are based on observations, descriptions, and transects of the mapunit.
Description of Nunn, Wet
Setting
Landform:Stream terraces, alluvial fans
Landform position (three-dimensional):Base slope, tread
Down-slope shape:Linear
Across-slope shape:Linear
Parent material:Alluvium
Typical profile
H1 - 0 to 10 inches: clay loam
H2 - 10 to 47 inches: clay
H3 - 47 to 60 inches: gravelly loam
Properties and qualities
Slope:1 to 3 percent
Depth to restrictive feature:More than 80 inches
Drainage class:Somewhat poorly drained
Runoff class: Medium
Capacity of the most limiting layer to transmit water (Ksat):Moderately low to
moderately high (0.06 to 0.60 in/hr)
Depth to water table:About 24 to 36 inches
Frequency of flooding:NoneRare
Frequency of ponding:None
Calcium carbonate, maximum content:10 percent
Maximum salinity:Nonsaline to very slightly saline (0.0 to 2.0 mmhos/cm)
Available water supply, 0 to 60 inches: High (about 9.9 inches)
Interpretive groups
Land capability classification (irrigated): 2w
Land capability classification (nonirrigated): 3s
Hydrologic Soil Group: C
Ecological site: R067BZ902CO - Loamy Plains
Hydric soil rating: No
Minor Components
Heldt
Percent of map unit:6 percent
Ecological site:R067BZ902CO - Loamy Plains
Hydric soil rating: No
Dacono
Percent of map unit:3 percent
Ecological site:R067BY042CO - Clayey Plains
Hydric soil rating: No
Mollic halaquepts
Percent of map unit:1 percent
Landform:Swales
Hydric soil rating: Yes
Custom Soil Resource Report
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Custom Soil Resource Report
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References
American Association of State Highway and Transportation Officials (AASHTO).
2004. Standard specifications for transportation materials and methods of sampling
and testing. 24th edition.
American Society for Testing and Materials (ASTM). 2005. Standard classification of
soils for engineering purposes. ASTM Standard D2487-00.
Cowardin, L.M., V. Carter, F.C. Golet, and E.T. LaRoe. 1979. Classification of
wetlands and deep-water habitats of the United States. U.S. Fish and Wildlife
Service FWS/OBS-79/31.
Federal Register. July 13, 1994. Changes in hydric soils of the United States.
Federal Register. September 18, 2002. Hydric soils of the United States.
Hurt, G.W., and L.M. Vasilas, editors. Version 6.0, 2006. Field indicators of hydric
soils in the United States.
National Research Council. 1995. Wetlands: Characteristics and boundaries.
Soil Survey Division Staff. 1993. Soil survey manual. Soil Conservation Service.
U.S. Department of Agriculture Handbook 18. http://www.nrcs.usda.gov/wps/portal/
nrcs/detail/national/soils/?cid=nrcs142p2_054262
Soil Survey Staff. 1999. Soil taxonomy: A basic system of soil classification for
making and interpreting soil surveys. 2nd edition. Natural Resources Conservation
Service, U.S. Department of Agriculture Handbook 436. http://
www.nrcs.usda.gov/wps/portal/nrcs/detail/national/soils/?cid=nrcs142p2_053577
Soil Survey Staff. 2010. Keys to soil taxonomy. 11th edition. U.S. Department of
Agriculture, Natural Resources Conservation Service. http://
www.nrcs.usda.gov/wps/portal/nrcs/detail/national/soils/?cid=nrcs142p2_053580
Tiner, R.W., Jr. 1985. Wetlands of Delaware. U.S. Fish and Wildlife Service and
Delaware Department of Natural Resources and Environmental Control, Wetlands
Section.
United States Army Corps of Engineers, Environmental Laboratory. 1987. Corps of
Engineers wetlands delineation manual. Waterways Experiment Station Technical
Report Y-87-1.
United States Department of Agriculture, Natural Resources Conservation Service.
National forestry manual. http://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/
home/?cid=nrcs142p2_053374
United States Department of Agriculture, Natural Resources Conservation Service.
National range and pasture handbook. http://www.nrcs.usda.gov/wps/portal/nrcs/
detail/national/landuse/rangepasture/?cid=stelprdb1043084
19
United States Department of Agriculture, Natural Resources Conservation Service.
National soil survey handbook, title 430-VI. http://www.nrcs.usda.gov/wps/portal/
nrcs/detail/soils/scientists/?cid=nrcs142p2_054242
United States Department of Agriculture, Natural Resources Conservation Service.
