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Alaska Oil and Gas Conservation Commission
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INDEX AREA INJECTION ORDER lSA
COLVILLE RIVER FIELD
1. February 3, 2000
2. February 4, 2000
3. February 9, 2000
4. August 16, 2000
5. July 8, 2002
6. July 29, 2002
7. May 12, 2002
8. May 5, 2004
9. July 7, 2004
10. July 26,2004
ARCO Application for Amendment to AIO 18
Core Samples
Notice of hearing, Affidavit
E-mail from AOGCC Re: Stormwater Silt Disposal
Approval
List of suspended solids
Decision Document
Request for Administrative Approval for Injection of
Treated Camp Effluent and Approved Non-Hazardous
Fluids in to Alpine Sea Water Flood Wells
Letter to Mr. Alonzo from Jim Regg Re: Requirements
E-mail from operation to Regg
CDI-I9A Class Disposal Well Fracture Growth Estimate
11. September 27,2004 Public Notice to Amend Underground Injection Orders to
Incorporate Consistent Language Addressing the
Mechanical Integrity of Wells
AIO 18A
·
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STATE OF ALASKA
OIL AND GAS CONSERVATION COMMISSION
3001 Porcupine Drive
Anchorage, Alaska 99501-3192
Re:
The APPLICATION OF ARCO
ALASKA Inc. ("ARCO") for an
amendment of Area Injection Order
No. 18 to allow disposal into certain
disposal intervals on an area basis in
the Colville River Field.
) Area Injection Order No.18A
) Colville River Field
) Colville River Unit
) Alpine Oil Pool
)
)
April 18, 2000
IT APPEARING THAT:
1. By application dated February 3, 2000, ARCO Alaska, Inc. ("ARCO") requested authorization from
the Alaska Oil and Gas Conservation Commission ("Commission") to amend Area Injection Order
No. 18 to allow disposal of fluids into the disposal intervals specified in Disposal Injection Order No.
18 on an area basis.
2. Notice of opportunity for public hearing was published in the Anchorage Daily News on
February 9,2000.
3. The Commission did not receive a protest or a request for a public hearing.
FINDINGS:
1. Commission regulation 20 MC 25.460 provides authority to issue an order governing underground
injection of fluids on an area basis for all wells within the same field, facility site, reservoir, project,
or similar area.
2. The Commission has issued Disposal Injection Order No. 18 on April 19, 1999 and Area Injection
Order No. 18 on January 24,2000. The findings, conclusions and administrative records are adopted
by reference and incorporated into this order.
3. The Alpine Oil Pool ("AOP") is located in the Colville River Delta area on Alaska's North Slope.
4. ARCO is the only operator of all wells within one-quarter mile of the area proposed for dispsoal. The
State of Alaska and Kuukpik Corporation are the surface owners.
5. ARCO anticipates drilling up to five disposal wells into the disposal interval approved for Class II
disposal operations in DIO No. 18.
6. The Commission issued Disposal Injection Order No. 18 for well WD-02. The well is currently
operating as a Class I well under EPA UIC Area Permit AK-1I003-A.
Mea ¡nj,,"on 0_ No. t 8A .
April 18, 2000
Page 2
,
7. EPA UIC Area Permit AK-1I003-A Part ILA.3 prohibits the drilling of offsetting wells into or below
the arresting zone (lower Kingak) within the 'l4 mile radius area of review unless directed by EP A.
8. Salinity calculations range from 15,000 to 18,000 milligrams per liter ("mg/L") total dissolved solids
("TDS") throughout the Cretaceous and older stratigraphic sections in the Colville Delta Area.
9. Disposal well design requirements include 16-inch conductor casing set at 75'and cemented; surface
holes drilled to a minimum of2200' TVDSS and either 95/8" or 7 5/8" casing set and cemented to
surface; and production casing set near the base ofthe injection zone and cemented across and not
less than 500' measured depth above the Alpine formation. Single tubing strings between 2 7/8" and
4 W' OD will be installed in each well. The tubing by casing annulus will be isolated within 200' of
the top of the uppermost injection interval.
10. The only wellbores penetrating the disposal interval will be those wellbores intended for disposal
purposes. Since these wellbores will be fully cemented across both the injection and confining
intervals, there are no past, present or planned penetrations of this interval that could provide
communication channels to shallower intervals.
11. ARCO estimates that oil field waste fluids could total 4 million barrels over the life of the field.
ARCO also anticipates disposal of as much as 14 million barrels of produced water before the
initiation ofwaterflood operations re-injecting the produced water.
12. ARCO seeks to dispose of oil field waste fluids that may include drill cuttings and fluids, completion,
workover and stimulation fluids, frac sand, produced water, crude oil, production vessel sludge/sand,
natural gas liquids, rig wash and well cellar fluids, diesel/methanol used as freeze protectant, plant
upset fluids, snowmelt, and any fresh or seawater necessary to enable disposal.
13. Daily injection volumes are not expected to exceed 2,500 barrels, and disposal rates are not expected
to exceed 5 barrels per minute. A maximum injection pressure of 3200 psi is estimated.
14. ARCO plans to run a cement quality log to verify the cement quality and top of cement behind the
production casing in any well prior to use as a disposal well.
15. ARCO will demonstrate the mechanical integrity ofi11iection wells as specified in 20 AAC 25.412
prior to initiating injection operations.
16. The operator will comply with the requirements of20 AAC 25.402 (d) & (e) to monitor tubing-casing
annulus pressures of injection wells periodically during injection operations to ensure there is no
leakage and that casing pressure remains less than 70% of minimum yield strength of the casing.
17. All existing wells drilled within the proposed project area have been constructed in accordance with
20 AAC 25.030. All wells abandoned in the proposed project area have been abandoned in
accordance with 20 AAC 25.105 and 20 AAC 25.112 or an equivalent precursor regulation.
CONCLUSIONS:
1. The application requirements of20 AAC 25.402 have been met.
2. An Area Injection Order is appropriate for the project area in accordance with 20 AAC 25.460.
Area Injection Order No. ¡SA .
April 18, 2000
Page 3
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3. No underground sources of drinking water ("USDW's") exist beneath the permafrost in the Colville
River Unit area.
4. No wells may be drilled into or below the arresting zone (lower Kingak) for the wells covered in the
\.4 mile radius area of review under EPA permit AK-1I003-A.
5. The proposed injection operations will be conducted in permeable strata, which reasonably can be
expected to accept injected fluids at pressures less than the fracture pressure of the confining strata.
6. Disposal will be limited to produced water and oil field wastes that the Commission determines are
suitable for disposal in a Class II well.
7. Well mechanical integrity will be demonstrated in accordance with 20 AAC 25.412 prior to initiation
of injection operations.
8. The mechanical integrity of each injection well will be tested at least every four years after an initial
test. Wells used for grind and inject purposes must be tested every two years.
9. Tubing-casing annulus pressure and injection rates will be monitored at least weekly for disclosure of
possible abnormalities in operational conditions.
10. An amendment to Area Injection Order 18 to enable additional disposal wells will not cause waste
nor jeopardize correlative rights.
NOW, THEREFORE, IT IS ORDERED that: (1) Area Injection Order #18A supercedes Disposal
Injection Order #18 dated April 19, 1999 and Area Injection Order #18 dated January 24,2000; and (2)
the following rules govern Class II injection and disposal operations in the affected area described below:
UMIAT MERIDIAN
T11N R4E Section 1,2,3,4,5, 7, 8, 9, 10, 11, 12, 13, 14, 15, 16,21,22,23,24,25,26,27.
T11N R5E Sections 1,2,3,4,5,6,7,8,9,10,11,12,13,14,15,16,17,18,19,20, 21, 22, 23, 24,
29, and 30.
T12N R4E Sections 24, 25, 26, 27, 33, 34, 35 and 36.
Tl2N R5E Sections 13, 14, 15, 19,20,21,22,23,24,25,26,27,28,29,30,31,32,33,34,35 and 36.
Rule 1 Authorized Injection Strata for Enhanced Recovery
Within the affected area, fluids may be injected for purposes of pressure maintenance and enhanced
recovery into strata that are common to and correlate with the interval between the measured depths of
6876 and 6976 feet in the Bergschrund No.1 well.
Area Injection Order No. 18A .
April 18, 2000
Page 4
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Rule 2 Authorized Iniection Strata for Disposal
Within the affected area, Class II fluids may be injected for purposes of disposal into strata that are
common to and correlate with the interval between the measured depths of 8432 and 9540 feet in the
Sohio Alaska Petroleum Company Nechelik No.1 well.
Rule 3 Fluid Iniection Wells
The underground injection of fluids must be through a well permitted for drilling as a service well for
injection in conformance with 20 AAC 25.005 or through a well approved for conversion to a service well
for injection in conformance with 20 AAC 25.280.
Rule 4 Monitorine: the Tubine:-Casine: Annulus Pressure Variations
The tubing-casing annulus pressure and injection rate of each injection well must be checked at least
weekly to ensure there is no leakage and that it does not exceed a pressure that will subject the casing to a
hoop stress greater than 70% of the casing's minimum yield strength.
Rule 5 Reportine: the Tubine:-Casine: Annulus Pressure Variations
Tubing-casing annulus pressure variations between consecutive observations need not be reported to the
Commission unless well integrity failure is indicated as in Rule 7 below.
Rule 6 Demonstration of Tubine:-Casine: Annulus Mechanical Intee:ritv
A schedule must be developed and coordinated with the Commission that ensures that the tubing-casing
annulus for each injection well is pressure tested prior to initiating injection and at least once every four
years thereafter. For slurry injection wells, the tubing/casing annulus must be tested every two years for
mechanical integrity. A test surface pressure of 1500 psi or 0.25 psi/ft. multiplied by the vertical depth of
the packer, whichever is greater, will be used. The test pressure must show a stabilizing trend and must
not decline more than 10% in a thirty-minute period. The Commission must be notified at least twenty-
four (24) hours in advance to enable a representative to witness pressure tests.
Rule 7 Well Intee:ritv Failure
Whenever operating pressure observations, injection rates, or pressure tests indicate pressure
communication or leakage of any casing, tubing or packer, the operator must notify the Commission on
the first working day following the observation, obtain Commission approval of a plan for corrective
action, and obtain Commission approval to continue injection.
Rule 8 Plue:e:ine: and Abandonment ofIniection Wells
An injection well located within the affected area must not be plugged or abandoned unless approved by
the Commission in accordance with 20 AAC 25.105.
Area Injection Order No. 18A .
April 18, 2000
Page 5
Rule 9 Surveillance
,
For slurry injection wells, a baseline temperature survey from surface to total depth, initial step rate test to
pressure equal or exceeding maximum injection pressure and pressure falloff are required prior to
sustained disposal injection. Regular fill depth tags are required at least once annually or as warranted
following consultation with the Commission. Operating parameters including disposal rate, pressure,
annuli pressures and volume of slurry pumped must be monitored and reported according to the
requirements of20 AAC 25.432.
For slurry injection wells, an annual performance report will be required including rate and pressure
performance, surveillance logging, fill depth, survey results, and volumetric analysis of the disposal
storage volume, estimate of fracture growth, if any, and updates of operational plans. Report submission
must be on or before April 1, in conjunction with the Alpine Pool Annual Reservoir Report.
Rule 10 Notification
The operator must notify the Commission if it learns of any improper Class II injection. Additionally,
notification requirements of any other State or Federal agency remain the operators' responsibility.
Rule 11 Administrative Action
Upon request, the Commission may administratively amend any rule stated above as long as the operator
demonstrates to the Commission's satisfaction that sound engineering practices are maintained and the
amendment will not result in an increased risk of fluid movement into a USDW.
DONE at Anchorage, Alaska and dated April 18, 2000.
obert N. Christenson, P .E., Chair
Alaska Oil and Gas Conservation Commission
~~~
Camillé Oechsli Taylor, CommisslOne
Alaska Oil and Gas Co e t' Commission
AS 31.05.080 provides that within 20 days after receipt of written notice of the entry of an order, a person affected by it may file with the
Commission an application for rehearing. A request for rehearing must be received by 4:30 PM on the 23rd day following the date of the order, or
next working day if a holiday or weekend, to be timely filed. The Commission shall grant or refuse the application in whole or in part within 10 days.
The Commission can refuse an application by not acting on it within the 10-day period. An affected person has 30 days ITom the date the
Commission refuses the application or mails (or otherwise distributes) an order upon rehearing, both being the final order of the Commission, to
appeal the decision to Superior Court. Where a request for rehearing is denied by nonaction of the Commission, the 30-day period for appeal to
Superior Court runs ITom the date on which the request is deemed denied (i.e., 10th day after the application for rehearing was filed).
"
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~~~~Œ lID~ ~~~~æ~
.
A"~ASIiA. ORAND GAS
CONSERVATION COMMISSION
TONY KNOWLES, GOVERNOR
333 W. 7'" AVENUE, SUITE 100
ANCHORAGE, ALASKA 99501-3539
PHONE (907) 279-1433
FAX (907) 276-7542
ADMINISTRATIVE APPROVAL NO. AlO 18A.Ol
Re: The application from Phillips Alaska, Inc. to mix treated wastewater effluent with Class II EOR
injection fluids as needed when the primary disposal well is unavailable in the Colville River
Field, Alpine Oil Pool, North Slope, Alaska.
Thomas Manson
Michael Nelson
Alpine Development Project
P.O. Box 196860
Anchorage, AK 99519-6860
Gentlemen:
By letter dated May 12, 2002, Phillips Alaska, Inc. ("PAl") requested authorization to blend treated
wastewater effluent with seawater for injection into Class II enhanced oil recovery (EOR) wells in the
Alpine Oil Pool when the primary disposal well (WD-02) is unavailable. The Commission may authorize
the injection of fluids for enhanced recovery of oil and gas if the fluid is appropriate for enhanced recovery.
The Commission has reviewed the analyses of the treated waste effluent provided in your application.
Based on the effluent analysis and that of the seawater being used in the EOR process, the Commission
concludes that the characteristics of the treated effluent are consistent with other aqueous fluids used for
EOR injection. The estimated mix of 1 % effluent with seawater injectant will not impact properties of the
seawater as it relates to EOR efficiency.
Therefore, in accordance with the provisions of Area Injection Order l8A, the Commission approves the
mixing of camp waste effluent with Class II fluids used for EOR. As a condition of this approval PAl must
continue to collect and analyze representative samples of the mixed fluid stream to demonstrate its
continued suitability for EOR injection. Analysis results shall be retained according to the provisions of
20 AAC 25.310. Volumes shall be incorporated into the monthly (Form 10-406) and annual (Form 10-413)
injection reports.
DONE at Anchomge, Ala,ka and dated Augost 1, 20...~~.,~... ~
~ MdvJ-~9.I i~/
Cammy oe~sli Taylor Ò Dan e T. Seamount, Jr.
Chair Commissioner
BY ORDER OF THE COMMISSION
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FRANK H. MURKOWSKI. GOVERNOR
AI,ASIiA. OIL AlO) GAS
CONSBRVATlON COJDIISSION
333 W. 7fH AVENUE, SUITE 100
ANCHORAGE, ALASKA 99501-3539
PHONE (907) 279-1433
FAX (907)27&7542
September 27, 2004
Proposals to Amend Underground Injection Orders to Incorporate
Consistent Language Addressing the Mechanical Integrity of Wells
The Alaska Oil and Gas Conservation Commission ("Commission"), on its own motion,
proposes to amend the rules addressing mechanical integrity of wells in all existing area injection
orders, storage injection orders, enhanced recovery injection orders, and disposal injection
orders. There are numerous different versions of wording used for each of the rules that create
confusion and inconsistent implementation of well integrity requirements for injection wells
when pressure communication or leakage is indicated. In several injection orders, there are no
rules addressing requirements for notification and well disposition when a well integrity failure
is identified. Wording used for the administrative approval rule in injection orders is similarly
inconsistent.
