HomeMy WebLinkAbout3.9.4 OXY CC SWMP Rev 12-2013STORMWATER MANAGEMENT PLAN
FOR CONSTRUCTION ACTIVITIES
Cascade Creek Common Plan of Development
Garfield County, Colorado
Prepared For:
Nikirp,/
OXY USA WTP LP
760 Horizon Drive, Suite 101
Grand Junction, Colorado 81506
Prepared by:
OLSSON
ASSOCIATES
Olsson Associates
760 Horizon Drive, Suite 102
Grand Junction, Colorado 81506
Project # 011-2824
Cascade Creek CPD SWMP in effect as of March 2009
Revision: Dec 2013
Administrative Log
Cascade Creek Common Plan of Development
OXY USA WTP LP
Date:
Editor:
Edited Section
and Page No:
Change (s) to Stormwater
Management Plan:
3/30/2010
Olsson
3.0a
Update to legal and local contacts.
4/8/2010
Olsson
1.0
Combining permits.
5/21/2010
Olsson
3.0a
Update to administrator, legal and
local contact.
7/2010
Olsson
3.0a
Update to stormwater
administrator.
12/13/2010
Stormwater Administrator
(C.Gudorf)
Throughout
Updates to SWMP.
4/20/2011
Stormwater Administrator
(C.Gudorf)
Sections: 1.0,
2.0, 3.0, 5.0
Updates to SWMP.
5/2/2011
Stormwater Administrator
(C.Gudorf)
Sections: 1.0,
2.0, 3.0, 5.0
Updates to SWMP.
06/06/2011
Stormwater Administrator
(C.Gudorf)
Table 3-7
06/28/2011
Stormwater Administrator
(C.Gudorf)
Pg. 2, 3, 24, 26,
30
Changes per Doug Weaver
10/062011
Stormwater Administrator
(C.Gudorf)
Site Maps in
Section 2.0;
Appendix A;
5.0.8; 1.0b
Stormwater Site Maps; update to
construction site boundary;
CDPHE Modification form
construction site boundary; update
to SPCC inspection schedule;
update to access roads.
10/21/2011
Stormwater Administrator
(C.Gudorf)
Site Maps in
Section 2.0;
Table 3 and
Table 5.
Updated site map to include new
pipelines, updated table 3 and 5 to
include new pipelines.
12/19/2011
Stormwater Administrator
JC.Gudorf)
Site Maps in
Section 2.0;
Updated site map to include new
pipelines and well pads
2/29/2012
Stormwater Administrator
(C.Gudorf)
Tables 3, 4 & 5
Updated vegetation and receiving
waters
3/6/2012
Stormwater Administrator
(C.Gudorf)
Tables 3 & 4
Updated vegetation and receiving
waters
5/21/2012
Olsson
Section 1.c
Section 2.0
Tables 3, 5, 6
Removed Logan Wash Rd (/Trail
Ridge Rd) from SWMP (Rec
Waters Table, Veg Table, Seed
Mixes, overall site maps); updated
disturbed acreage.
6-2013
Olsson
All
SWMP updated/ re -written into
new template, new overview maps
12-2013
Olsson
1.A, 1.C, Project
Site Overview
Map, NRCS
Soils Units Map
Disturbed acreage and overview
maps updated to reflect sites
added back into inspections after
damage from July storm.
OXY USA WTP LP, Certification
Stormwater Management Plan for
Cascade Creek Common Plan of Development
Garfield County, Colorado
Olsson Associates has prepared this Stormwater Management Plan for Construction Activities
for OXY USA WTP LP for the Cascade Creek Common Plan of Development located in
unincorporated Garfield County, Colorado.
"I certify under penalty of law, that this document and all attachments were prepared under my
direction or supervision in accordance with a system designed to assure that qualified personnel
properly gather and evaluate the information submitted. Based on my inquiry of the person or
persons who manage the system, or those persons directly responsible for gathering the
information, the information submitted is, to the best of my knowledge and belief, true, accurate,
and complete. I am aware that there are significant penalties for submitting false information,
including the possibility of fine and imprisonment for knowing violations."