2006. Land resource regions and major land resource areas of the United States,
the Caribbean, and the Pacific Basin. U.S. Department of Agriculture Handbook
296. http://www.nrcs.usda.gov/wps/portal/nrcs/detail/national/soils/?
cid=nrcs142p2_053624
United States Department of Agriculture, Soil Conservation Service. 1961. Land
capability classification. U.S. Department of Agriculture Handbook 210. http://
www.nrcs.usda.gov/Internet/FSE_DOCUMENTS/nrcs142p2_052290.pdf
Custom Soil Resource Report
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APPENDIX C – Standard Operating Procedures
Enclave at Redwood Standard Operating Procedure (SOP)
Minor Spill of Material (Paint, Stain, Solvent, Glue) (Less than Reportable
Quantity)
A. Purpose
The purpose of this Standard Operating Procedure is to establish uniform
procedures for clean up and disposal of material from a minor accidental spill of
paint, stain, solvent, or glue. The procedures outlined in this SOP are applicable
to all personnel working on site. Clean up and proper disposal of spilled material
into the soil or onto the ground surface is required to ensure the material or
contaminated soil does not enter or impact the waters of the state or the sanitary
sewer system.
B. Summary of the Method
This procedure outlines the steps to be taken to prevent spilled material from
impacting waters of the state and disposal of the resulting contaminated cleanup
material.
C. Definitions
1. Material Safety Data Sheet (MSDS). The standard industry list for a
product detailing the chemical make-up, safety hazards, first aid, fire
fighting, and spill cleanup measures, handling, storage, and disposal
methods
D. Health and Safety Warnings
Many construction materials may be flammable, cause skin and eye irritation,
and may be harmful or fatal if swallowed. Caution should be used during clean
up operations. The MSDS for the spilled material should be consulted to ensure
personnel safety during cleanup operations.
E. Equipment and Supplies
1. Absorbent pads and booms
2. Hand equipment (shovels, brooms)
3. Waste containers (5 gallon buckets, drums)
4. Personal Protective Equipment
F. Procedural Steps
1. Shut down all equipment operating in the area to prevent ignition of the
spill.
2. Quickly control the spill by stopping or securing the spill source. This
could be as simple as up-righting a tipped container or shutting down a
piece of equipment producing the spill.
3. Contact the Responsible Person on site to enact the emergency response
contact procedure.
a. Responsible Person shall consult the MSDS for proper spill
procedures and determination of Reportable Quantity for a spill.
In the event the spilled quantity exceeds the reportable quantity
the Responsible Person shall contact:
1. Call 911 for fire control if necessary.
2. Colorado Environmental Release and Incident Reporting
Hotline (1-877-518-5608)
3. Fort Collins: (970) 416-2740
b. A release of any chemical, oil, petroleum product, sewage, etc.,
which may enter waters of the State of Colorado (which include
surface water, ground water, and dry gullies or storm sewers
leading to surface water) must be reported to CDPHE
immediately (25-8-601 CRS).
4. Prevent migration of the spill by using an absorbent. This could include
absorbent pads or booms, floor dry, cat litter, or dirt. The absorbent
should be spread across the spill and along the downhill side to stop any
flow.
5. If necessary to prevent the material from entering a storm inlet or manhole
a dam of absorbent material should be placed in the g utter upstream from
the inlet.
6. Begin cleanup of the spilled material and absorbents by placing the
materials in 5 gallon, plastic buckets with lids or into a provided drum.
7. Continue cleanup until all spilled material and contaminated absorbents
are removed. On a hard surface this should include sweeping of the area.
Material spilled on dirt should be removed down to a level where
discoloration of the soil has been removed. Water shall never be used to
flush material off a surface.
8. All material shall be properly stored in a location designated by the
Responsible Person on site.
9. The Responsible Person shall contact the Site Contracted Emergency
Response and Disposal Co. to collect and properly dispose of the
material.
10. Location of the spill will be documented on the Stormwater Maintenance
Plan (SWMP) in the construction trailer.
11. Inspection of materials and equipment shall occur daily.
G. Record Management
All documentation from the incident, including incident report and incident
disposal manifests, shall be maintained at NexMetro Communities. 5601 Old E
Wadsworth Blvd, Suite 220, Arvada, CO 800002, for a period of 3 years from the
date of the spill.
