HomeMy WebLinkAbout20191743.tiffWATER SUPPLY INFORMATION SUMMARY
Section 30-28.133,(d), C.R.S. requires that the applicant submit to the County,'Adequate evidence that a water supply that
is sufficient in terms of quantity, quality and dap$ndabiiity will be available to ensure an adaquate supply of water.
1. NAME OF DEVELOPMENT AS PROPOSED
Hookside
Compressor Station and
Gas Processing Plant
2. LAND USE ACTION Construction of a compressor station and
gas processing plant.
3. NAME OF EXISTING PARCEL AS RECORDED GABEL CATTLE LLC 3288 S2 30 9 60 EXC MIN (2L6R) 046730000002
SUBDIVISION NA
HUNG
N.A BLOCK
N/A
LOT N/A
4. TOTAL ACREAGE 162
5. NUMBER OF LOTS PROPOSED N/A PLAT MAP ENCLOSED S YES
E. PARCEL HISTORY - Please attach copies of deeds. fists et ether evidence or documentation.
A. Was parcel recorded with county prior to June 1, 1972? O YES
B. Has the parcel ever been part of a division of land action since June
If yes, describe the previous action
►N
NO
1, 1972? El YES CK NO
7. LOCATION OF PARCEL - Include a map deliniatinq the project area and tie to a section corner.
114 OF 1/4 SECTION 30 TOWNSHIP 9
N CIS RANGE 60 Ti E I W
.Xi
PRINCIPAL MERIDIAN: E 6TH
■
Ft.M. E7 UTE Li COSTILLA
8. PLAT Location of ail wells on property roust be plotted and permit numbers provided.
Surveyors plat 111 Yes O No If not, scaled hand drawn sketch O Yes ; No
9. ESTIMATED WATER REQUIREMENTS - Gallons per Qay or Acre Fat per Year
10. WATER SUPPLY SOURCE
HOUSEHOLD USE # 0 of units GPO AF
O EXISTING
WELLS
WELL PERMIT NUMBERS
■
DEVELOPED
SPRING
® NEW WELLS
PROPosID MARRS CAECA ONE
0 Au(MAI 0 UM ARAPAHO£
None
0 UPPER OAwsaw 0 torso ARAPAHO£
o towER DAWSON Ca uRAME Fox HAAS
COMMERCIAL USE a 0 of S.F. GPD AF
O petal
O DAKOTA
21 QUO His hPlains Brule Fm
IRRIGATION 4' 0
of acres GPD AF
Twr - White River Group
STOCK WATERING b 0 of head GPO AF
•
O MUNICIPAL
_.. . .. _
OTHER N/A GPD AF
O ASSOCIATION
O COMPANY
WATER COURT DECREE CASE NO.'S
❑ DISTRICT
TOTAL GPO AF
NAME
LETTER OF COMMITMENT FOR
SERVICE ❑ YES ® NO
11. ENGINEER'S WATER SUPPLY REPORT
■
YES
►:4
NO IF YES, PLEASE FORWARD WITH THIS FORM. (The may be required before ow review es .:ampletedj
12. TYPE OF SEWAGE DISPOSAL SYSTEM
A new septic system is proposed to be constructed on site as one does not exist today -
0 SEPTIC TANK/LEACH FIELD O CENTRAL SYSTEM - DISTRICT NAME
O LAGOON
■
VAULT - LOCATION SEWAGE HAULED TO
CI ENGINEERED SYSTEM (Attach a copy of engmaun g deugn) O OTHER
GURETUN
MIDSTREAM
518 17111 STREET SUITE 1405
DENVER, CO 80202
PHONE: 303-324-5967
Waste Management Plan
The following Waste Management Plan outlines general guidelines for waste management
practices at all Cureton Front Range, LL (Cureton) facilities.
General Waste Management Practices
The following management practices must be followed in the management of wastes
generated within Cureton facilities:
1. Dispose or manage wastes and recoverable materials in permitted or otherwise
authorized locations and facilities only. Unauthorized disposal or management will not
be tolerated.
2. Reduce waste generation whenever practical. This is known as waste minimization or
pollution prevention.
3. Reuse or recycle materials whenever practical. This not only lowers consumption
of raw materials, it also eliminates the need for waste disposal.
4. Avoid co -mingling wastes of different classifications. For example, never place non-
hazardous wastes in the same container as hazardous waste. Keep recyclable
material separate from non -recyclable waste. It can be difficult or impossible to
separate wastes after they are generated.
5. Maintain good housekeeping practices. Employees and contractors should maintain
neat, clean work areas to reduce the need for additional clean up and the wastes
such clean up can generate.