The Commission proposes these three rules as replacements in all injection orders:
Demonstration of Mechanical Integritv
The mechanical integrity of an injection well must be demonstrated before injection
begins, at least once every four years thereafter (except at least once every two years in
the case of a slurry injection well), and before returning a well to service following a
workover affecting mechanical integrity. Unless an alternate means is approved by the
Commission, mechanical integrity must be demonstrated by a tubing/casing annulus
pressure test using a surface pressure of 1500 psi or 0.25 psi/ft multiplied by the vertical
depth of the packer, whichever is greater, that shows stabilizing pressure and does not
change more than 10 percent during a 30 minute period. The Commission must be
notified at least 24 hours in advance to enable a representative to witness mechanical
integrity tests.
Well Integrity Failure and Confinement
Whenever any pressure communication, leakage or lack of injection zone isolation is
indicated by injection rate, operating pressure observation, test, survey, log, or other
evidence, the operator shall immediately notify the Commission and submit a plan of
corrective action on a Form 10-403 for Commission approval. The operator shall
immediately shut in the well if continued operation would be unsafe or would threaten
contamination of freshwater, or if so directed by the Commission. A monthly report of
daily tubing and casing annuli pressures and injection rates must be provided to the
Commission for all injection wells indicating well integrity failure or lack of injection
zone isolation.
Administrative Actions
Unless notice and public hearing is otherwise required, the Commission may
administratively waive or amend any rule stated above as long as the change does not
promote waste or jeopardize correlative rights, is based on sound engineering and
geoscience principles, and will not result in fluid movement outside of the authorized
injection zone.
The following table identifies the specific rules affected by the rewrite.
Affected Rules
Injection Order "Demonstration of "Well Integrity "Administrative
Mechanical Failure and Action"
Integrity" Confinement"
I Area Inj ection Orders
AIO 1 - Duck Island Unit 6 7 9
AIO 2B - Kuparuk River
Unit; Kuparuk River, 6 7 9
Tabasco, Ugnu, West Sak
Fields
AIO 3 - Prudhoe Bay Unit; 6 7 9
Western Operating Area
AIO 4C - Prudhoe Bay Unit; 6 7 9
Eastern Operating Area
AIO 5 - Trading Bay Unit; 6 6 9
McArthur River Field
AIO 6 - Granite Point Field; 6 7 9
Northern Portion
AIO 7 - Middle Ground 6 7 9
Shoal; Northern Portion
AIO 8 - Middle Ground 6 7 9
Shoal; Southern Portion
AIO 9 - Middle Ground 6 7 9
Shoal; Central Portion
AIO lOB - Milne Point Unit;
Schrader Bluff, Sag River, 4 5 8
Kuparuk River Pools
AIO 11 - Granite Point 5 6 8
Field; Southern Portion
AIO 12 - Trading Bay Field; 5 6 8
Southern Portion
AIO 13A - Swanson River 6 7 9
Unit
AIO 14A - Prudhoe Bay 4 5 8
Unit; Niakuk Oil Pool
AIO 15 - West McArthur 5 6 9
( ,
'~..
~
Affected Rules
"Demonstration of "Well Integrity "Administrati ve
Injection Order Mechanical Failure and Action"
Integrity" Confinement"
River Unit
AIO 16 - Kuparuk River 6 7 10
Unit; Tam Oil Pool' 6 8
AIO 1 7 Badami Unit 5
AIO 18A - Colville River 6 7 11
Unit; Alpine Oil Pool
AIO 19 - Duck Island Unit; 5 6 9
Eider Oil Pool
AIO 20 - Prudhoe Bay Unit; 5 6 9
Midnight Sun Oil Pool
AIO 21 - Kuparuk River 4 No rule 6
Unit; Meltwater Oil Pool
AIO 22C - Prudhoe Bay 5 No rule 8
Unit; Aurora Oil Pool 6 9
AIO 23 Northstar Unit 5
AIO 24 - Prudhoe Bay Unit; 5 No rule 9
Borealis Oil Pool
AIO 25 - Prudhoe Bay Unit; 6 8 13
Polaris Oil Pool
AIO 26 - Prudhoe Bay Unit; 6 No rule 13
Orion Oil Pool
Dis~osal Injection Orders
DIO 1 - Kenai Unit; KU No rule No rule No rule
WD-l
DIO 2 - Kenai Unit; KU 14- No rule No rule No rule
4
DIO 3 - Beluga River Gas No rule No rule No rule
Field; BR WD-l
DIO 4 - Beaver Creek Unit; No rule No rule No rule
BC-2
DIO 5 - Barrow Gas Field; No rule No rule No rule
South Barrow #5
DIO 6 - Lewis River Gas No rule No rule 3
Field; WD-l
DIO 7 - West McArthur 2 3 5
River Unit; WMRU D-I
DIO 8 - Beaver Creek Unit; 2 3 5
BC-3
DIO 9 - Kenai Unit; KU 11- 2 3 4
17
DIO 10 - Granite Point 2 3 5
Field; GP 44-11
Affected Rules
"Demonstration of "Well Integrity " Administrative
Injection Order Mechanical Fail ure and Action"
Integrity" Confinement"
DIO 11 - Kenai Unit; KU 2 3 4
24-7
DIO 12 - Badami Unit; VVD- 2 3 5
1, VVD-2
DIO 13 - North Trading Bay 2 3 6
Unit; S-4
DID 14 - Houston Gas 2 3 5
Field; Well #3
DID 15 - North Trading Bay 2 3 Rule not numbered
Unit; S-5
DID 16 - West McArthur 2 3 5
River Unit; WMRU 4D
DID 1 7 - North Cook Inlet 2 3 6
I Unit; NCill A-12
DID 19 - Granite Point 4 6
Field; W. Granite Point State 3
17587 #3
I DID 20 - Pioneer Unit; Well 3 4 6
1702-15DA WDW
DID 21 - Flaxman Island; 3 4 7
Alaska S tate A - 2
DID 22 - Redoubt Unit; RU 3 No rule 6
Dl
DIO 23 - Ivan River Unit; No rule No rule 6
IRU 14-31
DIO 24 - Nicolai Creek Order expired
Unit; NCU #5
DIO 25 - Sterling Unit; SU 3 4 7
43-9
DIO 26 - Kustatan Field; 3 4 7
KF1
Storage In.iection Orders
SIO 1 - Prudhoe Bay Unit, No rule No rule No rule
Point McIntyre Field #6
SIO 2A- Swanson River 2 No rule 6
Unit; KGSF #1
SIO 3 - Swanson River Unit; 2 No rule 7
KGSF #2
Enhanced Recovery In.i ection Orders
EID 1 - Prudhoe Bay Unit; No rule 8
Prudhoe Bay Field, Schrader No rule
Bluff Formation Well V-I05
'-'")
Affected Rules
Injection Order "Demonstration of "Well Integrity "Administrative
Mechanical Failure and Action"
Integrity" Confinement"
EIO 2 - Redoubt Unit; RU-6 5 8 9
l
I
02-902 (Rev. 3/94)
Publisher/Original Copies: Department Fiscal, Department, Receiving
AO.FRM
STATE OF ALASKA
ADVERTISING
ORDER
NOTICE TO PUBLISHER ADVERTISING ORDER NO.
INVOICE MUST BE IN TRIPLICATE SHOWING ADVERTISING ORDER NO, CERTIFIED AO-02514016
AFFIDAVIT OF PUBLICATION (PART 2 OF THIS FORM) WITH ATIACHED COpy OF
ADVERTISEMENT MUST BE SUBMITIED WITH INVOICE
F
AOGCC
333 West ih Avenue, Suite 100
Anchorage, AK 99501
907-793-1221
AGENCY CONTACT
DATE OF A.O.
R
o
M
DATES ADVERTISEME~T REQUIRED:
T
o
Journal of Commerce
301 Arctic Slope Ave #350
Anchorage, AK 99518
October 3, 2004
THE MATERIAL BETWEEN THE DOUBLE LINES MUST BE PRINTED IN ITS
ENTIRElY ON THE DATES SHOWN.
SPECIAL INSTRUCTIONS:
United states of America
AFFIDAVIT OF PUBLICATION
REMINDER
State of
ss
INVOICE MUST BE IN TRIPLICATE AND MUST
REFERENCE THE ADVERTISING ORDER NUMBER.
A CERTIFIED COPY OF THIS AFFIDAVIT OF PUBLICATION
MUST BE SUBMITTED WITH THE INVOICE.
ATTACH PROOF OF PUBLICATION HERE.
division.
Before me, the undersigned, a notary public this day personally appeared
who, being first duly sworn, according to law, says that
he/she is the
of
Published at
in said division
and
state of
and that the advertisement, of which the annexed
is a true copy, was published in said publication on the
day of
2004, and thereafter for _ consecutive days, the last
publication appearing on the _ day of
. 2004, and that
the rate charged thereon is not in excess of the rate charged private
individuals.
Subscribed and sworn to before me
This _ day of
2004,
Notary public for state of
My commission expires
P.ublic ,NQtices
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Subject: Public Notices
From: Jody Colombie <jody _ colombie@admin.state.ak.us>
Date: Wed, 29 Sep2004 13:01 :04 -0800
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Public Notices
<iseott.Öranswick@ml1ls..gpv>, ~rad McKim..<rl1ck:ìl1lbs@B~·~.cQl1l>
P;1eé:\se. find the attached Not i ceancl. At tachme:nt . . for tÌle.. proJ?0E;ed atrieildmefit
undèrground.injection orders and the· Public Notice Happy Valley #10.
Jody COlombie
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~ublic ~~tice
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Subject: Public Notice
From: Jody Colombie <jody _ colombie@admin.state.ak.us>
Date: \V'~~~(.~~..~ep 2004 -0800
...........~~~~
Please publish the attached Notice on October 3, 2004.
Thank you.
Jody Colombie
Mechanical Integrity of Wells
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9/29/2004 1:10PM
Citgo Petroleum Corporation
PO Box 3758
Tulsa. OK 74136
Mary Jones
XTO Energy, Inc.
Cartography
810 Houston Street. Ste 2000
Ft. Worth, TX 76102-6298
/fjall¿:d /ð/;m'1
David McCaleb
IHS Energy Group
GEPS
5333 Westheimer, Ste 100
Houston, TX 77056
Kelly Valadez
Tesoro Refining and Marketing Co.
Supply & Distribution
300 Concord Plaza Drive
San Antonio, TX 78216
Robert Gravely
7681 South Kit Carson Drive
Littleton, CO 80122
George Vaught, Jr.
PO Box 13557
Denver, CO 80201-3557
Jerry Hodgden
Hodgden Oil Company
408 18th Street
Golden, CO 80401-2433
Richard Neahring
NRG Associates
President
PO Box 1655
Colorado Springs, CO 80901
John Levorsen
200 North 3rd Street, #1202
Boise, ID 83702
Kay Munger
Munger Oil Information Service, Inc
PO Box 45738
Los Angeles, CA 90045-0738
Samuel Van Vactor
Economic Insight Inc.
3004 SW First Ave.
Portland, OR 97201
Michael Parks
Marple's Business Newsletter
117 West Mercer St, Ste 200
Seattle, WA 98119-3960
Mark Wedman
Halliburton
6900 Arctic Blvd.
Anchorage, AK 99502
Schlumberger
Drilling and Measurements
2525 Gambell Street #400
Anchorage, AK 99503
David Cusato
200 West 34th PMB 411
Anchorage, AK 99503
Baker Oil Tools
4730 Business Park Blvd., #44
Anchorage, AK 99503
Ciri
Land Department
PO Box 93330
Anchorage, AK 99503
Jill Schneider
US Geological Survey
4200 University Dr.
Anchorage, AK 99508
Gordon Severson
3201 Westmar Cr.
Anchorage, AK 99508-4336
Jack Hakkila
PO Box 190083
Anchorage, AK 99519
Darwin Waldsmith
PO Box 39309
Ninilchick, AK 99639
James Gibbs
PO Box 1597
SOldotna, AK 99669
Kenai National Wildlife Refuge
Refuge Manager
PO Box 2139
Soldotna, AK 99669-2139
Penny Vadla
399 West Riverview Avenue
Soldotna. AK 99669-7714
Richard Wagner
PO Box 60868
Fairbanks, AK 99706
Cliff Burglin
PO Box 70131
Fairbanks, AK 99707
Bernie Karl
K&K Recycling Inc.
PO Box 58055
Fairbanks, AK 99711
Williams Thomas
Arctic Slope Regional Corporation
Land Department
PO Box 129
Barrow, AK 99723
North Slope Borough
PO Box 69
Barrow, AK 99723
'. ['Fwd: Re~ Consistent Wording for Injection\,...,y,èrs - Well Integrity ...
'-'"
Subject:. [Fwd: Re: ·ConsistêntWor~Î11.~tºr IrJ.J~ctiôn.9rd.¢*~..w~n~t~gí"ìtY~ª~vised.)]
From: John N orman<john~llOrrnan@a~m'¡Il~srate.a1(.u~?:
01 Oct 2004 11:09:26-0800
more
-------- Original Message --------
Subject:Re: Consistent Wording for Injection Orders - Well Integrity (Revised)
Date:Wed, 25 Aug 2004 16:49:40 -0800
From:Rob Mintz <robert mintz~law.state.ak.us>
To:jim regg~admin.state.ak.us
CC:dan seamount@admin.state.ak.us, john norman@admin.state.ak.us
Jim, looks good, but I still think maybe it would be good to include the following sentence or something like it in the well
integrity and confinement rule:
"The operator shall shut in the well if so directed by the Commission."
My thinking is that otherwise, an operator might argue that the Commission can only require the well to be shut in by
going through an enforcement action, issuing an order after notice and opportunity for hearing, or meeting the strict
requirements for an emergency order under the regulations. The proposed language makes clear that it is a condition of the
authorization to inject, that the operator must shut in the well if directed by the Commission after a notification of loss of
integrity, etc.
»> James Regg <jim regg@admin.state.ak.us> 8/25/20043:15:06 PM »>
Rob - Thanks for the review; here's a redraft after considering your comments. I have accepted most of the suggested edits;
also attached is response to questions you pose (responses are embedded in the comments, using brackets [JBR - ...] to set
apart from your questions).
Jim Regg
Rob Mintz wrote:
Jim, I have some questions about the draft language, which are shown as comments on the first document attached. Based
on my current guesses about what the answers will be to my questions, I also have some suggested edits, which are shown
as redlines on the second document attached.
»> James Regg <¡im regg~admin.state.ak.us> 8/17/20044:33:52 PM »>
Please delete previous version (email sent 8/9/04); I found another inconsistency in the injection orders regarding well
integrity that I have integrated into the proposed fix.
Attached is a proposal for consistent language in our injection orders addressing 3 rules related to well integrity:
- "Demonstration of Tubing/Casing Annulus Mechanical Integrity"
- "Well Integrity Failure"
- "Administrative Actions".
This proposal includes input from all Sr. staff (except Jack). If you agree with the approach, I'll work with Jody to
prepare the public notice.
Main points -
Demonstration of Tubing/Casing Annulus Mechanical Integrity
- standardizes the wording used for mechanical integrity demonstrations, and establishes abililty to grant alternate
methods (e.g., temp survey, logging, pressure monitoring in lieu of pressure testing
1 nf"
1 f\¡'1¡'1f\f\A A .f\'7 Dl\Jf
[Fwd: Re: Consistent Wording for Injection
.ers - Well Integrity ...
- specific to AIO 2C for Kuparuk, there is wording that is more appropriately included in Well Integrity Failure (i.e., more
frequent MITs when communication demonstrated)
- establishes more frequent MIT schedule for slurry injection wells (every 2 yrs) which is consistent with our current
practice (but not addressed in regulations)
Well Integrity Failure
- retitles to "Well Integrity Failure and Confinement"; inserted language regarding injection zone integrity (see DIO 25
and 26)
- consistent language regardless of type of injection (disposal, EOR, storage);
- eliminates requirement for immediate shut in and secure; allows continued injection until Commission requires shut in if
there is no threat to freshwater;
- eliminates delay in notifying Commission after detect leakage or communication ("i.e., "immediately notify");
- removes language about notifying "other state and federal" agencies;
- requires submittal of corrective action plan via 10-403;
- requires monthly report of daily injection rate and pressures (tubing and all casing annuli); this is a requirement we
currently impose when notified of leak or pressure communication;
- notice and action not restricted to leaks above casing shoe as stated in several DIOs
Administrative Actions
- adopts" Administrative Actions" title (earlier rules used" Administrative Relief');
- consistent language regardless of type of injection (disposal, EOR, storage);
- uses "administratively waive or amend" in lieu of terms like "revise", "reissue", etc.;
- adds geoscience to "sound engineering principles";
- language is more generic regarding fluid movement out of zone; existing versions mention varying combinations of
protecting "freshwater", "aquifers", "USDWs"; "risk of fluid movement"; "fluid escape from disposal zone"
Jim Regg
John K. Norman <John Norman@admin.state.us>
Commissioner
Alaska Oil & Gas Conservation Commission
? "f?