Signature:
Name: Chris Clark
Title: Operations Manager
Date:
TABLE OF CONTENTS
INTRODUCTION 1
Stormwater Runoff Permitting Requirements 1
Project Description 1
1. CONSTRUCTION SITE DESCRIPTION 2
1.A Nature of Construction Activity 2
1.6 Sequence of Construction Activities 2
1.0 Estimate of Total Area of Site and Area to be Disturbed 5
1.D Soil Data and Erosion Potential 5
1.E Vegetation Description and Estimate 6
1.F Potential Pollution Sources and Locations 7
1.G Non-Stormwater Discharges 7
1.H Receiving Waters 7
2. SITE MAP(S) 7
2. A Construction Site Boundaries 7
2. B Areas of Ground Disturbance 7
2. C Areas of Cut and Fill 7
2. D Storage Areas 7
2. E Location of Asphalt and Concrete Batch Plants 7
2. F Locations of Structural BMPs 7
2. G Locations of Non -Structural BMPs 7
2. H Locations of Springs, Streams, Wetlands and Other Surface Waters 7
3. STORMWATER MANAGEMENT CONTROLS 8
3.A Stormwater Administrator 8
3.B Potential Pollutant Sources 8
3.0 BMPs for Stormwater Pollution Prevention 9
3.C.1 Structural Practices for Erosion and Sediment Control 9
3.C.2 Non -Structural Practices for Erosion and Sediment Control 9
3.C.3 Phased BMP Installation 9
3.C.4 Materials Handling and Spill Prevention 10
3.C.5 Dedicated Asphalt or Concrete Batch Plants 11
3.C.6 Vehicle Tracking 11
3.C.7 Waste Management and Disposal, Concrete Washout, and Contaminated Soils 12
3.C.8 Ground Water and Stormwater Dewatering 12
4. FINAL STABILIZATION AND LONG TERM STORMWATER MANAGEMENT 12
5. INSPECTIONS AND MAINTENANCE PROCEDURES 13
OXY USA WTP LP i Olsson Associates
Cascade Creek SWMP
LIST OF TABLES
Table 1
Table 2
Table 3
Table 1-1
Table 3-1
Vegetation Descriptions
Typical Seed Mixture
Down -Hole Chemicals/MSDS Inventory
Soils Data and Erosion Potential
BMP Phasing
LIST OF FIGURES
Figure 1 Project Site Overview (/Receiving Waters) Map
LIST OF APPENDICES
Appendix A Certification: COR -038414, General Permit: COR -030000, and Related Docs
Appendix B NRCS Soil Unit Map & Soil Descriptions
Appendix C Inspection Report Form and Example Site Map
Appendix D Best Management Practice (BMP) Manual
Appendix E BLM Gold Book, Chapters 4 and 6
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Cascade Creek SWMP
INTRODUCTION
This Stormwater Management Plan (SWMP) for Construction Activities is written to comply with
the Colorado Department of Public Health and Environment (CDPHE)'s General Permit No.
COR -030000, issued on July 1, 2007 and administratively continued on June 30, 2012 to
remain in effect until the new permit being developed by the Water Quality Control Division is
issued and effective, and with related U.S. Environmental Protection Agency (USEPA) National
Pollutant Discharge Elimination System (NPDES) stormwater regulations. This SWMP
addresses construction activities associated with OXY USA WTP LP (Oxy)'s oil and gas
exploration and production activities at the Cascade Creek Common Plan of Development
(Cascade Creek), in Garfield County, Colorado. A copy of the certification to discharge (COR -
038414), the Colorado Discharge Permit System (CDPS) general permit (COR -030000), and
related documentation can be found in Appendix A.
This SWMP is intended to be revised as necessary to address planned developments, new
disturbances, and other changes required to manage stormwater and protect surface water
quality. These changes shall be documented in the Administrative Log located at the front of
this document.
Stormwater Runoff Permitting Requirements
The Federal Clean Water Act [Section 402(p)] requires that discharges of pollutants to waters of
the U.S. from any point source be regulated by NPDES permits. In November 1990 the EPA
published final regulations that established application requirements for stormwater associated
with construction activity for soil disturbances of 5 acres or more be regulated as an industrial
activity and covered by an NPDES permit. In December 1999 the EPA published final Phase II
NPDES regulations that established application requirements for stormwater associated with
construction activity for soil disturbances to be regulated as an industrial activity and covered by
an NPDES permit. These regulations became effective July 1, 2002.
On June 30, 2005, Colorado stormwater regulations went into effect to require CDPS permits for
stormwater discharges from construction activities for oil and gas activities (1 acre or greater).
Federal permit coverage for these discharges was conditionally exempted from the Federal
Clean Water Act by the 2005 Federal Energy Bill. On February 1, 2006, the CDPHE issued a
letter clarifying that the CDPHE Water Quality Control Commission decided to maintain the
existing requirements for stormwater permitting for oil and gas construction sites greater than 1
acre.
Project Description
Oxy's Cascade Creek area is located in Garfield County, Colorado, north of the town of De
Beque. The project site is divided into three smaller well fields: Mesa, Valley, and Logan Wash.
The three fields are located within Township 5 through 8 South, Range 96 and 97 West, of the
6th PM. See Figure 1 for an overview map of the project site.
The current drilling and development plan includes well pad, access road, and pipeline
construction, well drilling, well testing, well completion, and installation of associated facilities.
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Cascade Creek SWMP
1. CONSTRUCTION SITE DESCRIPTION
The following section provides a description of the construction activities.
1.A Nature of Construction Activity
Construction at Cascade Creek will be performed using conventional cut and fill earthmoving
techniques and trenching. The total estimated disturbance for all current and planned pads,
pipelines, and access roads is approximately 800 acres. Reserve pits may be constructed for
use during operations to contain drilling fluids and cuttings. The pits will be designed,
constructed, and reclaimed according to COGCC requirements.