6. Properly store wastes, especially hazardous wastes, to avoid releases to soil, water,
and air, until they can be appropriately managed and disposed of.
7. Clearly identify waste containers. Use a label or other means to clearly identify the
contents of containers of hazardous, non -hazardous, and inert wastes.
8. Document quantities and disposition of all hazardous and non -hazardous wastes
as instructed in this Waste Management Plan. Waste tracking can help Cureton
manage costs, and is required for all hazardous wastes.
a. Such documentation will be included in the final report developed at the
conclusion of any response activities.
9. Recovered liquids (e.g., oil, water, sludge) should be collected and stored in as large
a container as possible (e.g., Department of Transportation [DOT] drum, tote tank,
frac tank, or barge) to maximize the decanting potential, facilitate uninterrupted
recovery, and to minimize equipment decontamination requirements.
10. Employees and contractors should communicate ideas for waste minimization and
waste management improvements to supervisors and fellow employees in different
areas.
CURE 0
MIDSTREAM
518 17TH STREET SUITE 1405
DENVER, CO 80202
PHONE: 303-324-5967
Waste Handlers
Liquid materials recovered at each facility will be collected for proper disposal or recycling.
Following facility startup, the appropriate disposal and/or recycling companies will be
identified and listed to handle the waste generated. The list will be facility specific.
Waste Designation
The process of classifying waste as solid or hazardous waste is termed "waste designation."
Petroleum products such as diesel generally are not designated as hazardous waste.
Recovered oil liquids and other materials contaminated by oil that are not designated as
hazardous waste and that may be recycled, burned, or blended for fuel are considered solid
waste and subject to designation as a hazardous waste as determined through testing. If such
wastes do not designate as a hazardous waste they are classified and managed as a solid
waste.
1. Waste Characterization
Wastes that can typically be identified as non -hazardous via operator or generator
knowledge include non -oiled waste from response activities and minimally oiled wastes
such as some discarded decontaminated or personal protective equipment (PPE).
Some oiled waste material may be tested to determine if the waste is a Federal or
state hazardous waste. If the waste is designated as not hazardous, testing will
identify if the waste concentration is low enough in total oil and grease or total organic
carbon to be accepted in a local landfill or Resource Conservation and Recovery Act
(RCRA) Class III disposal facility. Spent oiled boom and sorbent material as well as
contaminated soil, sand, or other loose, natural material would be composite sampled
as a means to classify the material.
All oily waste streams will be characterized so that the wastes are managed in
accordance with Federal and state hazardous waste regulations. The testing results
will determine the final disposition and disposal of the waste. A minimum of 10 percent
of a waste stream (e.g., oily waste bags) will be tested if operator knowledge indicates
hazardous waste may be present.
2. Waste Classification
a. Oily - Liquid Wastes
Oily liquid wastes (i.e., oily water and emulsions) that are handled, stored, and
disposed of during operations are very similar to those handled during routine
storage and transfer operations. Oily water and emulsions may be generated
by vehicle operations (e.g., spent motor oils, lubricants, etc.), and equipment
cleaning operations.
b. Non -Oily - Liquid Wastes
Significant quantities of non -oily liquid wastes outside of sewage is not
anticipated for Cureton facilities. A septic system will handle sewage on site.
CURETON
MIDSTREAM
518 17111 STREET SUITE 1405
DENVER, CO 80202
PHONE: 303-324-5967
c. Solid Wastes
A solid waste is defined as any discarded material provided that it is not
specifically excluded under Federal or State regulations. These exclusions
cover materials such as domestic sewage and mixtures of sewage discharged
through a sewer system or industrial wastewater point source discharges. A
discarded material is any material which is abandoned (i.e., disposed of,
burned, or incinerated) or accumulated, stored, or treated prior to being
abandoned. A discarded material is also any material recycled or any material
considered inherently waste like. Recycled material is considered solid waste
when used in a manner constituting disposal, placed on land, or burned for
energy recovery.
A solid waste may be considered a hazardous waste. A solid waste, as
defined above, may be a hazardous waste if it is not excluded from
Federal or State regulation and is either a listed hazardous waste or
exhibits the characteristics of a hazardous waste. A solid waste exhibits
the characteristics of a hazardous waste if it exceeds the thresholds
established in determining the following:
■ Ignitability
■ Corrosivity
■ Reactivity
■ Toxicity
A solid waste may also become a hazardous waste if it is mixed with a
listed hazardous waste or, in the case of any other waste (including
mixtures), when the waste exhibits any of the characteristics identified
above.
d. Oily - Solid/Semi-Solid Wastes
Examples of oily solid/semi-solid wastes that may be generated include
damaged or worn-out booms, disposable/soiled equipment, used sorbent
materials, saturated soils, contaminated beach sediments, driftwood, and
other debris.
e. Non -Oily - Solid/Semi-Solid Wastes
Non -oily solid/semi-solid wastes may be generated by emergency
construction operations (e.g., scrap, wood, pipe, and wiring) and office
and field operations (e.g., refuse).