.. ^ I...... 1__"''' .. ....._~... ..
.. XFwd: Re:'Consistent Wording for Injection \xs - Well Integrity...
~
Subject: [Fwd: Re: Consistent Wording for lliJëctiøii0rger$ ~WêtlIi1tègrìty€R;evis~d)]
From: John Nonllan <john_notman@admin.s~äteòak.µs>
Date: 01 Oct 2004 11:08:55 -0800
please print all and put in file for me to review just prior to hearing on these amendments. thanx
-------- Original Message --------
Subject:Re: Consistent Wording for Injection Orders - Well Integrity (Revised)
Date:Thu, 19 Aug 2004 15:46:31 -0800
From:Rob Mintz <robert mintz(ã¿law.state.ak.us>
To:dan seamount(ã¿admin.state.ak.us, Jim regg(ã¿admin. state. ak.us,
john norrnan(ã¿admin.state.ak.us
Jim, I have some questions about the draft language, which are shown as comments on the first document attached. Based
on my current guesses about what the answers will be to my questions, I also have some suggested edits, which are shown as
red lines on the second document attached.
»> James Regg <iim regg@¿admin.state.ak.us> 8/17/20044:33:52 PM »>
Please delete previous version (email sent 8/9/04); I found another inconsistency in the injection orders regarding well
integrity that I have integrated into the proposed fix.
Attached is a proposal for consistent language in our injection orders addressing 3 rules related to well integrity:
- "Demonstration of Tubing/Casing Annulus Mechanical Integrity"
- "Well Integrity Failure"
- "Administrative Actions".
This proposal includes input from all Sr. staff (except Jack). If you agree with the approach, I'll work with Jody to prepare
the public notice.
Main points -
Demonstration of Tubing/Casing Annulus Mechanical Integrity
- standardizes the wording used for mechanical integrity demonstrations, and establishes abililty to grant alternate methods
(e.g., temp survey, logging, pressure monitoring in lieu of pressure testing
- specific to AIO 2C for Kuparuk, there is wording that is more appropriately included in Well Integrity Failure (i.e., more
frequent MITs when communication demonstrated)
- establishes more frequent MIT schedule for slurry injection wells (every 2 yrs) which is consistent with our current practice
(but not addressed in regulations)
Well Integrity Failure
- retitles to "Well Integrity Failure and Confinement"; inserted language regarding injection zone integrity (see DIG 25 and
26)
- consistent language regardless of type of injection (disposal, EOR, storage);
- eliminates requirement for immediate shut in and secure; allows continued injection until Commission requires shut in if
there is no threat to freshwater;
- eliminates delay in notifying Commission after detect leakage or communication ("i.e., "immediately notify");
- removes language about notifying "other state and federal" agencies;
- requires submittal of corrective action plan via 10-403;
- requires monthly report of daily injection rate and pressures (tubing and all casing annuli); this is a requirement we
currently impose when notified of leak or pressure communication;
- notice and action not restricted to leaks above casing shoe as stated in several DIOs
Administrative Actions
lof2
10/2/20044:07 PM
[Fwd: Re: Consistent Wording for Injection
~rs - Well Integrity...
- adopts "Administrative Actions" title (earlier rules used "Administrative Relief');
- consistent language regardless of type of injection (disposal, EOR, storage);
- uses "administratively waive or amend" in lieu of terms like "revise", "reissue", etc.;
- adds geoscience to "sound engineering principles";
- language is more generic regarding fluid movement out of zone; existing versions mention varying combinations of
protecting "freshwater", "aquifers", "USDWs"; "risk of fluid movement"; "fluid escape from disposal zone"
Jim Regg
John K. Norman <John Norman@¿admin.state.us>
Commissioner
Alaska Oil & Gas Conservation Commission
Content-Type: application/msword
Injection Order language - questions.doc
Content-Encoding: base64
---...--.... ..---
Content-Type: application/msword
Injection Orders language edits.doc
Content-Encoding: base64
2of2
11ì;' ;'lìf) A A .f)"7 n1\ K
---
'~
Standardized Language for Injection Orders
Date: August 17, 2004
Author: Jim Regg
Demonstration of Tubing/Casing Annulus Mechanical Integrity
The mechanical integrity of an injection well must be demonstrated before injection begins, after
a workover affecting mechanical integrity, and at least once every 4 years while actively
injecting. For slurry injection wells, the tubing/casing annulus must be tested for mechanical
integrity every 2 years. The MIT surface pressure must be 1500 psi or 0.25 psi/ft multiplied by
the vertical depth, whichever is greater, must show stabilizing pressure and may not change more
than 10% during a 30 minute period. Any alternate means of demonstrating mechanical integrity
must be approved by the Commission. The Commission must be notified at least 24 hours in
advance to enable a representative to witness pressure tests.
Well Integritv Failure and Confinement
The tubing, casing and packer of an injection well must demonstrate integrity during operation.
The operator must immediately notify the Commission and submit a plan of corrective action on
Form 10-403 for Commission approval whenever any pressure communication, leakage or lack
of injection zone isolation is indicated by injection rate, operating pressure observation, test,
survey, or log. If there is no threat to freshwater, injection may continue until the Commission
requires the well to be shut in or secured. A monthly report of daily tubing and casing annuli
pressures and injection rates must be provided to the Commission for all injection wells
indicating pressure communication or leakage.
Administrative Actions
Unless notice and public hearing is otherwise required, the Commission may administratively
waive or amend any rule stated above as long as the change does not promote waste or
jeopardize correlative rights, is based on sound engineering and geoscience principles, and will
not result in fluid movement outside of the authorized injection zone.
Standardized Language for Injection ()rders
Date: August 17,2004
Author: Jim Regg
Demonstration of Tubing/Casing Annulus Mechanical Integrity
The mechanical integrity of an injection well must be demonstrated before injection begins, at
least once every four years thereafter (exeept at least once every two years in the case of a slurry
iniection \vcll), and before returning a \vcl1 to service folh.1\ving aft.eF a workover affecting
mechanical integrity, and at lea~;t once e\'cr)' /1 year:; while acti';e1y injecting. For slurry
injection wells, the tubing/casing ar..nulus Inust be tested for mechanical integrity e\'ery 2 years.
Unless an alternate ¡-neans is approved bv the COlnnlission. Inechanic.al integrity rnust be
demonstrated by a tubing pressure test using a::r.tTe M-I+-surface pressure ofnlust be 1500 psi or
0.25 psi/ft multiplied by the vertical depth, whichever is greater, that mt:rSf-shoWâ stabilizing
pressure that doesand 1nay not change more than 10Q4r- percent during a 30 minute period. --A:R-y
alten1ate nleans of de1TIonstrating Inechanical integrity mu:;t be approved by the C01nnlission.
The Commission must be notified at least 24 hours in advance to enable a representative to
witness pressure tests.
Well Integrity Failure and Confinement
Except as otherwise provided in this rule,3=!he tubing, casing and packer of an injection well
must demonstrate Inaintain integrity during operation. \Vhenever any pressure conlmunication,
leakage or lack of injection zone isolation is indicated bv injection rate. operating pressure
observation, test, survey, log. or other evidence, t+he operator ~sha]l immediately notify the
Commission and submit a plan of corrective action on ª-Form 10-403 for Commission approval.:.
\vhencvcr any pressure comlnunicatiøn, leakage or lack of injection zone isolation is indicated by
injection fate, operating pressure øbsefTv'atíon, test, survey, or log. The operator shall shut in the
vveIl if so directed bv the Comnlission. The operator shall shut in the well \vithout awaiting a
response horn the Comlnission if continued operation would be unsafe or would threaten
contamination of freshwaterIf there is no threat to freshV";ater, injection 111ay continue until the
COlTI1TIÌssion requires the '.vell t(:1 be shut in or secured. Until corrective action is successfully
completed. ª monthly report of daily tubing and casing annuli pressures and injection rates
must be provided to the Commission for all injection wells indicating pressure communication or
leakage.
Administrative Actions
Unless notice and public hearing is otherwise required, the Commission may administratively
waive or amend any rule stated above as long as the change does not promote waste or
jeopardize correlative rights, is based on sound engineering and geoscience principles, and will
not result in fluid movement outside of the authorized injection zone.
~ ..(Fwà: ~e: [Fwd: AOGCC Proposed WI Lan~e for Injectors]]
\~.
SubJect: [Fwd: Re: [Fwd: AOGCC Proposed WI Language for Inj~ct()rs]]
From: Winton Aubert <winton_aubert@adrnin.state.ak~us>
D~t~: Thu, 28Qct 2004()9:48:53-0&OO
'1\
This is part of the record for the Nov. 4 hearing.
WGA
-------- Original Message --------
Subject: Re: [Fwd: AOGCC Proposed WI Language for Injectors]
Date: Thu, 28 Oct 2004 09:41:55 -0800
From: James Regg <jim regg@admin.state.ak.us>
Organization: State of Alaska
To: Winton Aubert <winton aubert@admin.state.ak.us>
References: <41812422.8080604@admin.state.ak.us>
These should be provided to Jody as part of public review record
Jim
Winton Aubert wrote:
FYI.
--------
Original Message --------
AOGCC Proposed WI Language for
Tue, 19 Oct 2004 13:49:33 -0800
Engel, Harry R <EngeIHR@BP.com>
winton aubert@admin.state.ak.us
Injectors
Subject:
Date:
From:
To:
Winton...
Here are the comments we discussed.
Harry
*From: * NSU, ADW Well Integrity Engineer
*Sent: * Friday, October 15, 2004 10:43 PM
*To: * Rossberg, R Steven¡ Engel, Harry R¡ Cismoski, Doug A¡ NSU, ADW Well
Operations Supervisor
*Cc: * Mielke, Robert L.¡ Reeves, Donald F¡ Dube, Anna T¡ NSU, ADW Well Integrity
Engineer
*Subject: * AOGCC Proposed WI Language for Injectors
Hi Guys.
John McMullen sent this to us, it's an order proposed by the AOGCC to replace the
well integrity related language in the current Area Injection Orders. Listed
below are comments, not sure who is coordinating getting these in front of
Winton/Jim. Overall, looks okay from an Operations perspective. We do have a few
comments, but could live with the current proposed language. Note the proposed
public hearing date is November 4.
The following language does not reflect what the slope AOGCC inspectors are
currently requiring us to do:
"The mechanical integrity of an injection well must be demonstrated before
injection begins, at least once every four years thereafter (except at least once
every two years in the case of a slurry injection well), and * before* **
1 ~¡: '1
1 f\ /,., Q 1")f\f\A 1 1 .f\Q A l\Æ
[Fwd: Re: [Fwd: AOGCC Proposed WI Lan!.
~ for Injectors]]
returnj_ng a well to service following a workover affecting mechanical integrity."
After a workover, the slope AOGCC inspectors want the well warmed up and on
stable injection, then we conduct the AOGCC witnessed MITIA. This language
requires the AOGCC witnessed MITIA before starting injection, which we are doing
on the rig after the tubing is run. Just trying to keep language consistent with
the field practice. If "after" was substituted for "before", it would reflect
current AOGCC practices.
It would be helpful if the following language required reporting by the "next
working day" rather than "immediately", due to weekends, holidays, etc. We like
to confer with the APE and get a plan finalized, this may prevent us from doing
all the investigating we like to do before talking with the AOGCC.
"Whenever any pressure communication, leakage or lack of injection zone isolation
is indicated by injection rate, operating pressure observation, test, survey,
log, or other evidence, the operator shall * immediately*_** notify the
Commission"
This section could use some help/wordsmithing:
"A monthly report of daily tubing and casing annuli pressures and injection rates
must be provided to the Commission for all injection wells indicating well
integrity failure or lack of injection zone isolation."
Report content requirements are clear, but it's a little unclear what triggers a
well to be included on this monthly report. Is it wells that have been reported
to the AOGCC, are currently on-line and are going through the Administrative
Action process? A proposed re-write would be:
"All active injection wells with well integrity failure or lack of injection zone
isolation shall have the following information reported monthly to the
Commission: daily tubing and casing annuli pressures, daily injection rates."
Requirements for the period between when a well failure is reported and when an
administrative action is approved are unclear. This document states "the operator
shall immediately notify the Commission and submit a plan of corrective action on
a Form 10-403". If we don't plan to do any corrective action, but to pursue an
AA, does a 10-403 need to be submitted? The AOGCC has stated they don't consider
an AA as "corrective action".
Let me know if you have any questions.
Joe
-----Original Message-----
From: Kleppin, Daryl J
Sent: Wednesday, September 29, 2004 1:37 PM
To: Townsend, Monte Ai Digert, Scott Ai Denis, John R (ANC) i Miller,
Mike Ei McMullen, John C
Subject: FW: Public Notices
FYI
-----Original Message-----
From: Jody Colombie [ mailto:jody colombie@admin.state.ak.us
Sent: Wednesday, September 29, 2004 1:01 PM
Subject: Public Notices
Please find the attached Notice and Attachment for the proposed amendment of
underground injection orders and the Public Notice Happy Valley #10.
Jody Colombie «Mechanical Integrity proposal. ZIP» «Mechanical Integrity of
Wells Notice.doc»
2 of3
IIì j") S2 j") 1ì1ìL1 1 1 . (\Q ^ 1\ ¡f
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Alaska, Inc.
Kelli L. Hanson
Production Engineer
700 G Street, ATO-1764
Post Office Box 100360
Anchorage, Alaska 99510-0360
Telephone 907-265-6945
dill·- C)-\ 0
~CJ \95-~
July 26, 2004
Alaska Oil and Gas Conservation Commission
Attention: Mr. James Regg, mc Manager
333 W. 7th Avenue Suite 100
Anchorage, AK 99501
Subiect: CDl-19A Class IT Disposal Well Fracture Growth Estimate
Dear Mr. Regg:
This letter is in response to your May 5th letter requesting an estimate of fracture growth
in the Alpine Class IT Disposal Well CDl-19A. To comply with your request, a
pressure fall-off (PFO) test was performed on the CDl-19A well in June 2004.
The PFO data has been analyzed. Fracture extension and closure were evident in the
early time fall-off data. The fracture resulting from the test closed at 7.58 minutes post
injection at 6,492 psia, corresponding to a fracture gradient of 0.716 psi/foot. The
gradient has increased since the initial step rate test (0.665 psi/foot) as a result of
changes in well injectivity index and poroelastic effects. The fracture half-length was
estimated to be 356 ft. A Nolte-Smith plot of the injection data indicates the fracture
grew in length, but was height constrained. Please see the attached report for further
details.
If you have any further questions, please call me at 265-6945.
Sincerely,
J(J1;. L· 14-~~
rAfT-
i~ç
. \..""",
'Uti 0
J ¡L f::
''-'oOIi
l~..J J \
Kelli L. Hanson
CDl Production Engineer
if~Ja$¥. a O·
1 .
"'"
-~
'- .
~
ConocoPhillips
Alaska, Inc.
Date:
July 26, 2004
Subject:
CDl-19A Pressure Fall-Off Summary
From/Location: Kelli Hanson, Alpine Production Engineer
ATO-1764
Telephone:
265-6945
Test Overview -A pressure fall-off test was performed on Alpine's Class II Disposal Well,
CDI-19A on June 19,2004. Dual Panex gauges were run and set in a XN lock in the
XN nipple at 10,778' RKB. Little Red Services pumped 850 bbls of seawater down
the well at 1.5 bpm. Following seawater injection, the well was freeze protected with
20 bbls diesel at 1.0 bpm. The well was shut in and static bottom hole pressures were
recorded.
Analvsis - Attachment 1 shows the pressure behavior recorded by the down hole pressure
gauges. CDl-19A remained shut-in for approximately 4 days.
Saphir pressure transient analysis software was utilized to analyze the data.