In areas that are disturbed by construction, topsoil will be stripped and stockpiled near the site.
All brush, limbs, and other woody material will be stockpiled separately from the topsoil. Soil
materials will be managed so that erosion and sediment transport are minimized. Nearby
drainages will be protected by appropriate measures.
If a well is not productive, it will be plugged and abandoned in accordance with COGCC rules
and the pad area will be reclaimed to approximate pre -construction contours and seeded.
Construction and reclamation activities will also be completed, if and where appropriate, in
accordance with BLM Gold Book Chapters 4 and 6, which are included as Appendix E.
1.B Sequence of Construction Activities
The development of a natural gas well is generally accomplished in six work phases. They
include: access road and pad construction, well drilling, well completion, production, interim
reclamation, and final reclamation. Each work phase is briefly discussed below and the BMPs
are discussed in Section 3.C.
Access road and pad construction
Pad and access road construction will be performed using traditional cut and fill construction.
Blasting is also used in some areas. Size and maintenance requirements for each access road
are based on road location and traffic level. Reserve pits may be constructed on the pads at
this time to store certain fluids and solids during drilling and completion operations. No fluids or
solids, excluding any accumulated stormwater, will be stored in the reserve pits during this
phase.
Basic construction activities that are conducted during this phase include clearing and grubbing,
segregation of topsoil for use in reclamation, grading and excavation, compaction, final grading
and contouring, and installation of surfacing materials such as gravel. To the extent possible,
BMPs that will be utilized to control stormwater throughout the life of the facility will be
constructed during this phase.
Sediment discharge is the main potential pollutant of concern during access road and pad
construction. No chemicals or fuels will be stored on site during this phase; however, attention
will be paid to the potential for leaks that might occur during the use of construction equipment.
Well drilling
The well drilling phase includes the drilling of one or more wells at each location. Activities
associated with the drilling phase may include:
Mobilization of the drilling rig and associated equipment, including generators and
drilling -mud handling equipment. In some instances a smaller drilling rig may be used to
drill the initial stages of each well prior to the larger drilling rig mobilizing to the location
Installation of storage, office and housing trailers
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Cascade Creek SWMP
Storage of down hole chemicals, fuels and lubricants
Installation of potable water tanks and sewage -handling equipment (e.g., portable toilets
or sewage vaults)
Well drilling activities including the installation and cementing of well casing
Demobilization of the drilling rig and all other equipment at the completion of this phase
Drilling mud and water will be used to maintain appropriate down hole pressures and lubrication.
Unused fresh water and mud chemicals will be stored on the pad. Used materials will be
discharged to the reserve pit, or captured in tanks during closed-loop drilling processes.
Petroleum products are used for the duration of the drilling process to fuel or lubricate
equipment and include: fuel, gear oil, hydraulic oil, brake fluid, and grease. Materials to be used
to cement casing placed in the well may also be stored and prepared on location or may be
transported to the site.
Sediment discharge, unused mud chemicals and/or well casing materials, used drilling
water/mud, and petroleum products are potential pollutants of concern during this phase of
construction.
Procedures will also be implemented for prompt containment and remediation of any spills that
may occur during the drilling phase. These procedures are outlined in Oxy's Cascade Creek
Spill Prevention, Control and Countermeasures (SPCC) plan.
As equipment is demobilized at the completion of this phase, the well pad and surrounding
areas will be carefully inspected to identify any spills or leaks that may have occurred so that
those areas can be remediated prior to initiation of the well completion phase.
Well completion
The well completion phase may include hydraulic fracturing (fracking), cementing, and other
processes that stimulate the well and prepare it for production. The basic activities that are
conducted during this phase include:
Mobilization of equipment required for well completion
Storage of down hole chemicals, fuels and lubricants
Installation of potable water tanks and sewage -handling equipment (e.g., portable toilets
or sewage vaults) or continued maintenance of such equipment installed during the
drilling phase
Fracking and other well -stimulation processes
Drill out of any plugs placed during well completion with a work -over rig
Flowback of the well to remove frac water, sand and other impurities
Demobilization of equipment when this phase has been completed
Several temporary facilities/structures will be placed on site during this phase. These will
include: frac trucks, storage and office trailers, generators, and frac tanks. During completions,
certain chemicals may be used to stimulate the formation for the extraction of natural gas.
Unused water and chemicals will be stored on the pad. Used water will be stored in the reserve
pit, recycled, or used in other operations.
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Sediment discharge, unused and used chemicals, frac water, and small amounts of equipment
lubricant or fuel are potential pollutants of concern during this phase of construction.
Procedures outlined in the SPCC plan will also be implemented for prompt containment and
remediation of any spills that may occur.
As equipment is demobilized at the completion of this phase, the well pad and surrounding
areas will be carefully inspected to identify any spills or leaks that may have occurred so that
those areas can be remediated prior to initiation of the production phase.