H. After Incident Briefing
All personnel involved in the incident shall attend a debriefing to determine the
cause of the spill, procedures followed, and corrective actions to prevent future
spills. All pertinent data shall be documented. All fin dings from the debriefing
should be discussed at the next Safety Meeting. Fort Collins shall be notified.
Standard Operating Procedure (SOP)
Minor Fuel or Oil Spill (Less than 5 Gallons)
A. Purpose
The purpose of this Standard Operating Procedure is to establish a uniform
procedure for clean up and disposal of material from a minor accidental spill of
fuel (gasoline or diesel) or oil (hydraulic or motor). The procedures outlined in this
SOP are applicable to all personnel working on site. Clean up and p roper
disposal of spilled fuel or oil into the soil or onto the ground surface is required to
ensure the material or contaminated soil does not enter or impact the waters of
the state or the sanitary sewer system.
B. Summary of the Method
This procedure outlines the steps to be taken to prevent spilled fuel or oil from
impacting waters of the state and disposal of the resulting contaminated cleanup
material.
C. Definitions
1. Material Safety Data Sheet (MSDS). The standard industry list for a
product detailing the chemical make-up, safety hazards, first aid, fire
fighting, and spill cleanup measures, handling, storage, and disposal
methods
D. Health and Safety Warnings
Fuels and fuel oils may be extremely flammable, cause skin and eye irritation,
and may be harmful or fatal if swallowed. Caution should be used during clean
up operations. The MSDS for the spilled material should be consulted to ensure
personnel safety during cleanup operations.
E. Equipment and Supplies
1. Absorbent pads and booms
2. Hand equipment (shovels, brooms)
3. Waste containers (5 gallon buckets, drums)
4. Personal Protective Equipment
F. Procedural Steps
1. Shut down all equipment operating in the area to prevent ignition of the
spill.
2. Quickly control the spill by stopping or securing the spill source. This
could be as simple as up-righting a tipped container or shutting down a
piece of equipment producing the spill.
3. Contact the Responsible Person on site to enact the emergency response
contact procedure.
a. Responsible Person shall consult the MSDS for proper spill
procedures and determination of Reportable Quantity for a spill.
In the event the spilled quantity exceeds the reportable quantity
the Responsible Person shall contact:
1. Call 911 for fire control if necessary.
2. Colorado Environmental Release and Incident Reporting
Hotline (1-877-518-5608)
3. Fort Collins: (970) 416-2740
b. A release of any chemical, oil, petroleum product, sewage, etc.,
which may enter waters of the State of Colorado (which include
surface water, ground water, and dry gullies or storm sewers
leading to surface water) must be reported to CDPHE
immediately (25-8-601 CRS).
4. Prevent migration of the spill by using an absorbent. This could include
absorbent pads or booms, floor dry, cat litter, or dirt. The absorbent
should be spread across the spill and along the downhill side to stop any
flow.
5. If necessary to prevent the material from entering a storm inlet or manhole
a dam of absorbent material should be placed in the gutter upstream from
the inlet.
6. Begin cleanup of the spilled material and absorbents by placing the
materials in 5 gallon, plastic buckets with lids or into a provided drum.
7. Continue cleanup until all spilled material and contaminated absorbents
are removed. On a hard surface this should include sweeping of the area.
Material spilled on dirt should be removed down to a level where
discoloration of the soil has been removed. Water shall never be used to
flush material off a surface.
8. All material shall be properly stored in a location designated by the
Responsible Person on site.
9. The Responsible Person shall contact the Site Contracted Emergency
Response and Disposal Co to collect and properly dispose of the material.
10. Location of the spill will be documented on the Stormwater Maintenance
Plan (SWMP) in the construction trailer.
11. Inspection of materials and equipment shall occur daily.
G. Record Management
All documentation from the incident, including incident report and incident
disposal manifests, shall be maintained at NexMetro Communities. 5601 Old E
Wadsworth Blvd, Suite 220, Arvada, CO 800002, for a period of 3 years from the
date of the spill.
H. After Incident Briefing
All personnel involved in the incident shall attend a debriefing to determine the
cause of the spill, procedures followed, and corrective actions to preven t future
spills. All pertinent data will be recorded. All findings from the debriefing should
be discussed at the next Safety Meeting. Fort Collins shall be notified.