Conventional and pressure derivative calculations were performed to calculate
well/reservoir properties (permeability, skin, and wellbore storage coefficient) fromthe
test. Assumed data for the analysis are given below.
- "
Porosi ty (<I» 0.15
Viscosity (µ) 0.499 cp
Fonnation Volume Factor (Bw) 1.0 RB/STB
Well Radius (rw) 0.2615 ft
Total Compressibility (Ct) 4.109 x 10-b l/psi
Depth (D) 11,465' MD (9,062' TVDSS)
Pump Rate (Q) 1.5 bpm (2,160 BPD) water, 1 bpm
(1,440 BPD) diesel FP
A log-log plot of M> versus ~t was constructed and is shown in Attachment 2 with the
pressure derivative. A Horner plot is shown in Attachment 3.
The early time data was also analyzed to detennine fracture properties. A plot of
pressure versus the square root of time (Attachment 4) was prepared to identify
fracture extension and closure.
Finally, a Nolte-Smith plot was created to model the fracture growth characteristics
during injection. This plot is shown as Attachment 5.
, '
CD 1-19A PFO Summary
Page 2
Results - The following table summarizes the well/reservoir properties obtained from analysis of
the pressure fall-off data.
k.h 745 md.ft
Skin (s) 2.96
Wellbore Storage Coeff. (C) 0.211 bbl/psi
Fracture Closure Pressure 6,492 psia @ dt=7.58 min
Fracture Gradient 0.716 psi/ft
Fracture Half-Length (Xf) 356 ft
Fluid Efficiency 1%
Pressure transient analysis yielded a k.h value of 745 md.ft. If it is assumed that most
of the fluid entered the top two perforation sets (higher injectivity index), the thickness
(h) would be 30-45 feet, resulting in a penneability of 17-25 md. This estimate
compares favorably with the calculated log model liquid penneability of 21 md.
_~u_."~."...~·~-'r.·""",."",,,,,
The log-log plot shows a classic damaged well response and a skin of 2.96. Near-
well bore damage was expected due to the frequent disposal of dirty fluids. The skin
has increased since the initial PFO, run 6/4/2000. Evaluation of that test demonstrated
the well was slightly damaged, skin = 0.65. The initial test was conducted prior to
regular disposal operations.
During a step rate test on September 17, 2000, the fonnation fracture pressure was
observed as 6,035 psi using a 9,062' column of 9.2 ppg brine and 1,700 psi on the
wellhead. Using this data, a fracture gradient of 0.665 psi/ft was calculated for the
reservoir. During nonnal operations, injection occurs above this fracture pressure, thus
hydraulically fracturing the well. Refemng to the square root of time plot, Attachment
4, a fracture was observed to close at dt=7.58 minutes and 6,492 psia, yielding a
fracture gradient of 0.716 psi/ft. The elevated fracture gradient can most likely be
attributed to a reduction in well injectivity and poroelastic effects due to the long
pumping period.
Injection was assumed to enter the fonnation through the top two perforation sets, thus
a fracture height of 35 feet was used in the early-time analysis. A regression fit to the
early-time fall-off data resulted in a fracture half-length of 356 feet and a fluid
efficiency of 1 %.
Attachment 5 shows a Nolte-Smith plot from the injection data. The quarter slope
indicates a Perkins and Kern system, i.e. a wedge-shaped contained fracture, which is
growing in length.
CD1-19A PFO Summary
Page 3
Conclusions -Due to disposal injection operations, the near wellbore area has been damaged.
Fractures extending past the damage zone have allowed continued injection. The data
suggests the fractures extend in length, but are vertically contained.
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CD1-19A Panex Data
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~
Log-Log plot
""
"-"
Attachment 2
Company CPAI
Well CD1-19A
Field Alpine
Test Name I #6/28/04 PFO
1E+5
1E-4
1E-3
0.01
0.1
10
100
1000
10000
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ïñ
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c:
ro
0.
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dt [hr]
top gauge (Mod) (Mod) fall-off #3
Rate 0 STBID
Rate Change 1440 STBID
P@dt=O 6577.49 psia
Pi 4522.83 psia
Smoothing 0.1
Selected Model
Model Option Standard Model
Well Storage + Skin
WBS Type Changing
Reservoir Homogeneous
Boundary Infinite
Results
TMatch 2.09 [hr]**-1
PMatch 0.00734 [psia]**-1
C 0.211 bbl/psi
Ci/Cf 0.357
Alpha 22400
Skin 2.96
Delta P Skin 403.857 psi
Pi 4522.83 psia
k.h 745 md.ft
k 21.3 md
Rinv 1970 ft
Test. Vol. 1.13919E+7 Barrels
Saphlr v3.10.09 - 07-2004 1-19A PF054 hrs lead.ks3
~
KAPPA
ïñ
B
a.
~,
Horner plot
~
Attachment 3
Field Alpine
Test Name / # 6/28/04 PFO
Company CPAI
Well CD1-19A
+++ + + +
6000-
5000-
I I I I I I I I I
I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I
2 3 4 5
log(tp+dt)-Iog( dt)
top gauge (Mod) (Mod) fall-off #3
Rate 0 STB/D
Rate Change 1440 STB/D
P@dt=O 6577.49 psia
Pi 4522.83 psia
Smoothing 0.1
Saphir v3.10.09 - 07-2004 1-19A PF054 hrs lead.ks3
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Attachment 4
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(
Attachment 5
Net Pressure Plot
#9
CUI-IYA
Jim,
As a follow-up to your request dated May 5, 2004 and our follow-up phone
conversation concerning frac growth estimate on CDl-19A per Area Injection Order
18A. The status of the work required to fulfill the request via PTA using a down
hole injection well pressure falloff is as follows:
Ran down hole gauges on June 19th.
Injected seawater into well and shut-in.
Pulled Gauges June 26th.
We are currently in the process of analyzing the SPFO data and will have a report
out by July 23rd. Please let me know if you have further questions.
Chris Alonzo
Alpine Engineering Supervisor
ConocoPhillips, Alaska
(907) 265-6822
~.þ..1.:~..~..§...~...9.:~.S?!2.~.?~~.S;..?~S?~gp}?:.~..~J..~..P§'._~...S;..?0
1 of 1
7/12/20042:29 PM
#8
AI1A.SIiA. OIL AND GAS
CONSERVATION COMMISSION
FRANK H. MURKOWSK', GOVERNOR
333 W. -¡rn AVENUE, SUITE 100
ANCHORAGE, ALASKA 99501-3539
PHONE (907) 279-1433
FAX (907) 276-7542
May 5,2004
Mr. Chris Alonzo
Alpine Engineering Supervisor
ConocoPhillips Alaska, Inc.
P.O. Box 100360
Anchorage, AK 99510-0360
Dear Mr. Alonzo:
Disposal Injection Order 18 dated April 19, 1999, and Area Injection Order 18A dated April 18,
2000, address specific requirements for waste injection into specific disposal injection intervals
within the Colville River Unit. Rule 9 of DIO 18A requires an annual perfonnance report that
includes "rate and pressure performance, surveillance logging, fill depth, survey results, and
volumetric analysis of the disposal storage volume, estimate of fracture growth, if any, and
updates of operational plans." The Alaska Oil and Gas Conservation Commission
("Commission") received from ConocoPhillips Alaska, Inc. ("ConocoPhillips") the 2003
Disposal Performance Report for the Alpine Oil Pool within the Colville River Unit. The report
is dated March 17, 2004, and summarizes pressure and rate performance, surveillance, and
testing of disposal injection Wells WD-2 and CD 1-19A associated with Alpine Oil Pool
development during calendar year 2003.
The Commission has completed its review of the 2003 Disposal Well Performance Report.
Regarding Well CDI-19A, ConocoPhillips states: "all fluid injection to date has occurred above
fracture pressure." There is no estimate of fracture height and length as required by Area
Injection Order 18A, Rule 9. ConocoPhillips notes that no data was collected to estimate fracture
height and fracture length.
Please provide the Commission with a summary of how ConocoPhillips' intends to resolve this
deficiency in the annual surveillance requirements of Area Injection Order 18A.
Sincerely,
~B J.?~C1
James Regg l (
UIC Manager
cc: John K. Nonnan, Chair
Daniel T. Seamount, Jr., Commissioner
#7
1'II11I,IP5
œ
~
PHilliPS Alaska, Inc.
A Subsidiary of PHILLIPS PETROLEUM COMPANY
\~
Alpine Development Project
Alpine - HSE - ALP 14
P. O. BOX 196860
ANCHORAGE, ALASKA 99519-6860
ONLY
Chair I
C-omm I
~C-omm
. File
Telephone 907- 670-4200
Facsimile 907- 670-4778
May 12, 2002
R"};, E· (-..~ 1: I V .-.
.-.~ _ t
!) 1.. ?Ufìf¡?
; , I... Vb,.
......~ t
Cammie Taylor
Alaska Oil and Gas Conservation Commission
3001 Porcupine Drive
Anchorage, AK 99501-3192
Alaska OH & Gas Comt Commission
AnchoraQ8
RE: Administrative Approval for Injection of Treated Camp Effluent and Approved
Non-hazardous Fluids in to Alpine Sea Water Flood Wells
Dear Ms. Taylor:
The Alpine facility is a stand-alone development, geographically isolated from neighboring
infrastructure. There are no permanent roads connecting Alpine to other facilities. Access is-
by winter ice road during the months of February through April, and by aircraft only during
other times of the year. As a result of this isolation, the Alpine facility must be self-sufficient
and equipped with on-site facilities and procedures to effectively manage all manner of
contingencies, particularly in the summer months.
Under normal operating conditions, treated camp effluent and other approved non-
hazardous fluid waste, such as snowmelt, stormwater, sump fluids, and wash waters are
disposed of by injection in the permitted Class 1 well, WD-02. Camp effluent is hard-piped_
to the Class 1 disposal well, while the other wastes fluids are typically disposed in batch
loads offloaded in holding tanks associated with the well.
Area Injection Order 18A states Class 2 EOR "fluids may be injected for purposes of
pressure maintenance and enhanced recovery" and does not describe or limit the
appropriate fluids. In testimony, the Alpine recovery process has been described as a "water
alternating gas" (MWAG) process.
With this letter, Phillips Alaska, Inc. respectfully requests administrative approval by the
Commission to utilize a blend of seawater and treated camp wastewater effluent as the '
water phase of the Alpine recovery process, injecting these fluids into Class 2 EOR wells on-
an as needed basis, such as periods when well WD-02 is not operable due to annual
mechanical integrity testing (MIT), maintenance activities, or in the event of an operational
failure of WD-02.
Phillips Alaska, Inc. is a Subsidiary of PHilLIPS PETROLEUM COMPANY
Administrative Approval for :",-.;tion of Treated Camp Effluent
May 12, 2002
Page 2
'''-'''
The fluid would be injected using the existing grey water pumps to feed the SWI system.
The grey water pumps maximum capacity is approximately 40 US GPM, thereby minimizing
any potential to significantly dilute the seawater. The anticipated blend ratio, based on
normal daily rates, would be approximately one hundred parts seawater to one part effluent.
wJ
\J !0Ú)
t ( L.t7L'
The injection water would be distributed to various water flood wells currently taking SWI and
completed in the Alpine formation.
PAl experts have reviewed the physical properties of the anticipated effluent blend ratio, and
more concentrated effluent blend ratios. Given normal operating conditions, it is not
anticipated that the proposed mixture will be detrimental to the reservoir, surface, or
subsurface facilities. The proposed dilution ratio will be high enough to reduce oxygen
content to levels where accelerated corrosion is not a concern. Corrosion levels will be
monitored to assure actual conditions are as anticipated.
In the reservoir, the difference between the proposed mixed water injectant and seawater is
not expected to have any significant impact on injection performance or hydrocarbon
recovery. While the mixed water bacterial content will be higher than in seawater alone, the
Alpine recovery process is expected to have relatively low water throughput, hence, it is
expected there will be little impact to produced fluid hydrogen sulfide levels at the end of field
life.
Included for your review is analytical for a representative sample of treated effluent from the
Alpine waste water treatment plant (WWTP) demonstrating the waste in non-hazardous.
Also included is a copy of an approval previously granted to Kuparuk Operations for injection
of treated effluent for EOR, illustrating this disposal request is consistent with other approved·
practices.
Thank you for your consideration of the proposal. Please do not hesitate to contact us at
(907) 670-4200 should you have any questions or additional information needs.
Sincerely,
~~
Thomas Manson/Michael Nelson
Field Environmental Coordinator
Attachments:
Analytical Results
Letter from AOGCC to ARCO Alaska (Now Phillips Alaska)
Phillips Alaska, Inc. is a Subsidiary of PHilLIPS PETROLEUM COMPANY
#6
....~
~
Decision Document
July 29, 2002
Request: Authorization to periodically mix treated wastewater effluent with Class II enhanced oil
recovery (EOR) injection fluids when the primary disposal well (WD-02) is unavailable
because of maintenance or in the event of failure.
Company: Phillips Alaska Inc.
Date: May 12, 2002, letter
Relevant Data and Considerations in the Decision
I. Chemical make-up of effluent stream to be mixed with EOR fluids; is it hazardous? Does it
exhibit characteristics of hazardous wastes (per 40 CFR 261.20 through 261.24)?
a. Analysis provided by Phillips at AOGCC request documents the chemical make-up of the
EORjZuid, and the EORjZuid with treated wastewater. The estimated mix of 1% effluent
with seawater injectant will not significantly impact properties of the seawater.
2. Susceptibility of formation to react negatively with EOR fluid mix; will it cause plugging or other
reservoir impacts that will prevent efforts to achieve ultimate recovery?
a. The characteristics of the treated effluent are consistent with other aqueous jZuids used
for EOR injection. The estimated mix of 1% effluent with seawater injectant will not
significantly impact properties of the seawater
3. Threat to fluid movement from intended confined zone, and potential for fluid mixture to change
potential for movement? If the fluid mixture would change the potential for movement, then a
detailed reassessment of the well construction and an AOR would be needed.
a. Nothing in the jZuid make-up, fluid quality, or injection process compromises the well
integrity. The process is a simple mixing ofjZuid streams.
4. Alternatives to the proposed action?
a. Facility shutdown;
b. Developing additional surface storage as a buffer when it is not possible to use the WD-
02 well for disposal;
i. Lined pits - an unacceptable approach for temporary storage given the injection
capabilities and the potential risk to the surface environment (and well
documented concerns for such).
ii. Alpine's reduced footprint leaves little space for buffer tanks to provide storage
of the wastewater effluent
5. Logistical issues and the significance of such?
a. Alpine is a remote development that is accessible only by air in the summer, and by ice
road in the winter months (January - May). Transportation from Alpine in either case
would increase handling of the waste that is historically where most large volume
releases occur.
6. Performance standards and compliance responsibilities
a. Sampling and analysis of representative mixture;
b. Retention of records; available to AOGCC upon request;
c. Volumes of treated wastewater mixed with EORjZuids and injected in wells on Forms 10-
406 (Monthly Injection Report) and 10-413 (Annual Injection Report).
7. Other Factors
a. Kuparuk Field approved to mix effluent waste water in EOR
#5
""~/
90"7-670-
Jul07 200~ 8:39PM
PAt CNST - ALPINE
..~
¡FAX
FROM:
Tom Manson
A/pine Production Facility
HEST-ALP 14
P.O. Box 196860
Anchorage, AK 99519
TO:
Jack Harts
Or Pouch
Phone
Fax
(907) 670-4200
907 670..4778
Phone
Fax
793-1232
276-7542
I CC:
I REMARKS: D Urgent
181 For your review D Reply ASAP 0 Please Comment
Mr. Harts,
Randy Kanady, my alternate, asked me to forward information on our wastewaster treatment
plant suspended soils (85) and on SS for the seawater we are injecting into our EOR wells.
This information is in support of the Phillips Alaska, Inc. request to inject wastewater into our
seawater water flood wells (Class 2R) on an as needed basis.
I have attached a spreadsheet of the May and June SS for the wastewater plant effluent and
the Seawater Treatment Plant monthly report for March - June and a report showing the
average todate for July 2002.
Please contact us if you have any further questions.