Production
The production phase includes the installation of long-term facilities such as permanent well
heads, storage tanks, oil and natural gas processing equipment, flow measurement equipment,
and any associated flow lines needed to produce gas from the formation. Pipeline installation or
any required maintenance work is generally accomplished by trenching. The area of
disturbance for each pipeline project is determined by location, pipeline size, and the scope of
the work being done.
Sediment discharge, produced fluids, and small amounts of equipment lubricant, fuel, corrosion
inhibitors or other chemicals are potential pollutants of concern during this phase. Procedures
outlined in the SPCC plan will also be implemented for prompt containment and remediation of
any spills that may occur.
Interim reclamation
The interim reclamation phase includes the contouring of the majority of the pad to a smaller
area. The reduced area will be utilized for long-term production and ongoing routine
maintenance of the well(s). In general, this phase includes contouring of the site, spreading of
topsoil on contoured areas and seeding those areas.
Sediment discharge, produced fluids, and small amounts of equipment lubricant, fuel, corrosion
inhibitors or other chemicals are potential pollutants of concern during this phase of
construction. Procedures outlined in the SPCC plan will also be implemented for prompt
containment and remediation of any spills that may occur.
Permit coverage may be inactivated for oil and gas construction sites even if stabilized unpaved
surfaces exist and/or disturbed land that has been restored to cropland remains non -vegetated,
as long as construction activities have been completed and all other disturbed areas are re -
vegetated.
Final reclamation
When the production of a well is exhausted, it will be abandoned. Upon well abandonment each
borehole will be plugged, capped, and all surface equipment will be removed. Subsurface
pipelines will be removed to specified locations or abandoned in place as per COGCC Rule
1103.
The pad area will be reclaimed by contouring disturbed soils to conform to the surrounding
terrain, by redistributing the stockpiled topsoil, seeding of disturbed soil areas in order to
reestablish cover vegetation, and by construction of any permanent erosion and sediment
control structures as needed.
Sediment discharge is the main potential pollutant of concern during this phase. No chemicals
or fuels will be stored on site during this phase; however, attention will be paid to the potential
for leaks that might occur during the use of construction equipment.
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Cascade Creek SWMP
1.0 Estimate of Total Area of Site and Area to be Disturbed
The total project site encompasses approximately 29,800 acres. The total disturbed acreage for
the project is approximately 800 acres. As new sites are added to the project site, or as sites
reach final stabilization and are removed from the permit, the SWMP will be updated to reflect
the changes.
1.D Soil Data and Erosion Potential
Runoff characteristics are based primarily on site topography, soil type, and vegetative cover.
The major soil types for the areas of disturbance are: Biedsaw-Sunup gravelly loams, 10 to 40
percent slopes; Debeque very channery loam, 5 to 20 percent slopes; Grobutte very channery
loam, 30 to 60 percent slopes; Happle very channery sandy loam, 3 to 12 percent slopes;
Happle-Rock outcrop association, 25 to 65 percent slopes; Northwater loam, 15 to 65 percent
slopes; Northwater-Adel complex, 5 to 50 percent slopes; Parachute-Irigul complex, 5 to 30
percent slopes; Parachute-Irigul-Rhone association, 25 to 50 percent slopes; Parachute -Rhone
loams, 5 to 30 percent slopes; Silas loam, 1 to 12 percent slopes; Tosca channery loam, 25 to
80 percent slopes; and Utso-Rock outcrop complex, 40 to 90 percent slopes. The major soil
types are moderately well to well drained soils with a very low to very high (-2.7 inches to -26.7
inches) water holding capacity.
A Natural Resources Conservation Services (NRCS) unit map and soils descriptions for the
dominant soils in the construction areas are provided in Appendix B.
The K -factor approximates soil detachment due to runoff and raindrop impact. Lower k -Factor
values (0.1 - 0.17) indicate Tess susceptibility to sheet and rill erosion, while higher k -Factor
values (>0.30) indicate greater susceptibility to erosion.
The Hydrologic Group describes soil and soil units with the potential for runoff under similar
storm and cover conditions. Group A has a high infiltration rate and a corresponding lower
potential for runoff, while Group D has low infiltration rates due to finer soil texture or a high
water table, giving them a high potential for runoff.
The average annual precipitation for Cascade Creek is approximately 25 to 30 inches (Western
Regional Climate Center map - http://www.wrcc.dri.edu/pcpn/co.gif).
Table 1-1 shows the soils data and erosion potential for each major soil within the areas that will
undergo construction.
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Cascade Creek SWMP
Table 1-1
Soils Data and Erosion Potential
1.E Vegetation Description and Estimate
Existing vegetation surrounding the areas of disturbance includes but is not limited to: grasses,
sagebrush, aspen, serviceberry, and scrub oak. Percent ground cover ranges from 50 to 90
percent. Specific existing vegetation descriptions and percents ground cover for each site are
listed in Table 1.