Standard Operating Procedure (SOP)
Small Fuel or Oil Spill (5 Gallons to Less than 25 Gallons)
A. Purpose
The purpose of this Standard Operating Procedure is to establish a uniform
procedure for clean up and disposal of material from a small acc idental spill of
fuel (gasoline or diesel) or oil (hydraulic, or motor). The procedures outlined in
this SOP are applicable to all personnel working on Site. Clean up and proper
disposal of spilled fuel or oil into the soil or onto the ground surface is required to
ensure the material or contaminated soil do not enter or impact the waters of the
state or the sanitary sewer system.
B. Summary of the Method
This procedure outlines the steps to be taken to prevent spilled fuel or oil from
impacting waters of the state and disposal of the resulting contaminated cleanup
material.
C. Definitions
1. Material Safety Data Sheet (MSDS). The standard industry list for a
product detailing the chemical make-up, safety hazards, first aid, fire
fighting, and spill cleanup measures, handling, storage, and disposal
methods
D. Health and Safety Warnings
Fuels and fuel oils may be extremely flammable, cause skin and eye irritation,
and may be harmful or fatal if swallowed. Caution should be used during clean
up operations. The MSDS for the spilled material should be consulted to ensure
personnel safety during cleanup operations.
E. Equipment and Supplies
1. Absorbent pads and booms
2. Hand equipment (shovels, brooms)
3. Waste containers (5 gallon buckets, drums)
4. Personal Protective Equipment
F. Procedural Steps
1. Shut down all equipment operating in the area to prevent ignition of the
spill.
2. Contact the Responsible Person on site to enact the emergency response
contact procedure.
a. The Responsible Person begins contacting Emergency Response
Agencies.
1. For gasoline or diesel spill call 911 for fire control
b. Responsible Person shall consult the MSDS for proper spill
procedures and determination of Reportable Quantity for a spill.
In the event the spilled quantity exceeds the reportable quantity
the Responsible Person shall contact:
1. Call 911 for fire control if necessary.
2. Colorado Environmental Release and Incident Reporting
Hotline (1-877-518-5608)
3. Fort Collins: (970) 416-2740
c. A release of any chemical, oil, petroleum product, sewage, etc.,
which may enter waters of the State of Colorado (which include
surface water, ground water, and dry gullies or storm sewers
leading to surface water) must be reported to CDPHE
immediately (25-8-601 CRS).
3. Attempt to control the spill by stopping or securing the spill source. This
could be as simple as up-righting a tipped container or shutting down a
piece of equipment producing the spill.
4. Prevent migration of the spill by using an absorbent. This could include
absorbent pads or booms, floor dry, cat litter, or dirt. The absorbent
should be spread across the spill and along the downhill side to stop any
flow.
5. If necessary to prevent the material from entering a storm inlet or manhole
a dam of absorbent material should be placed in the gutter upstream from
the inlet.
6. Begin cleanup of the spilled material and absorbents by placing the
materials in 5 gallon, plastic buckets with lids or into a provided drum.
7. Continue cleanup until all spilled material and contaminated absorbents
are removed. On a hard surface, this should include sweeping of the
area. Material spilled on dirt should be removed down to a level where
discoloration of the soil has been removed. Water shall never be used to
flush material off a surface.
8. All material shall be properly stored in a location designated by the
Responsible Person on site.
9. The Responsible Person shall contact the Site Contracted Emergency
Response and Disposal Co. to collect and properly dispose of the
material.
10. Location of the spill will be documented on the Stormwater Maintenance
Plan (SWMP) in the construction trailer.
11. Inspection of materials and equipment shall occur daily.
G. Record Management
All documentation from the incident, including incident report and incident
disposal manifests, shall be maintained at NexMetro Communities. 5601 Old E
Wadsworth Blvd, Suite 220, Arvada, CO 800002, for a period of 3 years from the
date of the spill.
H. After Incident Briefing
All personnel involved in the incident shall attend a debriefing to determine the
cause of the spill, procedures followed, and corrective actions to prevent future
spills. All pertinent data will be recorded. The CDPHE shall be notified of a major
spill by a written follow up within five days of the incident. All findings from the
debriefing should be discussed at the next Safety Meeting. Fort Collins shall be
notified. Fort Collins will require one copy of any documents that are sent to the
state.