Tom Manson
Alpine Environmental Coordinator
RECEIVED
JUL 8 2002
Alaska on & Gas ConI. Commission
And10fage
Jul 07 2002 8:39PM p~T CNST - ALPINE
90"'-670-4778
p.2
~,
"-'"
Alpine Sewage Treatment Emuent Suspended Solids
The following is a ·list -of the ·suspended 'solids, 1n mgA~ leaving the Alpine wastewater
plant. Please ootetbat these figures only show suspended solids, not total solids. We
t d est fj dis lved r ds
present '¡ o·not t . or so SOl
Date 8.S., Date 8.S.
mgI1 mg/l
5/1 40 6/1 88 Total flow for May 'WaS 835,230
5/2 100 ·6/2 66 gallons for ·an average of26,943
5/3 60 ·6/3 84 gallons per ·day. 2-6,943 x 8.34=
5/4 100 6/4 6"8 224,705 Ibs of water per day. The
5/5 160 6/5 30 average eft1uent suspended solids
5/6 240 6/6 52 per day in May was 85.2 mg/L
5/7 140 .6/7 132 (224,70S/1,~,OOO) x 85.2=19.1
5/8 na ·618 88 Ibs of.suspended solids per day in
5/9 260 '6/9 80 the efiluent. Or, ·about 592 Ibs, for
5/10 120 6/10 28 the month·of May.
5/11 200 6/11 18
5112 118. 6/12 12
5/13 8 ·6/13 94
5114 21 6/14 1"6
5/15 52 6/15 44
5/16 9 6/16 28
5/17 4 6/17 34
S/18 46 '6113 12
5/19 9 6/1-9 22
5/20 15 6/20 78
5/21 28 6/21 30
5/22 52 6/22 10
5123 50 ·6/23 36
5/24 174 6/24 60
5/25 28 6/25 43
5126 24 6/26
5/27 126 6/27
5/28 177 ·6/28
5/29 na 6/29 #
5/30 76 6/30
5/31 66
Avg 85.2 . Avg 50.3
. ._.____~~.._._....____~._.~.__._... .. ____..._________ ..... ___._~ :_¥_____.__. _...__.,_... M _..______._____..._. .--.-....----
~ ;
î i
i
TREATED I¡ EOUIPMENT I
RUN 5CHE UNSCHEI
SEAWATER (TOTAL) 5515704 BBLS11 D D
SEAWATER (KRU) 3385674 BBLS! I FEED PUMP A 0.00 0.00 O.OO!
SEAWATER (ALPINE) 2130030 BBLS[I FEED PUMP B 744.00 0.00 0.001
i I TEMPERATURE 56 DEG F\ I FEED PUMP C 744.00 0.00 O.OO(
I (AVERAGE) !! FEED PUMP D 0.00 0.00 O.OO!
" PRESSURE 333 PSIGll
11 (AVERAGE) ! I TRANSFER 743.50 0.00 O.OO!
11 GAS RATIO 7.22 SCF/BBII PUMP A
(AVERAGE) Lj I TRANSFER 0.00 0.00 O.oo
DISSOLVED OXYGEN 15 PPS! I PUMP B
:1 (AVERAGE) I i TRANSFER 744.00 0.00 O.OO!
il FREE CHLORINE 0.05 PPMII PUMP C
:1 (AVERAGE) 0.001
__ /:!TSSAVERAGE 0.7 MG/LI CLARIFIER 0.00 0.00
·1 ¡I PUMP ¡
.-:-'-:~'-:':"';' ... .~..:.·.·.·.:·.~·1~;";'':.''.---''M''.~'''''.''---.':_-'.~:_.:..'.',_.. .... . ¡
I
PERMIT ! I CLARIFIER A 0.00 0.00 O.OO!
" FOR COMPLETE ¡ I CLARIFIER B 0.00 0.00 O.OOi
MONTHLY PERMIT 15-005
SUMMARY, SEE 744.00 0.00 O.OO!
'I NPDES DISCHARGE j STRAINER
MONITORING I 5-003 0.00 0.00 744.00
REPORT I STRAINER
. -·1...·.·:.:.·.·..:;:~*..":'""·'.-~·;-_:_-__:__:__-·; ._.. .~.
UTILITIES ¡¡FEED HEX A 0.00 0.00 744.00
'ì
'I TOTAL FUEL GAS 133,817 MSCFil FEED HEX B 744.00 0.00 0.00
, ¡
POWER GENERATED 3,521,000 KWHlllNTAKE HEX A 0.00 0.00 0.00
KUPARUK SEAWATER TREATMENT PLANT
MONTHLY REPORT FOR: MAR-02
As ofOS-JUL-Q2 13:44:10.9
. _ NSK Lab Chemist
":1' " 07/0512002 01 :44 PM
-rrr{·Pll~l~f:'·:f- To: ALP Env CoordlPPCO@Phlllips
cc:
Subject: C:\TEMP\STP _MON...,MAR..02.J .HTML
'"-'
'-.
p.3
907-670-4778
Jul 07 2002 8:39PM PAl CNST - ALPINE
Jul 07 2002 8:39PM PAl CNST - ALPINE
'-'
907-670-4778
..... I.' l..j...... ." NSK Lab Chemist
f ~ ~.~ .
. ' .: ·07/05/2002 01:43 PM
- . . '0'
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Subject: C:\TEMP\STP _MON_APR-02_1.HTML
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p.4
KUPARUK SEAWATER TREATMENT PLANT
MONTHLY REPORT FOR: APR-oZ
As ofOS-JUlr02 13:43:12.5
'r·····-·---····· .....------...--.--....----.-. - .....---....
:¡
¡¡TREATED
:1 SEAWATER (TOTAL) 7409783
j! SEAWATER (KRU) 4753774
j SEAWATER 2656009
¡ (ALPINE)
\1 TEMPERATURE
!I (AVERAGE)
:' PRESSURE
:1 (AVERAGE)
:1 GAS RATIO
¡ (AVERAGE)
:1 DISSOLVED
~!OXVGEN
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II (AVERAGE)
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. ¡ '""'=~7.''''· --.-~~~"'='"'="''"......_~,,="~"~~_____.
¡I PERMIT
11 FOR COMPLETE
I¡ MONTHLY PERMn
; ¡ SUMMARY, SEE
11 NPDES DISCHARGE
: I MONITORING
:! REPORT
6.39
0.04
,.-...-.-..---..--.-.--......... ..__.-._._...~-~--.
: UTIUTIES
.----.
.------.
..~._------_._. .-.-..- . ----..-.. .....-...--.-...-..-
54
;
! EOUIPMENT
BBLSi
BBLSr FEED PUMP A
BBLS: FEED PUMP B
¡ FEED PUMP C
DEG F¡ FEED PUMP D
RUNSCHED
0.00
719.00
719.00
0.00
PSIGi TRANSFER PUMP 719.00
iA
SCF/BS¡ TRANSFER PUMP 0.00
LI B
PPB¡ TRANSFER PUMP 719.00
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0.00
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0.00
0.00
0.00
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0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00 0.00 0.00
0.00 0.00 0.00
0.00 0.00 0.00
719.00 0.00 0.00
51.00 0.00 668.00
0.00
719.00
0.00
0.00
0.00
0.00
719.00
0.00
0.00
~~~
Jul O~ 2002 8:39PM PAT CNST - ALPINE
907-670-4778
'__J
.' NSK Lab Chemist
1.. ":4::l-' ..
. , . _ . . 07/05/2002 01 :42 PM
. .-.~,.~.. .'. - To: ALP Env CoordlPPCO@ Phillips
oc:
Subject: C:\TEMP\STP _MON_MAY-02_1.HTML
KUPARUK SEAWATER TREATMENT PLANT
MONTHLY REPORT FOR: MAY-02
M of05-JUL.02 13:41:30.0
.1·..··.. . -.....-...---..--..-.. ". .. ..... .......-.--..-..-..-. ...
HTREATED
i SEAWATER (TOTAL)
I SEAWATER (KRU)
II SEAWATER (ALPINE)
:1 TEMPERATURE
¡I (AVERAGE)
.!I! PRESSURE
¡ (AVERAGE)
;1 GAS RATIO
II (AVERAGE)
II DISSOLVED OXYGEN
;1 (AVERAGE)
!! FREE CHLORINE
~:¡ (AVERAGE)
;¡TSSAVERAGE
¡ Ii ....:~,.".... .... .~~-".-.,.,-,.",~.-.....-.-.......,..._- .-................---..." .......-~,.'"
:" PERMIT
i
i\ FOR COMPLETE
II! MONTHLY PERMIT
¡ SUMMARY, SEE
;, NPDES DISCHARGE
¡ I MONITORING
¡ ¡ REPORT
~ Í
_w_.___._...._..__ _...
8267798
5536104
2731694
55
6.46
0.03
t f'":.,~=.'::.~......'t'f'Pt'.:".~~~..~..... ... .~:..~...~'"'1':.~':7:.~-;-:--~~..~:-..~-:.
i
.1 UTIUTIES
: TOTAL FUEL GAS 113,629
: POWER GENERATED 1,897,000
p.5
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UNSCHE
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II CLARIFIER B
: 15-005
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15-CJ03
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MSCFj I FEED HEX B
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RUN SCHE
D
0.00 0.00
744.00 0.00
343.50 0.00
400.50 0.00
744.00 0,00
0.00 0.00
744.00 0.00
0.00 0.00
0.00 0.00
0.00 0.00
744.00 0,00
744.00 0.00
0.00
744.00
0.00
0.00
0.00
0.00
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I ;
I TREATED !·EOUIPMENT RUN SCHE UNSCHE
II· SEAWATER (TOTAL) 6853557 BBLSI D D
:1 SEAWATER (KRU) 4498566 BBLS FEED PUMP A 0.00 0.00 0.00
,I SEAWATER (ALPINE) 2354991 BBLSI FEED PUMP B 702.50 0.00 0.00
I ;
¡I TEMPERATURE 57 DEG pi FEED PUMP C 193.00 0.00 0.00
11 (AVERAGE) ! FEED PUMP D 512.50 0.00 0.00
;1 PRESSURE 317 PSIGj
ij (AVERAGE) ¡ TRANSFER 704.50 0.00 0.00
;1 GAS RATIO 7.01 SCF/BBj PUMP A
:1 (AVERAGE) Li TRANSFER 631.25 0.00 0.00
:1 DISSOLVED OXYGEN 25 PPB! PUMPS
I ;
! (AVERAGE) i TRANSFER 70.00 0.00 0.00
:¡ FREE CHLORINE 0.04 PPM! PUMP C
:1 (AVERAGE)
~·¡TSSAVERAGE 2.8 MG/LJ CLARIFIER 0.00 0.00 0.00
,[ j PUMP
.!' ..'".,...,.........~~.-~'''"=.".,~.~.=~,=w...~~=.,.._."...--- 1
:1 PE~MIT ¡ CLARlFIERA 0.00 0.00 0.00
'I FOR COMPLETE 1 CLARIFIER B 0.00 0.00 0.00
:1 MONTHLY PERMIT
;1 SUMMARY, SEE ; S-CJOS 703.50 0.00 0.00
)1 NPDES DISCHARGE STRAINER
:1 MONITORING 5-003 703.50 0.00 0.00
'I REPORT STRAINER
~ I .. ··..."...··-f..~ ........_..~_........:"'-....-:-:;...:-=:.-.:.:~';'"_.;~~:-:;-;-;.-.:::-:-~.~.~. ..~. ~~ '_.,._.w
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:1 UTI LInES FEED HEX A 0.00 0.00 720.00
:1 TOTAL FUEL GAS 121,618 MSCF FEED HEX B 702.00 0.00 0.00
,I POWER GENERATED 3,507,000 KWH INTAKE HEX A 0.00 0.00 0.00..
KUPARUK SEAWATER TREATMENT PLANT
MONTHLY REPORT FOR: JUN-02
As vf05-J1JL..02 B:16:39.7
.. -I-.!..' .1 .. NSK Lab Chemist
H_ .,07/05/200201:40 PM
;H'.t:~:. . . r
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Subject: C:\TEMP\STP _MON_JUN-02_1.HTML
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p.6
90":1-670-4778
Jul 07 2002 8:39PM ppT CNST - ALPINE
,
Ju 1 '07 2002 8: 39PM ppT CNST - ALP I NE
907-670-4778
~
... ._ .' . _ _ NSK Lab Chemist
o· .' ~_ _.."1" +: 07105/200201:15 PM
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cc:
Subject: C:\TEMP\STP _MON_JUL-Q2.-1.HTML
p.7
KUPARUK SEAWATER TREATMENT PLANT
MONTHLY REPORT FOR: JUL-02
.As ofOS-JUL.02 13:03:48.8
¡r-O-.---.-..-----.-----------.---O-O--.---------------------! 1"-----------0-_0-_-..--.-.-..----.-_-00------0.-.-00
. ¡ TREATED
i SEAWATER (TOTAL)
i. SEAWATER (KRU)
i II SEAWATER (ALPINE)
J, TEMPERATURE
il (AVERAGE)
'I
j) PRESSURE (AVERAGE)
í GAS RATIO
I (AVERAGE)
I DISSOLVED OXYGEN
i¡ (AVERAGE)
j' FREE CHLORINE
! (AVERAGE)
-:> i TSS AVERAGE
.---_.. .-....---..-.......--..........-...-.-..- ..------.-.................----.---.--..
PERMIT
FOR COMPLETE
. MONTHLY PERMIT
, SUMMARY, SEE NPDES
¡DISCHARGE
¡ MONITORING REPORT
: UTIUTIES
: TOTAL FUEL GAS
. POWER GENERATED
'·-~I"'-.~:·I:r~ ~~~.":: :.:~r:~7'-::-:-:-~· ~:-::-:-:=::=::: ::;~...::._ __...:~.: .:.....;.:.:.-~
697879
544492
153387
59
0.04
12,440
469,000
i 10EOUIPMENT
BBLSil
¡ i
BBLS¡ I FEED PUMP A
BBLSI I FEED PUMP B
DEG Fi ¡ FEED PUMP C
¡ i FEED PUMP D
¡ i
PSIGil
SCF/BB¡ITRANSFERPUMP 78.25
LilA
PPsl I TRANSFER PUMP 74.75
i!B
PPM: ¡ TRANSFER PUMP 0.00
¡!C
MG/Lil
.! CLARIFIER PUMP 53.75
! CLARIFIER A 53.75
: i
; ¡ CLARIFIER B 53.75
265
7.1
28
9.9
! ¡
, t 5..005
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; I S-CJ03
i I STRAINER
, ¡
, ;
MSCF¡ I FEED HEX A
KWH!, FEED HEX B
. i INTAKE HEX A
0_
RUN SCHED
0.00
79.00
96.00
0.00
96.00
96.00
0.00
77.25
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0,00
UNSCHE
D
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
96.00
0.00
0.00
. ,
Ja~:)B-OZ 11:00am' From-Ph¡//¡psAKSafety-Trn,
-. ~ 9076597861 T-315 P.D5/D7 F-9Z8
~ U ~ ~ ~ lW ~ ~11~@ ~lA\ ~~::fI';;;~~~ñ~
- ¡'"
I
,\L~\.Sli.c\ OIL ,\YD Gl\S
CONSEII.\',,\.TION CO~I~IISSI0N
~1·POJCUPJNe; OAM
,A.NC...afUGE. AL.4SU t9!0t.:s11a
p...oN€. (9Øn Z7t-1t3:1
TEL£C:CP"l': twIIm-7s.a
March 4, 1991
Mark. D l"UrDID
Kupandc: OperaûoD.S Representative
ARCe AJaska
P 0 Bax 100360
AÞcborage, AK 99510-0:160
RE: Use of Kuparuk Waste Water Trcatmcøt Plant (WWTP) treated
ecnueDt to perl%1llnently ~ugœent water injecûoD supply at CPF-l,
Kuparuk River Unit.
Dear Mr. Drumm:
We have evaluated your proposal of February 5 t 1991 to use WWTP
treated einUelll to augment the EOa water injection supply system at
Cl'F-l.
The Commission has reviewed the chemical amùysis that you proVided.
Cor the WWTP treated ecnuel1t. Based. upau that 8.%I81ysis., the
Commis$ioD. has caacluded. that the chemic:a1 characterisûcs of the
treated eCfJuea.t are similar to other fluids used in the EOR project.