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Representative Value
Soil Name
Hydrologic Group
K -factor
% Sand
% Silt
% Clay
Biedsaw-Sunup gravelly loams
Biedsaw
C
0.37
39.2
37.3
23.5
Sunup
D
0.37
39.8
37.7
22.5
Debeque very channery loam
Debeque
B
0.28
42.1
37.9
20
Grobutte very channery loam
Grobutte
B
0.28
38.5
36.5
25
Happle very channery sandy loam
Happle
B
0.28
65.1
18.9
16
Happle-Rock outcrop association
Happle
B
0.28
65.1
18.9
16
Rock Outcrop
D
-
-
-
-
Northwater loam
Northwater
B
0.2
39.2
37.3
23.5
Northwater-Adel complex
Northwater
B
0.2
43
38.5
18.5
Adel
B
0.15
35.4
33.6
31
Parachute-Irigul complex
Parachute
B
0.2
42.1
37.9
20
Irigul
D
0.28
39.8
37.7
22.5
Parachute-Irigul-Rhone association
Parachute
B
0.2
42.1
37.9
20
Irigul
D
0.28
39.8
37.7
22.5
Rhone
B
0.2
39.2
37.3
23.5
Parachute -Rhone loams
Parachute
B
0.2
42.1
37.9
20
Rhone
B
0.2
39.2
37.3
23.5
Silas loam
Silas
B
0.2
39.2
37.3
23.5
Tosca channery loam
Tosca
B
0.28
44.3
40.7
15
Utso-Rock outcrop complex
Utso
B
0.28
44.3
40.7
15
Rock Outcrop
D
-
-
-
-
1.E Vegetation Description and Estimate
Existing vegetation surrounding the areas of disturbance includes but is not limited to: grasses,
sagebrush, aspen, serviceberry, and scrub oak. Percent ground cover ranges from 50 to 90
percent. Specific existing vegetation descriptions and percents ground cover for each site are
listed in Table 1.
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1.F Potential Pollution Sources and Locations
The potential pollution sources for each phase of construction are discussed in Sections 1.B
Sequence of Construction Activities and 3.B Potential Pollutant Sources. The locations of the
potential pollution sources are shown on the site maps.
1.G Non-Stormwater Discharges
Non-stormwater discharges are not expected from the construction project.
1.H Receiving Waters
Oxy's Cascade Creek area lies within the Colorado River watershed. The majority of the project
site drains to the southwest via numerous named and unnamed tributaries of Roan Creek. The
north and east edges of the project site drain to numerous named and unnamed tributaries of
Parachute Creek. Roan Creek and Parachute Creek terminate at the Colorado River. Mount
Callahan Road, which is the eastern portion of the Oxy's Logan Wash area, drains partly to
unnamed tributaries of Smith Gulch and Kelly Gulch, which are direct tributaries of the Colorado
River. For more detail, refer to Figure 1, the overview map and/or to the individual site maps.
2. SITE MAP(S)
The site maps for Cascade Creek will be maintained within Oxy's stormwater database. The
maps will be regularly updated to reflect all changes to the sites, and additional maps will be
created in response to planned field activities. An example site map is included in Appendix C.
2. A Construction Site Boundaries
For an accurate representation of the construction site boundaries, refer to the site maps.
2. B Areas of Ground Disturbance
For an accurate representation of the areas of ground disturbance, refer to the site maps.
2. C Areas of Cut and Fill
For an accurate representation of the areas of cut and fill, refer to the site maps.
2. D Storage Areas
For an accurate representation of the storage areas, refer to the site maps.
2. E Location of Asphalt and Concrete Batch Plants
Asphalt or concrete batch plants are not anticipated within the project site, but, if used, will be
included on the site maps.
2. F Locations of Structural BMPs
For an accurate representation of the location of structural BMPs, refer to the site maps.
2. G Locations of Non -Structural BMPs
For an accurate representation of the location of non-structural BMPs, refer to the site maps.
2. H Locations of Springs, Streams, Wetlands and Other Surface Waters
For an accurate representation of the location of springs, streams, wetlands, and other surface
waters, refer to the overview map, Figure 1 and/or to the site maps.
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Cascade Creek SWMP
3. STORMWATER MANAGEMENT CONTROLS
3.A Stormwater Administrator
The SWMP Administrator for Cascade Creek is Oxy's HES Advisor. The SWMP Administrator
is responsible for developing, implementing, maintaining and revising the SWMP as necessary.
The administrator may delegate the SWMP inspections and maintenance of records to qualified
personnel.
3.B Potential Pollutant Sources
Disturbed and stored soils: The construction activities will involve soil disturbances and
stockpiling. Clearing, grading, and otherwise altering previously undisturbed land can greatly
increase the rate of soil erosion over pre -disturbance rates. The resulting sediment can impact
the water quality of receiving streams.
Vehicle tracking of sediments: Vehicles will be accessing the sites up until the Final
Reclamation phase. This also has the potential to facilitate the movement of sediment off site.
Management of contaminated soils: If a spill of any type were to occur, the impacted soil would
become a potential stormwater pollutant.