Waste Sampling Procedures
Following facility startup, the appropriate sampling procedures will be developed and be
facility -specific. Following are some general sampling protocols.
1. Samples analyses will include toxicity characteristics (benzene only), reactivity,
ignitability, and other analyses, as necessary.
2. Samples will be collected in pre -cleaned glass containers and stored and transported
GURETUN
MIDSTREAM
518 17111 STREET SUITE 1405
DENVER, CO 80202
PHONE: 303-324-5967
in specially designated portable coolers. Such supplies will be provided by the
analytical laboratory that Cureton contracts for each facility.
3. Containers will be labeled with date, time, sample type, sample location, unique
sample number, and the samplers' signature. The contracted analytical laboratory will
provide labels.
4. Samples will be collected using a clean scooping device such as a hand trowel (either
a one-time disposable device or a device that can be decontaminated between each
sample). Reusable sampling equipment will be decontaminated with isopropyl alcohol
and water between collection of each sample.
5. Nitrile gloves will be worn during collection of each individual sample and changed
between samples.
6. The samples will be stored in the field in chilled coolers. The samples then will be
moved to a refrigerator or delivered to an analytical laboratory within the sample
holding time specified for the analytical methods selected. Proper Chain of Custody
(COC) protocol will be followed.
Sampling Guidelines
For oil sampling, the following guidelines will be used:
1. Third -party contractors will be used to collect all neat and contaminated material
samples.
2. Third -party contractors will be used to gauge all tanks containing oil -water mixtures.
3. Samples will be collected in pre -cleaned glass containers provided by an accredited
analytical laboratory.
4. Containers will be labeled with information such as the date, time, sample type, and
sample locations.
5. Solid material type samples (e.g., PPE) will be collected using a utility knife or
scissors.
6. Liquid type samples will be collected using an appropriate liquid sampling device.
7. Sampling equipment will be decontaminated with isopropyl alcohol and water and
thoroughly rinsed after each sample is collected.
8. Nitrile gloves will be used for sample collection, and will be changed between
samples to prevent cross contamination.
9. All spent sampling equipment and contaminated material associated with sampling
will be consolidated, containerized, and moved to the waste staging area.
10. Proper COC protocol will be followed.
Accumulation of Hazardous Waste
No permits are needed for collection and temporary storage of hazardous waste during an
emergency oil spill clean-up as long as waste is properly contained, labeled, and stored.
Storage requirements for hazardous waste are more stringent than for non -hazardous waste.
A hazardous waste storage area inspection form will be used to document that waste was
appropriately managed. Generators of hazardous waste must obtain a State/Environmental
Protection Agency (EPA) identification number since hazardous waste may not be shipped off
site without an identification number.
GURETUN
MIDSTREAM
518 17111 STREET SUITE 1405
DENVER, CO 80202
PHONE: 303-324-5967
Cureton does not anticipate its facilities being categorized as Hazardous Waste Generators.
Management of RCRA-Regulated Waste
Many hydrocarbon products contain benzene, which can be considered a hazardous waste
under the RCRA toxicity characteristic rule. As a result, oily waste (excluding marine diesel
fuel -contaminated wastes) that cannot be recycled/reclaimed will be analyzed for hazardous
characteristics before a treatment or disposal option is chosen. Standard procedures approved
by RCRA regulations for sampling, analyzing, and monitoring oil and oily waste material will be
utilized. Representative samples will be collected and analyzed for hazardous characteristics
(i.e., ignitability, corrosivity, reactivity, or toxicity) by the Toxicity Characteristic Leaching
Procedure (TCLP) to determine if the waste should be handled as hazardous.
If oily waste is determined to be hazardous under the RCRA, the wastes will be sent to
an EPA- or State -permitted hazardous waste management facility for treatment and
disposal. If the material spilled is itself a RCRA-listed hazardous waste, any resulting
spill residue is automatically a RCRA-listed hazardous waste.
Interim Storage, Segregation, and Tracking
This section provides information on the interim storage of generated waste, includes
guidance on the segregation of different types of waste to facilitate proper and efficient
management.