In accordance with the provisions at AtO 2 J w. hereby approve the. us.
or WWTP cffiuents to permanently augmeat the water injectioa supply at
CPF-l. As a CODcUÛ9D.. at this app~va19 you will continue to u.œ1ne
the efnuect todelDQQstrate its continued suitability r~r EOa Injectioa..
Capies or the cbemical aaaJysis sbaJl be provided to AÇGCC as
requested.
SiAceNIy.
David W. Jo
Chairmaø. AOG
cc: Huale! Scott
.
#4
Re: S(0nn~ater S~·Jt.. Disposal Approval
It
~--
~
Subject: Re: Stormwater Silt Disposal Approval
Date: Wed, 16 Aug 200009:24:17 -0800
From: Wendy Mahan <Wendy_Mahan@admin.state.ak.us>
Organization: doa-aogcc
To: Donnelly&Manson <n1508@ppco.com>,
Dan Seamount <dan _ seamount@admin.state.ak.us>,
Camille Oechsli <cammy _ oechsli@admin.state.ak.us>
f\ \ Ü \'6 f::\
Mr. Manson,
The Commission will grant a waiver under 20 AAC 25.450(a) to allow the
Class II injection of nonhazardous silt that has settled out of snowmelt
collected at the Alpine Development Project this summer. Although there
is a Class I well on site, you have stated that it is currently
operating at maximum capacity with the construction/startup activity.
In subsequent conversation with myself, you indicated that the current
containment takes up a lot of space that Phillips would like to use, and
that once construction activities are complete, the pad will be graded.
You stated that the construction activities created what you consider to
be an unusual situation with increased traffic and the piling of snow
onto the gravel pad from ice pad areas in an effort to minimize tundra
impacts. In the future, you intend to use the Class I well to inject
this or similar wastes.
Due to the extenuating circumstances created by Alpine startup, the
Commission will allow the one-time injection of the snowmelt silt into
the CD 1-19A well.
Please call if you have any further questions.
Wendy Mahan
Natural Resource Manager
>
> Donnelly&Manson wrote:
> >
> > This is a request by Phillips Alaska, Inc. (PAI) to dispose of silt/mud
> by
> > injection into our Class II disposal Well (CDl-19A), which accumulated
> > during management of stormwater runoff at the Alpine Development Project
> > (ADP) this past breakup period.
> >
> > As the weather warmed during breakup at the ADP large pools of snowmelt
> > water formed around the drilling rig and elsewhere on the pad. Due to
> the
> > construction activity at the time these pools were frequently stirred up
> by
> > vehicle and foot traffic resulting in water with a high turbidity. The
> > high turbidity prevented PAI from discharging this snowmelt off the pad
> as
> > part of our stormwater management plan. Due to the large number of
> > construction personnel on-site at this time the Alpine Class I well was
> > running at full pump capacity injecting wastewater from the living
> quarters
> > and dining camps. Therefore, the snowmelt could not be injected into the
> > Class I well. Since the ADP Class II well was not operational at this
> time
> > we developed a system to capture the snowmelt and settle out the solids
> in
> > a 50 ft by 50 ft settling pond. PAI proposes to remove this material
1 "f'J
8/16/009:25 AM
Re: Srormwater S~t Disposal Approval
,/
~
> from
> > the settling pond and to dispose of it by creating s slurry and pumping
> it
> > down the Class II well. The ADP engineering group recommends use of
> > either the hot oil truck or the cement unit on the Grind and Inject
> > Facility to accomplish this.
> >
> > PAL feels that injecting the residual silt form the snowmelt into the
> Class
> > II well is proper and appropriate. The silt has been sampled, tested,
> and
> > found to be RCRA non-hazardous.
> > character, similar to the slurry
> > approved for injection into the
> settled
> > out of the snowmelt collected from the pad in areas around the drilling
> > operations as well as other areas. The April 18, 2000 amendment to Area
> > Injection Order No. 18A , Colville River Field, Colville River Unit,
> > Alpine Oil Pool allows for the injection of snowmelt (Finding 12) .
> >
> > We respectfully ask that you consider and grant our request to inject
> this
> > snowmelt residual silt into the ADP Class II well CDl-19A.
> >
> > Thomas Manson
> > Alpine Environmental Coordinator
The material also has a fluid, mud-like
from our drilling operations which is
class II well. Finally, the silt
') Af.,
8/16/009:25 AM
Re: Class II designation for gravel w/i well houses
.,~.
Subject: Re: Class II designation for gravel w/i well houses
Date: Tue, 20 Jun 2000 13:29:12 -0800
From: Wendy Mahan <Wendy_Mahan@admin.state.ak.us>
Organization: doa-aogcc
To: Lipchak&Rea <P2075@ppco.com>
CC: Camille Oechsli <cammy _ oechsli@admin.state.ak. us>,
Dan Seamount <dan _ seamount@admin.state.ak.us>
~\ C) d-~
~\a '-'''-
r'\\G \~(\-
Ms. Rea,
It is reasonable to consider the small amount of gravel stained with
nonhazardous hydraulic fluid within a wellhouse "associated waste"
directly related to the production process. Furthermore, it would be
preferential to allow the disposal of this waste in the Grind & Inject
facility along with the Class II waste generated from cleanup activities
in the wellhouse area.
The Commission approves the Class II disposal of this small amount of
nonhazardous associated waste consisting of soil from within wellhouses
in the Eastern Operating Area contaminated with hydraulic fluid.
Please call with any questions.
Wendy Mahan
Lipchak&Rea wrote:
>
> Wendy:
> In response to concerns expressed by ADEC's IPP group following field
> inspections last fall, we are implementing a comprehensive well house cleanup
> program ·in the Eastern Operating Area that involves removal of hydrocarbon
> stained gravel from within well houses. As a fol10wup to our discussion on June
> 16th, I am sending you this email to request AOGCC approval to dispose of all
> gravel within a wel1house (inside and outside of a cellar) to a Class II
> disposal well. In some cases, the gravel outside the cellar may have some minor
> staining of hydraulic fluid from the Surface/Subsurface Safey Valve (SSSV)
> control panels in each well house. The SSSV systems are uniquely associated
> with production activities. The control panels provide positive hydraulic
> pressure to the surface/subsurface safety valves. The hydraulic fluid is cycled
> from the panels to the safety valves located in the wellhead and tubing string
> at a depth below permafrost. Therefore as the safety valves are operated, the
> hydraulic fluid is moving back and forth from within the wellhead and tubing
> systems to the panel. Given that the quantity of gravel containing these
> leaks/drips of hydraulic fluid will be very minimal and the fluid is
> non-hazardous and considered to be part of the oil and gas production process,
> we request that the gravel containing this fluid be acceptable for disposal in
> Phillip Alaska'sClass II wells at the Grind & Inject facility.
>
> We believe that managing stained gravel within wel1houses through the Grind &
> Inject facility is the preferred option, both from a best practices and
> environmental perspective. We would appreciate a decision from AOGCC on this
> matter, as it would have significant impacts on the well house cleanup programs
> being undertaken across the North Slope.
>
> We look forward to hearing from you,
> ca ryn rea
> (907) 659-5999
I of I
6/20/00 1 :29 PM
Re: Ô;ass 11 designation for gravel w/i well houses ~
Subject: Re: Class II designation for gravel w/i well houses
Date: Fri, 23 Jun 2000 15:40:35 -0800
From: Wendy Mahan <Wendy_Mahan@admin.state.ak.us>
Organization: doa-aogcc
To: Colegrove&St Pierre <N1037@ppco.com>
CC: Camille OechsIi <cammy_oechsli@admin.state.ak.us>,
Dan Seamount <dan _ seamount@admin.state.ak.us>
~\ 0 ~ß
f\\ O~~
(\ \0 \ 'bP\
Shellie,
Thanks for the clarification.
Again, it is reasonable to consider the small amount of gravel stained
with nonhazardous hydraulic fluid from Safety Valve System control
panels within a wellhouse as "associated waste" that is directly related
to the production process. Also, the most environmentally sensible
practice would be to allow the disposal of this waste in Class II Grind
& Inject facilities along wiht the Class II waste generated from the
cleanup activities in the wellhouse area, rather than segregate and
send the small volume of nonhazardous waste to the Class I wells for
disposal.
The Commission approves the Class II disposal of this small amount of
nonhazardous associated waste consisting of soil from within wellhouses
in the Kuparuk and Alpine areas contaminated with hydraulic fluid.
The snow meltwater commingled with fluids from within the wellhouse
area and the nonhazardous hydraulic fluid may also be injected into a
Class II disposal well.
Please call if you have any additional questions.
Wendy Mahan
Colegrove&St Pierre wrote:
>
> Wendy,
> Sorry for the fragmented sentence. My request includes contaminated gravel from
> within the well cellars and well houses at both Kuparuk and Alpine. Like
> Prudhoe EOA, Kuparuk is also conducting a comprehensive clean up program of
> removing stained gravel within the well cellars and well houses throughout the
> field.
>
> What I meant by the fragmented sentence is that we also hydraulic fluid panels
> that support surface safety valve actuators that, in some cases, have leaked
> onto the gravel pad within the wellhouse, but outside the well cellar. The
> clean up program includes removal of stained gravel within the well cellar and
> the gravel contaminated with the non-RCRA-hazardous hydraulic fluid from the
> hydraulic fittings and valves. We anticipate minimal contaminated gravel and
> have been experiencing about 3 cubic yards per 1-3 drill sites including
> cleanups at various wells on the drill sites, as required. The percentage of
> hydrocarbon contamination will be less than 1%.
>
> In addition to the gravel, during break up, we have snowmelt water which
> naturally accumulates in low spots on the pad, including cellars, assisted by
> the slight grade on gravel drill sites sloping toward the wells and reserve
> pits. The snowmelt water may collect in the cellar and may also contact the
> gravel that is contaminated with hydraulic fluid stains within the wellhouse,
> but outside the cellar. We would like to know whether this meltwater now
1 ^I',,)
6/23/00 3 :40 PM
Re: Glass II designation for gravel w/i well houses \"'''w'
> commingled with fluids within the well cellar and the non-RCRA-hazardous
> hydraulic fluid stains may be injected into a Class II disposal well.
> Shellie.
>
>
?of?
6/23/00 3 :40 PM
#3
"-¥
Notice of Public Hearing
STATE OF ALASKA
Alaska Oil and Gas Conservation Commission
Re: Colville River Unit - Alpine Area
ARCO Alaska, Inc. by letter dated February 3, 2000, has requested an amendment
to Area Injection Order No. 18. The requested amendment would expand the scope of
the Area Injection Order to allow disposal injection of Class II fluids in the Alpine area of
the Colville River Unit.
A person who may be harmed if the requested order is issued may file a written
protest prior to 4: 00 PM, March 1, 2000 with the Alaska Oil and Gas Conservation
Commission, 3001 Porcupine Drive, Anchorage, Alaska 99501, and request a hearing on
this matter. If the protest is timely filed a hearing on the matter will be held at the above
address at 9:00 AM on March 21, 2000, in conformance with 20 AAC 25.540. If no
protest is filed, the Commission will consider the issuance of the order without a hearing.
If you are a person with a disability who may need a special modification in order
to comment or to attend the public hearing, please contact Diana Fleck at 793-1221
before March 14, 2000.
Robert N. Christenson, P .E.
Chair
Published February 9, 2000
ADN AO# 02014025
Anchorage Daily News
Affidavit of Publication
1001 Northway Drive, Anchorage, AK 99508
Ad # Date
Puchase Order
Edition Account
Price Per
Day
279048 02/09/2000
02014025
ON
STATE OF ALASKA
THIRD JUDICIAL DISTRICT
Eva Alexie, being first duly sworn on oath deposes and says that
she is an advertising representative of the Anchorage Daily News,
a daily newspaper.
That said newspaper has been approved by the Third Judicial
Court, Anchorage, Alaska, and it now and has been published in
the English language continually as a daily newspaper in
Anchorage, Alaska, and it is now and during all said time was
printed in an office maintained at the aforesaid place of
publication of said newspaper. That the annexed is a copy of an
advertisement as it was published in regular issues (and not in
supplemental form) of said newspaper on the above dates and
that such newspaper was regularly distributed to its subscribers
during all of said period. That the full amount of the fee charged
for the foregoing publication is not in excess of the rate charged
private individuals.
C (LU¿ ~
Lega I Cle rk_~ÇE::-_----~E-"::~'------
Subscribed ands,^,grnJ9prYl~~þ~fºE~~~is_.<:J-ª!~:~~_____<___~_ _
--_léj1£Ltl-8_Jj;-r~rlQ____-
Notary Public in and for the State of Alaska.
Third Division. Anchorage, Alaska
MY COMMISSION EXPIRES: !é.,k ~ ,;2ðIJt}
--_71_~{---------
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STOF0330
$73.53
$73.53
#2
Phillips Alpine Environmental
Phillips Alaska, Inc., Alp-] 4
PO Box ] 96860
~chorage,AJ( 995]9-6860
Attn: Jolin/Graika
Phone: (907) 670-4527
Fax: (907) 670-4712
NTL Lab#:
Client Sample ID:
LocationlProject:
COC #:
Sample Matrix:
Comments:
)~
"-".
NORTHERN TESTING LABORATORIES, INC.
3330 INDUSTRIAL AVENUE
8005 SCHOON STREET
POUCH 340043
FAIRBANKS, ALASKA 99701
ANCHORAGE, ALASKA 99518
PRUDHOE BAY, ALASKA 99734
(907) 456-3116' FAX 456-3125
(907) 349-1000 - fAX 349-1016
(907) 659-2145 -FAX 659-2146
Report Date:
Date Anived:
Date Sampled:
Time Sampled:
Collected By:
2/4/02
1/31/02
1/30/02
07:00
JB
NT]} 062
WWTP EIDuent
Alpine WWTP
27625
Liquid
FI82Definitions
MOL = Method DeteCtion Limit
B = Below Regulatory Minimum
H = Above Regulatory Maximum
M = Matrix Interference
J = Best Available Estimate
U= Less Than Detection· Limit
D = Lost To Dilution
Analysis Analysis
Parameter Result Units Flag MDL Method Date
EPA 9045
pH 7.61 Unit EPA 9045 1/31/02
EPA 1020
Flash Point > 140 Deg F EPA 1020 1/31/02
By: Jerry Pollen
Pruahoe Bay Laboratory Supervisor
>",-----,,<
\.--
NORTHERN TESTING LABORATORIES, INC.
3330 INDUSTRIAL AVENUE
5761 SILVERADO WAY; UNIT N
POUCH 340043
FAIRBANKS, ALASKA 99701
ANCHORAGE, ALASKA 99518
PRUDHOE BAY, ALASKA 99734
(907) 456-3116· FAX 456"3125
(907) 349-1000· FAX 349-1016
(907) 659-2145 . FAX 659-2146
Phillips Alaska Inc.
Alpine Development pf(~ject
PAl BEST-ALP 14 PO Box 196860
Anchorage, AK 99519-6105
Attn: Jeff Barnett
Phone: (907) 670-4527
Fax: (907) 670-4712
NTL Lab#: F304085
Client Sample ID: WWTP Effluent
Location/Project:
COC #: 27625
Report Date:
Date Arrived:
Date Sampled:
Time Sampled:
Collected By:
2115102
2/1/02
1/30/02
7:00
·m
Sample Matrix:
Liquid
Flae:Definitions
MDL = Method Detection Limit
MCL = Maximum Contaminant Level
B = Below Regulatory Minimum
H = Above Regulatory Maximum
M = Matrix Interference
J= Best Available Estimate
U= Less Than Detection Limit
Comments:
Prep Prep Analysis Analysis
Parameter Result Units Flag MDL MCL Method Date Method Date
Arsenic by TCLP <MOL mgIL U 0.06 5 EPA 1311 2/14/02 EPA 6010B 2/15/02
Barium by TCLP 0.012 mgIL J 0.006 100 EPA 1311 2/14102 EPA 6010B 2/15/02
Cadmium by TCLP <MDL mglL U 0.009 1 EPA 1311 2/14/02 EPA6010B 2/15/02
Chromium by TCLP <MDL mglL U 0.02 5 EPA 1311 2/14/02 EPA 6010B 2/15/02
Lead by TCLP <MDL mgIL U 0.04 5 EPA 1311 2/14102 EPA 60 lOB 2/15/02
Selenium by TCLP <MOL ingIL U 0.02 1 EPA 1311 2/14/02 BPA 6010B 2115/02
Silver by TCLP <MOL mgIL U 0.01 5 EPA 1311 2/14102 BPA 60 lOB 2/15/02
Mercury by TCLP <MDL mgIL U . 0.002 0.2 EPA 1311 BPA 7470 2/15/02
~ _:rZL
.....J )
Repeí!íed by Barry Durbrow
Fairbanks Chemistry Supervisor
'-'
',,-,,'
NORTHERN TESTING LABORATORIES, INC.