Loading and unloading operations: The sites may have tanks for the storage of fuels or
production -related liquids. The presence of such tanks would require loading and unloading of
the tanks.
Outdoor storage activities: The construction contractor will maintain a laydown or staging area
for equipment and material storage on site. Depending on the work phase of the site, chemicals
and/or other drilling materials may be stored on site, and tanks used to store fuels or production -
related liquids may be present. These storage activities are discussed in more detail in 1.B
Sequence of Construction Activities. An inventory of down -hole chemicals used for Oxy wells is
included as Table 3.
Vehicle and equipment maintenance and fueling: During construction, it is possible that
equipment will be maintained or fueled on site. On-site maintenance and fueling could
potentially result in leaks or spills of fuel, gear oil, hydraulic oil, brake fluid, or grease.
Significant dust or particulate generating processes: Construction activities and vehicle traffic to
and from the sites could potentially generate dust.
Routine maintenance activities: The use of fertilizers or weed killers is a possible at the sites in
order to achieve successful revegetation of disturbed areas. See also "vehicle and equipment
maintenance and fueling" above.
On-site waste management practices: Trash receptacles will be located on site to contain
construction -related or other trash or debris. Used drilling mud and water will be discharged to
the reserve pit, or captured in tanks during closed-loop drilling processes. Portable toilets may
be utilized on site.
Concrete truck/equipment washing: Concrete truck or equipment washing is not anticipated.
Dedicated asphalt and concrete batch plants: Dedicated asphalt and concrete batch plants are
not anticipated.
Non -industrial waste sources: All project phases involve people working on site. This can
generate personal and work-related trash and debris, and may also necessitate the use of
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portable toilets. Clearing operations may also generate waste in the form of slash (trees, brush,
etc.).
Other areas or procedures: No other areas or procedures where spills can occur are
anticipated at this time.
Spills or leaks from potential sources are described in the SPCC plan. Response to certain
events may require specialized training due to health and safety concerns. The locations of
potential pollutant sources are shown on the site maps. BMPs utilized to address potential
pollutant sources are described in Section 3.
3.0 BMPs for Stormwater Pollution Prevention
This section describes the BMPs that will be used at Cascade Creek for stormwater pollution
prevention. Oxy's BMP Manual containing the BMPs which may be implemented is included in
Appendix D. BMPs may be added or removed from the manual to accommodate changes in
site conditions and activities at Cascade Creek.
Run-on protection and run-off controls will be installed prior to the beginning of construction
activities, as practicable, with consideration given to worker safety and site access. Additional
structural and non-structural Best Management Practices (BMPs) will likely need to be installed
during and following construction.
3.C.1 Structural Practices for Erosion and Sediment Control
Descriptions, design and installation practices, and maintenance and removal considerations for
the structural BMPs available for use can be found in the BMP Manual. The location of all
structural BMPs will be found on the site maps.
3.C.2 Non -Structural Practices for Erosion and Sediment Control
Descriptions, design and installation practices, and maintenance and removal considerations for
the non-structural BMPs available for use can be found in the BMP manual. The location of all
non-structural practices will be found on the site maps.
3.C.3 Phased BMP Installation
The project will be phased to the extent practical to limit the amount of disturbed area that is
exposed at any given time. BMP implementation will be coordinated with the various stages of
construction. BMPs to control erosion and sediment transport will be installed prior to earth
disturbing activities. If additional areas are disturbed, BMPs will be implemented prior to the
start of ground disturbing activities in those areas. As portions of the site are completed and
previously disturbed areas are stabilized or the BMP is no longer needed, they will be removed.
Permanent or temporary erosion control measures for all slopes, channels, ditches, disturbed
land area, and soil stockpiles will be implemented as soon as practicable after final grading or
the final ground disturbance has been completed. When it is not possible to permanently
stabilize a disturbed area after a disturbance has been completed or where significant ground
disturbance activity ceases, temporary erosion control measures will be implemented as soon
as practicable. Table 3-1 below outlines the BMPs to be implemented during each phase of the
project.
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Table 3-1
BMP Phasing
Project Phase
BMPs to be implemented during each phase
Pre-Disturbance/Site Preparation
• Prepare stabilized staging area.
• Install vehicle tracking pad, geotextile, or mud mats
where applicable to provide designated access into
the ROW.
• Installation of perimeter control BMPs
• Limit access to areas that are not to be disturbed
protecting the existing vegetation.
Construction
• Locate stockpiles in work areas with perimeter
BMPs.
• Install BMPs per details in the BMP manual.
• Leave disturbed area of site in a surface
roughened condition when feasible.
• Protect, inspect and repair BMPs as necessary.
Post -construction
• Maintenance and repair of BMPs installed during
previous phases.
• Stabilize surface with gravel when feasible
• Inspection of BMPs
Final Stabilization
• Perform seeding and mulching or the installation of
erosion control blankets where applicable.