Standard Operating Procedure (SOP)
Significant Fuel or Oil Spill (25 Gallons or More)
A. Purpose
The purpose of this Standard Operating Procedure is to establish a uniform
procedure for clean up and disposal of material from a significant accidental spill
of fuel (gasoline or diesel) or oil (hydraulic or motor). The procedures outlined in
this SOP are applicable to all personnel working on site. Clean up and proper
disposal of spilled fuel or oil into the soil or onto the ground surface is required to
ensure the material or contaminated soil does not enter or impact the waters of
the state or the sanitary sewer system.
B. Summary of the Method
This procedure outlines the steps to be taken to prevent spilled fuel or oil from
impacting waters of the state and disposal of the resulting contaminated cleanup
material.
C. Definitions
1. Material Safety Data Sheet (MSDS). The standard industry list for a
product detailing the chemical make-up, safety hazards, first aid, fire
fighting, and spill cleanup measures, handling, storage, and disposal
methods
D. Health and Safety Warnings
Fuels and fuel oils may be extremely flammable, cause skin and eye irritation,
and may be harmful or fatal if swallowed. Caution should be used during clean
up operations. The MSDS for the spilled material should be consulted to ensure
personnel safety during cleanup operations.
E. Equipment and Supplies
1. Absorbent pads and booms
2. Hand equipment (shovels, brooms)
3. Waste containers (5 gallon buckets, drums)
4. Personal Protective Equipment
F. Procedural Steps
1. Shut down all equipment operating in the area to prevent ignition of the
spill.
2. Ensure the safety of personnel in the area. If necessary, evacuate the
area and wait for Emergency Response Personnel.
3. Contact the Chain of Command on site to enact the emergency response
contact procedure.
a. Responsible Person begins contacting Emergency Response
Agencies.
1. Call 911 for fire control
2. Colorado Environmental Release and Incident Reporting
Hotline (1-877-518-5608)
3. Fort Collins: (970) 416-2740
b. Responsible Person consults the MSDS for spill procedure
4. If it can be safely accomplished, attempt to control the spill by stopping or
securing the spill source.
5. If it can be safely accomplished, attempt to prevent migration of the spill
by using an absorbent. This could include absorbent pads or booms, floor
dry, cat litter, or dirt. The absorbent should be spread along the downhill
side to stop any flow.
6. If it can be safely accomplished, attempt to prevent the material from
entering a storm inlet or manhole by constructing a dam of absorbent
material in the gutter upstream from the inlet.
7. Emergency Response Personnel should handle stabilization of the spill
and initial cleanup.
8. Final cleanup and disposal of contaminated material should be handled by
the Site Contracted Emergency Response and Disposal Co.
9. Location of the spill will be documented on the Stormwater Maintenance
Plan (SWMP) in the construction trailer.
10. Inspection of materials and equipment shall occur daily.
G. Record Management
All documentation from the incident, including incident report and incident
disposal manifests, shall be maintained at NexMetro Communities. 5601 Old E
Wadsworth Blvd, Suite 220, Arvada, CO 800002, for a period of 3 years from the
date of the spill.
H. After Incident Briefing
All personnel involved in the incident shall attend a debriefing to determine the
cause of the spill, procedures followed, and corrective actions to prevent future
spills. All pertinent data will be recorded. The CDPHE shall be notified of a major
spill by a written follow up within five days of the incident. All findings from the
debriefing should be discussed at the next Safety Meeting. Fort Collins shall be
notified. Fort Collins will require one copy of any documents that are sent to the
state.
APPENDIX D – Erosion Control Plan
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®
1120 Lincoln Street, Suite 1000
Denver, Colorado 80203
P: 303.623.6300 F: 303.623.6311
HarrisKocherSmith.com
ISSUE DATE:
DATE REVISION COMMENTS
PROJECT #:20101304-08-2024
ENCLAVE AT REDWOOD
SITUATED IN THE SOUTHEAST QUARTER OF SECTION 1, TOWNSHIP 7 NORTH,
RANGE 69 WEST OF THE SIXTH PRINCIPAL MERIDIAN
CITY OF FORT COLLINS, COUNTY OF LARIMER, STATE OF COLORADO.