3330 INDUSTRIAL AVENUE
5761 SILVERADO WAY; UNIT N
POUCH 340043
FAIRBANKS, ALASKA 99701
ANCHORAGE, ALASKA 99518
PRUDHOE BAY, ALASKA 99734
(907) 456-3116· FAX 456-3125
(907) 349-1000· FAX 349-1016
(907) 659-2145 . FAX 659-2146
Phillips Alaska, Inc.; PAl HEST-ALP 14
P.O. Box 196860
Anchorage, AK 99519-6105
Attn: Jeff Barnett
Phone: (907)670-4527
Fax: (907) 670-4712
Report Date: 3/12/02
Date Anived: 2/4/02
Sample Date: 1/30/02
Sample Time: 7:00
Collected By: JB
NTL Lab#:
Client Sample ID:
Location:
Client Project:
COC#:
Sample Matrix:
Comments:
A300831
WWTP Effluent
Flag Definitions
MRL = Method Report Level
MCL = Max. Contaminant Level
B = Present in Method Blank
H = Above Regulatory Maximum
M = Matrix Interference
] = Estimated Value Below MRL
D = Lost to Dilution
E = Estimated Value
27625
Water
Analysis Method Result Flag MRL MCL Units Prep Prep Analysis
Parameter Method Date Date
EPA 8270
Hexachloroethane <MRL 0.100 3 mg/L EPA 1311 2/6/02 3/11/02
Nitrobenzene <MRL 0.100 2 mg/L
Hexachlorobutadiene <MRL 0.100 0.5 mg/L
2,4- Dinitrotoluene <MRL 0.100 0.13 mg/L
Hexachlorobenzene <MRL 0.100 0.13 mg/L
2,4,~Trichlor~henol <MRL 0.100 2 mg/L
2,4,5- Trichlor~henol <MRL 0.100 400 mg/L
Pentachlor~henol <MRL 0.100 100 mgIL
Pyridine <MRL 0.250 5 mgIL
o-Cresol <MRL 0.100 200 mgIL
m,p-Cresol <MRL 0.100 200 mgIL
Total Cresols <MRL 0.100 200 mgIL
2-Fluorophenol (Surr) 61 % Recovery
Phenol-d6 (Surr) 66 % Recovery
Nitrobenzene-dS (Surr) 75 % Recovery
2-Fluorobiphenyl (Surr) 72 % Recovery
~, ..~ i ~.""'r.k. U
Reported By: Wendy Mitchell
Anchorage Laboratory Manager
--.
',-,,'
NORTHERN TESTING LABORATORIES, INC.
3330 INDUSTRIAL AVENUE FAIRBANKS, ALASKA 99701
5761 SILVERADO WAY; UNIT N ANCHORAGE, ALASKA 99518
POUCH 340043 PRUDHOE BAY, ALASKA 99734
(907) 456-3116 - FAX 456-3125
(907) 349-1000 - FAX 349-1016
(907) 659-2145 -FAX 659-2146
Phillips Alaska, Inc.; PAl HEST-ALP 14
P.O. Box 196860
Anchorage, AK 99519-6105
Attn: Jeff Bamett
Phone: (907) 670-4527
Fax: (907) 670-4712
NTL Lab#: A300831
Client Sample ID: WWTP Effiuent
Location:
Client Project:
COC#:
Sample Matrix:
Report Date: 3/12102
Date .Arrived: 2/4/02
Sample Date: 1/30/02
Sample Time: 7:00
Collected By: m
27625
Water
FlaK Definitions
MRL = Method Report Level
MCL= Max. Contaminant Level
B = Present in Method Blank .
H = Above Regulatory Maximum
M = Matrix Interference .
1 = Estimated Value Below MRL
D = Lost to Dilution
B = Estimated Value
Comments:
Analysis Method Result Flag MRL MCL Units Prep Prep Analysis
Parameter Method Date Date
2,4,6- Tribromophenol (Surr) 83 % Recovery EPA1311 2/6/02 3/11/02
p- Terphenyl-d14 (Surr) 94 % Recovery
EP A 8260
Benzene <MRL 0.100 0.5 mg/L EPA1311 2/4/02 2/5/02
Carbon Tetrachloride <MRL 0.100 0.5 mgIL
Chlorobenzene <MRL 0.100 100 mgIL
Chloroform <MRL 0.100 6 mgIL
1,4-Dicblorobenzene <MRL 0.100 7.5 mgIL
1,2-Dicbloroethane <MRL 0.100 0.5 mgIL
1,I-Dicbloroetheœ <MRL 0.100 0.7 mgIL
2-Butanone (MEK) <MRL 0.500 200 mgIL
Tetrachloroetheoe <MRL 0.100 0.7 mgIL
TrichloroetbeDe <MRL 0.100 0.5 mgIL
Vinyl Chloride <MRL 0.100 0.2 mgIL
DBFM (Surr) 98 % Recovery
Toluene-d8 (Surr) 102 % Recovery
4-Bromoftuorobenzene 103 % Recovery
~ ~~~~1t-k.J'.
Reported By: Wendy Mitchell
Anchorage Laboratory MaDager
#1
ARca Alaska, Inò..-'
Post Office Box 100360
Anchorage, Alaska 99510-0360
Telephone 907 276 1215
~~
~~
February 3, 2000
-
-
Mr. Blair Wondzell
Alaska Oil and Gas Conservation Commission
3001 Porcupine Drive
Anchorage, Alaska 99501
Subject: Application for Amendment to Injection Orders
Alpine Oil Pool/Colville River Field
......
Dear Mr. Wondzell:
~
ARCO Alaska, Inc., as an owner and the operator of the Colville River Unit, seeks
Alaska Oil and Gas Conservation Commission approval to amend Area Inj ection Order
No. 18 (dated January 24, 2000) to authorize additional disposal wells in the disposal
intervals specified in Disposal Injection Order No. 18 (dated April 19,1999). Enclosed
please find a copy of ARCO's application which was prepared in accordance with 20
AAC 25.460 (Area Injection Orders) and 20 AAC 25.252 (Underground Disposal of Oil
Field Wastes and Underground Storage of Hydrocarbons).
~
Please note that to minimize operational constraints we propose spudding well CD 1-19 A
no later than April 17, 2000 in order to complete one Class II well before the end of this
ice road season. Your consideration and any recommendations regarding the expedient
processing of this request will be very much appreciated.
--
Inquiries regarding this application may be directed to either Mike Erwin or Doug
Chester at this office.
-
Sincerely,
RiGINAl
Mark M. Ireland
Alpine Development Manager
RECE\VED
fEBO 4 [000
askI 0" & GaaCani. eomm\Mion
At.. ~
~
-
...
y",-,,"
-
Application for DIO
November 1, 1998
Page 2
-
""'"
cc:
Mr. Kenneth A. Boyd, Director
Alaska Department of Natural Resources
Division of Oil & Gas
3601 C Street, Suite 1380
Anchorage, Alaska 99503-5948
Mr. Robert N. Christenson, Chairman
Alaska Oil and Gas Conservation Commission
3001 Porcupine Drive
Anchorage, Alaska 99501
~
Ms. Teresa Imm, Resource Development Manager
Arctic Slope Regional Corporation
301 Arctic Slope Avenue, Suite 300
Anchorage, Alaska 99518-3035
-
-
Mr. Isaac Nukapigak, President
Kuukpik Corporation
PO Box 187
Nuiqsut, Alaska 99789-0187
-
~
Jonathan Williams
Us EPA, Region 10
Groundwater Protection Unit
1200 Sixth Avenue (OW-137)
Seattle, WA 98101
(letter only)
-
Mrs. Catherine Lively
Anadarko Petroleum Corporation
PO Box 1330
Houston, Texas 77251-1330
~
Todd Liebel
Anadarko Petroleum Corporation
PO Box 1330
Houston, Texas 77251-1330
.......
~
~
~
Area Injection Order No. 18
Colville River Unit
Colville River Field
Alpine Oil Pool
Amendment No.1
ARC a Alaska, Inc
Anadarko
Petroleum Corporation
-.-
Union Texas Petroleum, LLC
-
February 3, 2000
--
-
-
Table of Contents
20 AAC 25.252 Page
(c) 1 Well Locations 4
(c) 2 Surface Owners and Operators 5
-
(c) 3 Affidavit (see Exhibit 10)
(c) 4 Geologic Details 6
(c) 5 Well Logs 9
(c) 6 Mechanical Integrity and Well Construction 10
(c) 7 Waste Sources and Characteristics 12
(c) 8 Inj ection Pressure 14
(c) 9 Waste Confinement 15
(c) 10 Formation Water Salinity 17
(c) 11 Aquifer Exemption Request 21
(c) 12 Offset Well Status 22
Exhibits
1
2
3
4
5
6
7
8
9
10
Colville River Unit Location Map
Type Log - WD-02
Geologic Cross-Section
Seismic Cross-Section
Structure Map - Kingak Depth
Structure Map - Sag River Depth
Structure Map - Lisburne Depth
Class II Typical Well Schematic
Well Head Schematic
Affidavit of Notice to Surface Owners
~
-
2
~
Introduction
~
On April 19, 1999, the Commission issued Disposal Injection Order No. 18 which
authorizes ARCO to inj ect Class II fluids into the Colville River Unit well WD-02. The
disposal intervals include the Permo-Triassic Ivishak and the Triassic Sag River
Formations.
-
On January 24,2000, the Commission issued Area Injection Order No. 18 which
establishes an Area Injection Order for enhanced oil recovery operations in the Alpine Oil
Pool (Exhibit 1).
-
ARCO recently recognized the need to expand its Class II operations to include
additional disposal wells. Hence, this application seeks Commission approval of
amendments to Disposal Injection Order No. 18 and Area Injection Order 18 to
authorize additional disposal wells in the injection zones specified in Disposal Injection
Order No. 18. This application has been prepared in accordance with 20 AAC 25.460
(Area Injection Orders) and 20 AAC 25.252 (Underground Disposal of Oil Field Wastes
and Underground Storage of Hydrocarbons
3
~
-
Well Locations
20 AAC 25.252 (c) 1
-
The attached map (Exhibit 1) shows all known wells penetrating the inj ection zone in the
proposed inj ection area. The map also shows the areal extent of the inj ection zone
relative to the Colville River Unit boundary.
-
Arco proposes to drill up to five penetrations into the proposed injection intervals for
Class II disposal purposes. Three locations are described in Arco's Application for
Disposal Order dated December 3, 1998. The three wells are shown on Exhibit 1 as wells
WD-O 1, WD-02, and WD-03. In addition, Arco is now considering the addition of two
well locations to be drilled from the well pad to facilitate access workover fluid disposal
as well as drilled fluids and cuttings from the Grind and Inject module which works in
tandem with the drilling rig. These two locations are shown as wells CD 1-19 A, and WD-
04. There are no additional disposal well requirements for the foreseeable future.
~
-
-
~
4
-
-
.......
Operator:
-
-
Surface Owners:
~
~
~
-
-
--
.~
Surface Owners and Operators
20 AAC 25.252 (c) 2
Operators and Suñace Owners within
One Quarter Mile of Injection Operations
ARCO Alaska, Inc.
Attention: Mark Ireland
P. O. Box 100360
Anchorage, AK 99510-0360
State of Alaska
Department of Natural Resources
Attention: Mike Kotowski
P. O. Box 107034
Anchorage, AK 99510
Kuukpik Corporation
Mr. Isaac Nukapigak
PO Box 187
Nuiqsut, Alaska 99789-0187
5
'~
-
Geologic Details
Type Log, Cross Section, Structure and Stratigraphy
-
-
20 AAC 25.252 (c) 4
Introduction
The geology of Permo-Triassic and Jurassic age sediments within the Colville River Unit
area is described with specific reference to the proposed injection and confining intervals.
The intervals of interest comprise clastic and carbonate rocks of the Kavik, Ivishak,
Eileen, Shublik, Sag River, and Kingak Formations, in ascending order (Exhibits 2 and
3). These formations are continuous across the Colville River Unit and eastward to the
Kuparuk and Prudhoe Bay fields. A seismic section is presented as Exhibit 4. Structure
maps on key horizons are presented (in Exhibits 5-7) with the location of proposed
disposal well CD 1-19 A noted.
~
The Jurassic and Permo-Triassic sediments comprise the Ellesmerian sequence
characterized by marine transgressive-regressive cycles deposited on a slowly-subsiding
passive-margin ramp to the south with a broad, stable platform to the north. The Permo-
Triassic Ivishak formation consists of lowstand t1uvial-deltaic-marginal marine deposits
that accumulated along the south-facing Ellesmerian ramp. Triassic transgression
blanketed this interval with shallow marine sandstone and siltstone (Eileen), organic-rich
calcareous shale and limestone (Shublik) and finally shelf sandstone (Sag River) across
the tectonically stable northern platform. The overlying Jurassic section (Kingak)
consists of southward prograding marine clastics.
The Sohio Nechelik #1 well was cored throughout the Ivishak Formation. The Ivishak is
described as white, gray, clear quartz-rich sandstone, with minor amounts of chert, coal,
pyrite, dolomite, calcite cement, and occasional mudstone pebbles. The sandstone is well
consolidated, fine to medium grained, moderately sorted with thin conglomerate bands.
Sedimentary structures include massive bedding, trough and planar crossbeds outlined by
muddy and silty laminae, and some ripple cross-lamination.
Formation Nomenclature
.~
Age
Jurassic
Triassic
Triassic
Triassic
Permian
Formation
Kingak
Sag River
Shublik
Eileen
Ivishak
~
-
Permian
Kavik
-
Depositional Environment and Lithology
Marine shelf and prodelta shales
Shallow marine sandstones
Shallow to deep marine shales and limestone
Shallow marine sandstones and siltstones
Fluvio-deltaic sandstones, conglomerates, and
siltstones, and shales
Prodelta and shelf shales
6
-
"'~
-
.-
Geology of the Waste Disposal Zones
Exhibits 2 and 3 show the geologic subdivisions for the proposed injection and confining
zones. Well WD-02 is the type log because of its proximity to the proposed development
area. Proposed Class 2 disposal well CDl-19A is 4000' northeast ofWD-02.
The table below relates the injection and confining zones to the formations displayed in
the exhibits. The formations described here are easily correlative to the fields to the east.
Expected formation thickness is prognosed primarily from WD-02.
Age
Jurassic
Triassic
Triassic
Permian
Permian
Formation
Kingak
Sag River
Shublik/Eileen
Ivishak
Kavik
Injection and Confining Zones
Confining Zone
Upper Injection Zone
Major Barrier
Lower Injection Zone
Lower Confining Zone
~
{-~
-
Lower Confining Zone
Permian Kavik Formation: Within the Colville River Unit area, the Kavik is 200 to 250
feet thick and consists of a fairly uniform, medium to dark gray, silty shales which are
pyritic, noncalcareous and micaeous. The Kavik shale is interpreted to have been
deposited as shelfal and pro-deltaic deposits. This section is easily correlatable and
extends across the entire Alpine Unit and west to Kuparuk. WD-02 reached TD 75 feet
into the Kavik shale.
Below the Kavik Shale are additional siltstones and shales of the Echooka Formation.
This formation has very poor porosity and permeability and will probably act as an
additional confining zone.
The interbedded limestones and mudstones of the Lisburne Group occur beneath the
Echooka Formation. Based on Nechelik 1 and Fiord 1, the Lisburne Group has very poor
porosity and permeability.