• Remove all non -biodegradable temporary BMPs
when applicable.
3.C.4 Materials Handling and Spill Prevention
Spills or leaks from potential pollution sources will be handled as described in Oxy's SPCC plan.
Petroleum Product Management
Pollutants from petroleum products used during construction activities adhere easily to soil
particles and other surfaces. In the case of a spill or leak, soils contaminated with petroleum
products will be contained, and remediated onsite or removed to a proper disposal site.
Use of secondary containment will reduce the risk of spills or leaks contacting the ground,
including during loading and unloading operations. The use of drip pans will reduce the
likelihood of spills or leaks contacting the ground during vehicle or equipment maintenance or
fueling. Proposed soil erosion and sediment control practices will also aid in the retention of
spills or leaks.
Proposed maintenance and safe storage practices will reduce the chance of petroleum products
contaminating the site. Oily wastes such as crankcase oil, cans, rags, and paper containing oils
will be placed in proper receptacles and disposed of or recycled. Routine daily inspections will
be conducted to identify leaks form equipment and vehicles and if needed corrective actions will
be implemented.
The following guidelines for storing and managing petroleum products will be implemented:
• All product containers will be clearly labeled
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Drums (if present) will be kept off the ground, within secondary containment. Lids for
drummed materials will be securely fastened.
Fuel tanks will be stored within secondary containment
Emergency spill response procedures will be available on site. Persons trained in
handling spills will be on call at all times
Spill response equipment and materials (absorbent, shovels, etc.) will be easily
accessible. Spills will be immediately cleaned up and contaminated materials will be
properly stored on site until they can be disposed of in accordance with applicable
regulations
Storage areas and containers will be regularly monitored for leaks and repaired or
replaced as necessary. Contractors and subcontractors should be reminded about
proper storage, handling and transferring of petroleum products or other hazardous
materials during safety meetings.
Other Material/Chemical Product Management
Any other chemicals or materials stored on site that could contribute pollutants to runoff will be
kept off the ground, and stored in original packaging and/or otherwise covered, to ensure that
the material does not interact with stormwater. Storage or laydown areas will be maintained
with good housekeeping, and regularly inspected for spills, leaks, and the potential of materials
commingling with stormwater. Any minor spills or leaks will be cleaned up immediately.
Spill Response
All spills and releases of exploration and production waste or produced fluid exceeding 5 barrels
(210 gallons) including those contained within unlined berms, shall be reported in writing on the
COGCC Spill/Release Report Form 19 within 10 days of discovery of the spill.
All spills/releases that exceed 20 barrels (840 gallons) of exploration and production
liquids/waste shall be verbally reported to the COGCC at (303) 894-2100 within 24 hours of
discovery.
Spills or releases of any size that impact or threaten to impact any waters of the state, residence
or occupied structure, livestock or public byway, shall be verbally reported to the COGCC as
soon as practical after discovery (COGCC Rule 906). If the spill may potentially reach waters of
the state (which includes surface water, ground water and dry gullies or storm sewers leading to
surface water), it must also be reported immediately to the CDPHE at 1-877-518-5608.
Spills or releases of more than 25 gallons of refined petroleum crude oil products such as
gasoline, diesel fuel, oil, or derivatives of mineral, animal or vegetable oil shall be reported to
the CDPHE at 1-877-518-5608, within 24 hours.
A hazardous substance release in any amount which enters or threatens to enter waters of the
state shall be reported to the CDPHE.
3.C.5 Dedicated Asphalt or Concrete Batch Plants
Dedicated asphalt or concrete batch plants are not anticipated within the project site.
3.C.6 Vehicle Tracking
In order to limit vehicle tracking of sediment, vehicles will use designated entry points into
construction areas. Access roads and drive paths on pads will be sloped and maintained such
that stormwater exits quickly, limiting the potential for excessive mud and rutting. Stabilization
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methods, such as road base and chemical stabilizers and stabilized construction entrances will
be used where practicable. The location of vehicle tracking controls will be shown on the site
map.
3.C.7 Waste Management and Disposal, Concrete Washout, and Contaminated Soils
Waste Management and Disposal
Construction -related and other trash will be collected in covered containers and hauled off-site
for disposal in suitable landfills. Used drilling water and mud will be remediated or disposed of
in accordance with COGCC rules. Portable toilets may be used to contain sanitary waste, with
waste materials regularly pumped and transported off-site for disposal at approved facilities. If
portable toilets are used, they will be staked or weighted to prevent tipping. Any slash from
clearing activities will, if possible, be chipped and used on site for mulch, or utilized as a brush
barrier at the site perimeter. The locations of any waste containments on site are shown on the
site maps.
Concrete Washout
Concrete washout is not anticipated within the project site.
3.C.8 Ground Water and Stormwater Dewatering
No groundwater dewatering is anticipated at this time. If groundwater is encountered, the
dewatering of the site will be regulated by a dewatering permit issued through CDPHE. All
stormwater will be diverted by berms and/or diversion ditches to avoid contact with the
groundwater.