TEMPORARY EROSION AND SEDIMENT
CONTROL PLANS
SCALE: 1" =
VICINITY MAP
900'
1120 Lincoln Street, Suite 1000
Denver, Colorado 80203
P: 303.623.6300 F: 303.623.6311
HarrisKocherSmith.com
SEQUENCING CHART
BEST MANAGEMENT
PRACTRICES (BMPs)MOBILIZATION DEMOLITION GRADING IMPORT/EXPORT
OF MATERIALS
UTILITIES
INSTALLATION
FLAT WORK
INSTALLATION
VERTICAL
INSTALLATION LANDSCAPE DEMOBILIZATION FINAL
STABILIZATION
STRUCTURAL "INSTALLATION"
SILT FENCE X X X X X X X
CONCRETE WASHOUT
AREA X X X X X
CONSTRUCTION FENCE X X X X X X X X X
INLET PROTECTION ANY EXISTING INLETS THAT COULD USE PROTECTING X X X X
ROCK SOCKS X X X X X X X X
STABILIZED STAGING
AREA X X X X X X
STOCKPILE PROTECTION X X X X X X
VEGETATIVE
TEMPORARY SEEDING
AND MULCHING ANY TIME THE SITE WILL SIT DORMANT LONGER THAN 30 DAYS
PERMANENT SEEDING
AND MULCHING X X X
ABBREVIATIONS
AC ACRE
AVE AVENUE
BLDG BUILDING
BLVD BOULEVARD
C&G CURB & GUTTER
CO CLEANOUT
DIA DIAMETER
E EAST, EASTING
EL ELEVATION
ESMT EASEMENT
EX EXISTING
FF FINISHED FLOOR
FG FINISHED GRADE
FH FIRE HYDRANT
FLOW LINE
FT FEET
MH MANHOLE
MIN MINIMUM
N NORTH, NORTHING
PROPERTY LINE
ROW RIGHT-OF-WAY
S SOUTH
SAN SANITARY
SF SQUARE FOOT, SINGLE FAMILY
TYP TYPICAL
UG UNDERGROUND
Sheet List Table
Sheet Number Sheet Title
1 COVER
2 NOTES
3 TESC PLAN - PHASE 1
4 TESC PLAN - PHASE 2
5 TESC PLAN - PHASE 3
6 TESC PLAN - PHASE 4
7 DETAILS
7 DETAILS
9 DETAILS
10 DETAILS
CALCULATIONS CHART
TOTAL DISTURBED AREA 32.96 ACRES
TOTAL "ONSITE" AREA OF DISTURBANCE 28.37 ACRES
TOTAL "OFFSITE" AREA OF DISTURBANCE 4.59 ACRES
TOTAL STORAGE/STAGING AREA 19.14 ACRES
TOTAL HAUL ROADS AREA
CONSTRUCTION VEHICLE TRAFFIC AREA
EST. PERCENT OF PROJECT AREA
EXPOSED N/A
EST. PERCENT VEGETATIVE COVER 98%DENSITY
EXISTING SOIL TYPE
LOVELAND CLAY
LOAM, NUNN CLAY
LOAM, AND NUNN
CLAY LOAM (WET)
GROUNDWATER DEPTH 7-17 FEET
NUMBER OF PHASES W/ PROJECT 1
TOTAL VOLUME OF IMPORTED (+) /
EXPORTED (-) MATERIALS 0 CUBIC YDS.
TOTAL AREA OF STOCKPILLING OR FILL OR
BORROW AREAS OFF SITE 0 ACRES
STEEPEST SLOPE 3:1 H:V
DISTANCE FROM A RIPARIAN AREA OR
SENSITIVE AREA 10 FEET
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SHEET NUMBER
ISSUE DATE:
DATE REVISION COMMENTS
DESIGNED BY:
CHECKED BY:
DRAWN BY:
PROJECT #:
1120 Lincoln Street, Suite 1000
Denver, Colorado 80203
P: 303.623.6300 F: 303.623.6311
HarrisKocherSmith.com
Know what's below.
Call before you dig.
®
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04-08-2024
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ISSUE DATE:
DATE REVISION COMMENTS
DESIGNED BY:
CHECKED BY:
DRAWN BY:
PROJECT #:
1120 Lincoln Street, Suite 1000
Denver, Colorado 80203
P: 303.623.6300 F: 303.623.6311
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ISSUE DATE:
DATE REVISION COMMENTS
DESIGNED BY:
CHECKED BY:
DRAWN BY:
PROJECT #:
1120 Lincoln Street, Suite 1000
Denver, Colorado 80203
P: 303.623.6300 F: 303.623.6311
HarrisKocherSmith.com
Know what's below.
Call before you dig.