Locations for Temporary Waste Storage Areas
Temporary waste staging areas (Waste Staging Areas) will be established prior to facility
startup.
How each Waste Staging Area will be constructed, bermed, or covered to minimize rainwater
infiltration and leaching will be identified by Cureton facility/site.
Waste Inventory
All containers (e.g., bags, drums, roll -off boxes, totes, dumpsters, etc.) will be
labeled with the following information:
• Type of material (e.g., oil boom, absorbent pads, etc.)
• Location (e.g., waste generation site)
• Date
• Time
•
Name and phone number of contact person
Include the term "Recovered Oil- (put type of material here, such as sand, PPE,
debris) Contaminated Material."
Oily wastes will be placed in leak -proof containers to prevent leakage during handling and
transportation. The containers may be 55 -gallon drums, portable tanks, tank trucks, roll -off
boxes, dumpsters, storage barges, or containers that can be sealed and covered to prevent
spillage.
LJURETUN
MIDSTREAM
518 17111 STREET SUITE 1405
DENVER, CO 80202
PHONE: 303-324-5967
Double -walled plastic bags may be used for this purpose or all oil -contaminated materials can
be double -bagged and tied or closed with duct tape. Not more than 20 pounds of debris are to
be placed in each double bag. Each container of collected debris will be labeled as to its
contents (e.g., tar balls, oily debris, or non -oily rubbish). Similar waste types should be staged
together as a key task in the spill response segregation strategy.
Chain of Custody
The contracted transporter of the generated waste shall provide facility personnel a copy of
the COC form. At a minimum, the COC shall contain the following information:
• Name of facility personnel handling waste transfer
• Date waste was generated
• Date waste was picked up
• Description of the waste
• Description of waste container
• Name of transport company
• Name of transport driver
• Location and name of disposal facility
• Signatures s of both parties involved and date of pickup
The facility will maintain copies of all COCs involved with waste generation and transfer.
Segregation
1. Contaminated Soil
Contaminated soil and shell material can be stockpiled in designated laydown areas
that will be identified prior to facility startup. Stockpile areas underlain with visqueen
and covered with visqueen or other sheeting may be required to prevent rainfall
infiltration and runoff. Stockpiling of contaminated soils should be viewed as a
temporary measure, as the soil will eventually be containerized for off -site treatment
andlor disposal. Soil will be characterized and stored as per direction from Cureton's
Environmental Health and Safety Department.
2. Oiled Organic Debris
Oiled organic debris includes wood, grasses, aquatic vegetation, and similar organic
matter that cannot be treated and restored. Oiled organic debris should be segregated
from dissimilar debris and containerized in clear plastic bags, so the contents inside
can be viewed. This material typically is designated for disposal at an approved solid
waste landfill.
3. Oiled Debris
Oiled debris includes equipment and materials that are not deemed to be treatable or
material that cannot be returned to its original service. Oiled debris will be
containerized in 55 -gallon drums or roll -off boxes and/or dumpsters. This material
typically is designated for disposal at an approved solid waste landfill.
CURETON
MIDSTREAM
518 17111 STREET SUITE 1405
DENVER, CO 80202
PHONE: 303-324-5967
a. Contaminated Sorbent Material and PPE
Contaminated sorbents (e.g., absorbent, booms, pads, wipes, etc.) and PPE
will be containerized in plastic bags, drums, roll -off boxes, or dumpsters as
appropriate. Plastic bags, taped, closed, and stored in roll -off boxes is the
preferred technique for containing such material.
b. Contaminated Rinsate Water from Decontamination Stations
Contaminated rinsate from personnel or equipment decontamination areas
will be containerized in open top 55 -gallon drums fitted with bung -sealing
lids. Contaminated rinse water and other oily water generated during a spill
response typically will be transported by vacuum truck from points of
generation of frac tanks and portable oily water storage tanks supplied by
the oil spill response organization or oily water reclamation contractor.
i. Hazardous Waste
Hazardous waste will be kept in designated areas within the temporary
waste staging areas. Hazardous waste will typically be containerized in
drums or visqueen-lined roll -off boxes with volatile organic compound
(VOC) controls, if necessary. Hazardous waste will not be co -mingled
with non -hazardous waste. Cureton does not anticipate any generation
of hazardous waste at its facilities.
it Non -Oiled Waste Generated from Spill Response Activities
Non -oil waste material includes trash generated at a facility that cannot
be recycled. Non -oiled waste will be segregated from any oiled waste into
a trash dumpster located at the facility.
Hello