If the need for stormwater dewatering is encountered, appropriate erosion and sediment control
BMPs, as described in the BMP manual, will be utilized to minimize erosion and trap sediment.
4. FINAL STABILIZATION AND LONG TERM STORMWATER MANAGEMENT
A site is considered finally stabilized when all ground surface disturbing activities at the site
have been completed, and all disturbed areas have been either built on, compacted, covered,
paved, or otherwise stabilized in such a way as to minimize erosion to the extent practicable, or
a uniform vegetative cover has been established that reflects a total percent plant cover of at
least seventy percent (70%) of pre -disturbance levels or reference areas.
The approved seed mix and application rates for Cascade Creek are presented in Table 2.
Specific BMPs for soil preparation and amendment, soil stabilization, and sediment control
during final stabilization will be chosen on a site by site basis, based on soil condition and slope.
The BMPs chosen will be shown on the individual site maps.
Sites are considered finally stabilized once site preparation and interim reclamation (COGCC
Rule 1003) are complete and the above stabilization criteria have been met, even though the
site will be disturbed again in the future for final reclamation.
Once stabilized, the site will be removed from this SWMP for sediment controls. However, if
petroleum hydrocarbons or other chemicals affect stormwater as a result of industrial activities
on-site, the site will maintain permit coverage. Permanent BMPs may be left in place if it is
deemed necessary to maintain site stability.
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5. INSPECTIONS AND MAINTENANCE PROCEDURES
Site inspections will be conducted with the requirements and minimum schedule as outlined in
Part I.D.6 of the CDPS general permit (COR -030000). The requirements are as follows:
All active construction sites will be inspected at a minimum of at least once every 14
calendar days, and within 24 hours after the end of any precipitation or snowmelt event
that causes surface erosion.
If a site is considered temporarily idle, that is, no construction activities will occur
following a storm event, than a post -storm inspection will be conducted prior to re-
commencing constructing activities, but no later than 72 hours following the storm event.
Routine inspections must still be conducted at least every 14 calendar days.
For sites or portions of sites in which all construction activities that will result in ground
disturbance are completed, and all activities for final stabilization, as outlined above in
section 4, with the exception of vegetative coverage are completed, inspections will be
conducted at least once every month, and post -storm inspections are not required.
Inspections are not required at sites where snow cover exists over the entire site for an
extended period of time as long as melting conditions do not exist. The following
information must be documented in the inspection record for the use of this exclusion:
dates when snow cover occurred, date when construction activities ceased, and date
melting conditions began.
A trained and qualified person familiar with the SWMP and stormwater controls will conduct all
inspections. The scope of the inspection will cover the construction site perimeter, all disturbed
areas, material and/or waste storage areas that are exposed to precipitation, discharge
locations, and locations where vehicles access the site. These areas will be inspected for
evidence of, or the potential for, pollutants leaving the construction site boundaries entering the
stormwater drainage system, or discharging to waters of the state. Also, all erosion and
sediment control practices identified in this SWMP will be evaluated to ensure that they are
maintained and operating correctly.
Personnel performing site inspections will record the information as outlined below on the
inspection report. This inspection report will identify any incidents of non-compliance with the
terms and conditions of the general permit. The inspection report will include:
i. The inspection date
ii. Name(s) and title(s) of personnel making the inspection
iii. Location(s) of discharges of sediment or other pollutants from the site
iv. Location(s) of BMPs that need to be maintained
v. Location(s) of BMPs that failed to operate as designed or proved inadequate for a
particular location
vi. Location(s) where additional BMPs are needed that were not in place at the time of
inspection
vii. Deviations from the minimum inspection schedule as outlined above
viii. Description of corrective action for items iii, iv, v, and vi, above, dates corrective
action(s) taken, and measures taken to prevent future violations, including requisite
changes to the SWMP, as necessary
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ix. After adequate corrective action(s) have been taken, or where a report does not identify
any incidents requiring corrective action(s), 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.
If deficiencies or maintenance issues are noted on the inspection form, or additional BMPs are
needed, then the Stormwater Administrator for Oxy will be contacted and they will direct a
subcontractor to perform the proper actions.
BMPs that have failed, or have the potential to fail without maintenance or modification, will be
addressed as soon as possible, immediately in many cases, to prevent the discharge of
pollutants. All BMPs will be adequately maintained in accordance with good engineering,
hydrologic and pollution control practices, including removal of collected sediment outside the
acceptable tolerances of the BMPs.
All inspection records will be kept and maintained in Oxy's stormwater database for a minimum
of three years from expiration or inactivation of permit coverage. An example report is included
in Appendix C.
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Tables
Figures
Appendix A
Certification, General Permit, and Related Documents
Site Termination Forms
Appendix B
NRCS Soil Unit Map
Soil Descriptions
Appendix C
Inspection Report Form
Example Site Map
Appendix D
BMP Manual
Appendix E
BLM Gold Book, Chapters 4 and 6