®
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ENCLAVE AT REDWOOD
TESC PLAN - PHASE 2 EC4
196 OF 203
04-08-2024
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SHEET NUMBER
ISSUE DATE:
DATE REVISION COMMENTS
DESIGNED BY:
CHECKED BY:
DRAWN BY:
PROJECT #:
1120 Lincoln Street, Suite 1000
Denver, Colorado 80203
P: 303.623.6300 F: 303.623.6311
HarrisKocherSmith.com
Know what's below.
Call before you dig.
®
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201013
ENCLAVE AT REDWOOD
TESC PLAN - PHASE 3 EC5
197 OF 203
04-08-2024
MJS
RCP
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SCALE: 1" =
100 100 200
100'
SHEET NUMBER
ISSUE DATE:
DATE REVISION COMMENTS
DESIGNED BY:
CHECKED BY:
DRAWN BY:
PROJECT #:
1120 Lincoln Street, Suite 1000
Denver, Colorado 80203
P: 303.623.6300 F: 303.623.6311
HarrisKocherSmith.com
Know what's below.
Call before you dig.
®
FI
L
E
P
A
T
H
:
P
:
\
2
0
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201013
ENCLAVE AT REDWOOD
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198 OF 203
04-08-2024
MJS
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MJS
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54450
PA
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C.
RAC H E L
SHEET NUMBER
ISSUE DATE:
DATE REVISION COMMENTS
DESIGNED BY:
CHECKED BY:
DRAWN BY:
PROJECT #:
1120 Lincoln Street, Suite 1000
Denver, Colorado 80203
P: 303.623.6300 F: 303.623.6311
HarrisKocherSmith.com
Know what's below.
Call before you dig.
®
FI
L
E
P
A
T
H
:
P
:
\
2
0
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201013
ENCLAVE AT REDWOOD
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199 OF 203
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CLH
RCP
CLH
NO
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CO L O R A D O LICEN
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D
54450
PA
T
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O
N
C.
RAC H E L
SHEET NUMBER
ISSUE DATE:
DATE REVISION COMMENTS
DESIGNED BY:
CHECKED BY:
DRAWN BY:
PROJECT #:
1120 Lincoln Street, Suite 1000
Denver, Colorado 80203
P: 303.623.6300 F: 303.623.6311
HarrisKocherSmith.com
Know what's below.
Call before you dig.
®
FI
L
E
P
A
T
H
:
P
:
\
2
0
2
0
\
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201013
ENCLAVE AT REDWOOD
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CLH
RCP
CLH
NO
C
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A
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54450
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RAC H E L
SHEET NUMBER
ISSUE DATE:
DATE REVISION COMMENTS
DESIGNED BY:
CHECKED BY:
DRAWN BY:
PROJECT #:
1120 Lincoln Street, Suite 1000
Denver, Colorado 80203
P: 303.623.6300 F: 303.623.6311
HarrisKocherSmith.com
Know what's below.
Call before you dig.
®
FI
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201013
ENCLAVE AT REDWOOD
TESC - DETAILS EC9
201 OF 203
04-08-2024
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CO L O R A D O LICEN
S
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D
54450
PA
T
T
O
N
C.
RAC H E L
SHEET NUMBER
ISSUE DATE:
DATE REVISION COMMENTS
DESIGNED BY:
CHECKED BY:
DRAWN BY:
PROJECT #:
1120 Lincoln Street, Suite 1000
Denver, Colorado 80203
P: 303.623.6300 F: 303.623.6311
HarrisKocherSmith.com
Know what's below.
Call before you dig.
®
FI
L
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P
A
T
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:
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201013
ENCLAVE AT REDWOOD
TESC - DETAILS EC10
202 OF 203
04-08-2024
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CO L O R A D O LICEN
S
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D
54450
PA
T
T
O
N
C.
RAC H E L
SHEET NUMBER
ISSUE DATE:
DATE REVISION COMMENTS
DESIGNED BY:
CHECKED BY:
DRAWN BY:
PROJECT #:
1120 Lincoln Street, Suite 1000
Denver, Colorado 80203
P: 303.623.6300 F: 303.623.6311
HarrisKocherSmith.com
Know what's below.
Call before you dig.
®
FI
L
E
P
A
T
H
:
P
:
\
2
0
2
0
\
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201013
ENCLAVE AT REDWOOD
TESC - DETAILS EC11
203 OF 203
04-08-2024
CLH
RCP
CLH
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A
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P
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F
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CO L O R A D O LICEN
S
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D
54450
PA
T
T
O
N
C.
RAC H E L