-
Lower Proposed Injection Zone
Permo-Triassic Ivishak Formation: Class 1 disposal well WD-02 is currently completed
in the Ivishak with 191 feet of perforations. The Ivishak is interpreted to be deposited as
fluvial-deltaic sandstones. The gross interval thickness is 600-700 feet and consists of
thick-bedded, fine-medium grained sandstones, thin-bedded conglomerates, and siltstones
and mudstones. WD-02 has 327 feet of gross sandstone within 659 feet of interval.
Using a 15% porosity cutoff, 57 feet of net sandstone is present. The net sandstone
averages 17% porosity and 50 millidarcies permeability based on log calculations.
~
-
7
.-
-
Major Barrier Between In,jection Zones
Triassic Eileen Formation: The Eileen Formation consists of interbedded very-fine
grained sandstone, siltstone and mudstone. The gross interval thickness is 150-200 feet.
Calculated sandstone porosities are less than 15%.
~
Triassic Shublik Formation: The Shublik Formation consists of250 to 350 feet of shale,
siltstones, and limestones deposited during a Triassic marine transgression. The Lower
Shublik consists predominantly of siltstones and shale. This interval is extremely
correlative and consistent in character and thickness. The high resistivity limestones of
the Upper Shublik overlie this section. These limestones are interpreted to have been
deposited in a shallow marine environment during a period of quiescence with minimal
clastic input. This horizon is also easy to correlate and very uniform in thickness.
Porosity and permeability are poor.
-
Upper Proposed Injection Zone
Triassic Sag River Formation: The upper injection zone within the Colville River Unit is
the Sag River Formation which was deposited in a shallow marine shelf setting. The
gross interval thickness is 35-50 feet and consists of quartzose, very fine grained,
glauconitic sandstones. In well WD-02, using a 15% porosity cutoff, 35 feet of net
sandstone is present within 38 feet of interval. The net sandstone averages 20% porosity
and nearly 100 millidarcies permeability based on log calculations.
Confining Zone
The Jurassic Kingak Formation is 1000-1300 feet thick and consists predominately of
shales deposited as marine shelf and/or prodelta mudstones. This thick shale horizon is
extremely consistent on a regional basis. The upper 500 feet of Kingak is an overall
coarsening upward sequence with thin siltstone interbeds more common near the top of
the sequence. The Kingak is characterized by very poor horizontal and vertical
permeability and therefore, represents a competent barrier to vertical fluid movement.
~
Occurrence of Hydrocarbons
There are no hydrocarbon accumulations within the Permo-Triassic proposed inj ection
intervals in the Colville River Unit. Extremely faint residual oil shows are present in the
Nechelik well. This is to be expected as these beds probably acted as migratory routes
long ago for hydrocarbons that are now accumulated elsewhere. Wireline logs indicate
that these zones are now wet.
-
Outcrops and Recharge
None of the Permo-Triassic or Jurassic formations outcrop in the local area or intercept
the 1300-1500 foot thick permafrost zone. The injection zones occur 8000 feet below the
permafrost.
-
8
~~
"-""
-
Well Logs
20 AAC 25.252 (c) 5
W ell logs and cuttings have been previously provided to the Commission following
completion of well WD-02 in April, 1999. Logs from early exploration and development
wells have already been filed with the Alaska Oil and Gas Commission.
-
-
-
-
9
'-.
Mechanical Integrity & Well Construction
-
20AAC 25.252 (c) 6
Mechanical Integrity
Prior to commencement of injection, the well will be cased and cemented in accordance
with 20 AAC 25.030 to prevent leakage out of the injection interval. Additionally, Arco
will provide a cement quality log or other well data approved by the Commission to
demonstrate isolation of the injected fluids in the injection interval, in accordance with 20
AAC 25.412(d). And each injection well will be pressure tested in accordance with 20
AAC 25.412(c), with notice to the Commission in accordance with 20 AAC 25.412(e).
During operation casing-tubing annulus pressures and injection rates will be monitored
no less than weekly by trained and qualified operators to ensure there is no leakage and
that pressures will not subject the wellhead or tubulars to pressures exceeding 70% of
their minimum yield strength.
In the event pressure observations or tests indicate communication or leakage of any
tubing, casing, or packer, Arco will notify the Commission no later than the first working
day following the observation to obtain Commission approval of appropriate corrective
actions, as well as permission to continue injection operations. Commission approval will
be received prior to commencement of corrective actions unless the situation represents a
threat to life or property.
Drilling/Well Design
All underground injection into the Permo-Triassic and Jurassic Formations will be
through wells permitted as service wells for injection in conformance with 20 AAC
25.005, or approved for conversion to service wells for inj ection in conformance with 20
AAC 25.280. Additionally, all injection wells will be constructed in accordance with 20
AAC 25.030, 20 AAC 25.412, and Conservation Order 443 (Colville River Field, Alpine
Oil Pool). A typical wellbore schematic is included as Exhibit 8, and a typical wellhead is
included as Exhibit 9.
-
The inj ection interval will be accessed from wells directionally drilled from one of two
gravel pads utilizing drilling procedures, well designs, casing and cementing programs
consistent with current practices in other North Slope fields. The following will preview
an Alpine drilling proposal for both producing and injection wells.
-
For proper anchorage and to divert an uncontrolled flow, 16-inch conductor casing will
be drilled and cemented at least 75 feet below pad. Cement returns to surface will be
verified by visual inspection. A diverter system compliant with the Commission
requirements will be installed on the conductor.
-
10
~
-
Surface holes will be drilled to a minimum of2200' TVDSS for proper anchorage,
prevention of uncontrolled flow, protection of aquifers, and protection from permafrost
thaw and freeze back. This casing setting depth provides sufficient depth for kick
tolerance while drilling through to the next casing point. Either 9-5/8" or 7 5/8" surface
casing strings will be cemented to surface using lead slurry of lightweight permafrost
cement, followed by tail slurry in a single stage. No hydrocarbon bearing intervals have
been encountered to this depth in previous wells.
~.
The casing head and blowout preventer stack will be installed and tested consistent with
Commission requirements. A Leak-Off Test (LOT) or Formation Integrity Test (FIT) will
be performed upon drilling no more than 50' beyond the surface casing shoe in
accordance with 20 AAC 25.030(f). Production casing will be set near the base of the
injection zone and cemented across and not less than 500 feet measured depth above the
Alpine.
~
Cement Quality Evaluation
Prior to running the completion, a cement quality log will be run to verify the cement
quality and top of cement behind the production casing.
Completion Design
Single tubing strings, 2-7/8" up to 4-1/2" OD, will be installed in each well. Isolation of
the tubing by casing annulus will be carried out within 200' of the top of the uppermost
inj ection interval. This isolation will be provided by use of either a permanent hydraulic
set packer or a polished bore receptacle / seal assembly combination (in the case of a
mono-bore completion). Subsurface safety valves will be installed below the permafrost
depth. At this time there are no specific plans in place for mandrels or other freeze
protection hardware, although they may be added at a future date.
In addition to conventional perforated completions, additional designs may be presented
for administrative approval after submitting and presenting data demonstrating that such
alternatives are based on sound engineering principles.
Abandonment
All abandonment procedures will be performed following Commission approval in accordance
with 20 AAC 25.105.
~
~
11
.,,,-",,
-
Waste Sources and Characteristics
-
20 AAC 25.252 (c) 7
~
Class II disposal wells are defined as wells which inj ect wastes brought to the surface in
connection with oil and gas production, with natural gas or liquid hydrocarbon storage
operations. Class II fluids may be mixed with other wastes from plant operations, unless
those wastes are classified as hazardous waste under 40 CFR 261.3.
-
Typical RCRA exempt wastes which are acceptable for injection can include the
following:
-
-
Drill Cuttings,
Drilling fluids,
Cement fluids,
Completion fluids,
W orkover fluids,
Stimulation fluids,
Frac Sand,
Produced Water,
Crude Oil,
Production Vessel Sludge/Sand,
Fresh or Sea Water,
Natural Gas Liquids,
Rig Wash,
Well Cellar Fluids,
and others allowed under 40 CFR 261.4.
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Typical Injection Rates and Volumes
Exempt wastes routinely generated by drilling, well workovers, contaminated crude oil,
vessel sludge/sand, diesel/methanol usage, spent acid, fracturing operations, snow melt,
and plant upsets could total 4 million barrels over the life of the field. These fluids will be
disposed of into wells located on the drilling pad, such as WD-04 and CDl-19A. Each
well could potentially dispose of 2-3 million barrels of fluid over their life. Daily
injection volumes are not expected to exceed 2,500 bbl., and rates are not expected to
exceed 5 BPM.
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Produced water disposal could reach 14 million barrels before produced water (PWI)
handling facilities are commissioned to commence waterflood re-injection of produced
water. This potentially 18 million-barrel waste stream is currently destined for injection
into well WD-02. Expectations are that wells WD-O 1 and WD-03 will be drilled to
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provide disposal capacity as necessary prior to initiating PWI injection in the waterflood.
Each of those wells could receive 3-5 million barrels of produced water injection at rates
not expected to exceed 5 BPM.
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There is concern that high density slurries will screen-out or plug a Sag River/Ivishak
well rendering a disposal interval useless. Therefore the disposal of drilling mud and
cuttings will be performed with sufficient volumes of water to maintain slurry densities
which maintain cuttings transport. Large solids may be captured and washed for
reclamation by the grind and inject facility associated with the drilling rig.
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Injection Pressure
20 AAC 25.252 (c) 8
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The following table shows the range of injection pressures that are estimated to occur through
the life of a single well over many years. They reflect behavior of the tighter Ivishak
formation since the Sag River is clean sand with significantly better porosity and permeability.
The Ivishak sand intervals containing clay, are tightly cemented, and are interspersed with
enough shale stringers that it may be difficult to push dirty fluids into a completion interval
for an extended period. The smaller pore throats will progressively become plugged in the
region around the wellbore. This damage zone will restrict well injectivity so that in order to
maintain the required disposal rate, it will be necessary to stimulate or fracture past the
restriction. It is anticipated that near-wellbore fractures will be required to establish new flow
paths to undamaged rock. The projected pressures reflect what is expected to occur because of
variations in lithology and changes in the well injectivity index with time. Should use of the
Sag River formation be required, fracturing would be much less prevalent. Further discussion
on fracturing is included in the next section.
Surface
In.iection Pressure
Early time frame: No fracturing of the injection zone required
but assumes zones are originally slightly over pressured.
1700 psi
Several years into field life: Some fracturing of the near wellbore
region may occur to get past early plugging caused by dirty fluids.
Assumes a clean sand fracture gradient of 0.65 psi/foot.
2200 psi
Later in field life: Fracturing of the near wellbore region is required.
Assuming a tighter shaley/sand fracture gradient of 0.70 psi/foot and
a higher injection rate, this level of pressure is required to overcome
estimated fracture mechanics and tubing frictional losses.
3000 psi
Maximum inj ection pressure: This generates a static fracture
gradient ranging from 0.77 - 0.80 psi/ft. If friction losses are taken
into account these gradient values would be smaller.
3200 psi.
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Waste Confinement
20 AAC 25.252 (c) 9
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This section discusses potential confinement issues, how these issues will be addressed,
and how they will be handled in the unlikely event that problems occur.
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Un cemented Wellbores
The Permo-Triassic and Jurassic Formations represent the deepest active reservoirs in the
Colville River Unit. As such, the only wellbores penetrating this interval are for disposal
purposes and fully cemented throughout both the injection and confining intervals. There
are no past, present, or planned penetrations in this interval that will provide
communication channels to shallower horizons.
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Wellbore Channeling
No oil reservoir development wells will penetrate the confining zone. Production well
casing strings will be cemented across the oil reservoir and 500-1000 feet into the shale
that overlays it.
There is no confinement risk associated with wellbore leakage due to development wells.
The only leakage that could occur would be associated with channeling adjacent to an
injection well. Tracer, temperature, or water flow log detection would be followed by
squeeze cementing to repair the channel. Verification of the repair by pressure testing
and logging would follow.
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Natural Faulting
As shown on the structure maps, and on Exhibit 7, there are normal faults cutting the
injection and arresting zones in the local area. They are minor compared to the thickness
of the overlying Kingak shale. At this depth, sand intervals will generally produce a
rubble zone that permits flow along the fault plane; however, brittle shales typically do
not follow this pattern. Experience has shown that it would take a very large pressure
differential to create flow along a normal fault where dense shales are juxtaposed against
each other.
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At Prudhoe Bay, major faults extend from the main oil/gas reservoirs at +/- 8500 feet to
the Cretaceous water disposal zone at +/ - 6000 feet. With a large gas cap present in the
Ivishak, obviously there was no upward gas migration or the Kingak shale would not
have become the cap rock for hydrocarbon accumulations. By the end of 1996, the main
oil reservoir pressure had declined 1000 psi. Conversely, the over lying Cretaceous
aquifers have been over-pressured several hundred psi due to a billion barrels of produced
15
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water disposal. This imbalance creates a pressure gradient of over 0.4 psi/ft (1000
psi/2500 feet). No cross flow has been detected from the Cretaceous zone.
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Fracturing of the Confining Zone
Wellbore damage is expected to accumulate from the periodic disposal of dirty fluids.
This will necessitate wellbore stimulations and near-wellbore fracturing to inject past the
damaged zone while maintaining effective disposal rates. Fractures are not expected to
be laterally extensive since fluid leak off will be rapid once new rock is contacted.
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Due to boundary lithology contrasts, fracturing will be vertically contained. Poisson's
Ratio has been derived from dipole sonic logs of wells WD-02 and Fiord #1. They
support a fracture gradient in the Lower Kingak of 0.76 psi/ft. The fracture gradient
measured in well WD-02 and reported in the EPA Completion Report, dated 4/19/1999,
was 0.66 psi/ft. With the shales fracturing at a gradient of 0.76 psi/ft, and disposal
interval sands at 0.66 psi/ft, the stress contrast is 0.10 psi/ft. At an arresting zone base
depth of 8,650 feet SS, this generates a stress contrast of 865 psi. This suggests that
fractures initiated in the Sag River Formation could not penetrate the overlying Kingak
shale. Even assuming limited vertical fractures grew upward from the Sag River, it is
highly unlikely they could penetrate the 660 feet of Kingak confining zone and reach
even the Alpine. Confinement risk associated with fracturing is minimal.
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Comparison With Similar Projects
There are similar but no direct comparisons with other North Slope disposal projects
because dirty water/wastes have not been injected into these formations on a long-term
basis. However, since 1985, produced water and seawater injected into 206 Prudhoe Bay
Sag River and Ivishak wells has totaled 6.146 billion barrels. At the Endicott field, 506
million barrels has gone into 26 wells and at the new Pt. McIntyre field, 205 million has
gone into 13 wells. The average per well ranges from 30 MMB at Prudhoe to 16 MMB at
Pt. McIntyre.
Many of the above wells have minor fracture systems associated with their injection zone,
some caused by thermal fracturing due to injection of cold surface waters and others by
fracturing past wellbore damage zones. Some of the fractures are permanent and others
probably open and close. In the rare case where injected fluids are not confined to the
desired sub-interval, it is usually associated with a poor casing cement job. Fluids are
confined within the Ivishak gross section.
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Summary
The risk of non-confinement of injected wastes must be viewed as minimal to non-
existent. A competent confining zone and successful large scale water injection at other
locations, coupled with proper well monitoring, all indicate wastes can be confined
without environmental damage.
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Formation Water Salinity
20 AAC 25.252 (c) 10
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Salinity Calculations
In the Alpine project area only the Nechelik #1 well has been logged from surface
through the injection zone. No clean sands were encountered above the confining zone;
however, the Alpine #1 well did cut some thin Albian sands at 5150-5204 feet and
Bergschrund #1 found a thin shelf sand at 4220 feet. Salinity calculations made on
available intervals resulted in the following.
· Bergschrund # 1 (4220 feet) 15,000 ppm NaCI eq.
· Alpine # 1 (5150-5204 feet) 15,000 ppm NaCI eq.
· N echelik # 1 (Sag River FOffilation) 18,000 ppm NaCI eq.
- · Nechelik #1 (Ivishak FOffilation) 17,000 ppm NaCI eq.
The methodology used and results obtained from salinity calculations on the
Albian/Nanushuk Shelf sand stringers (Alpine #1 and Bergschrund #1), Sag River, and
Ivishak FOffilations (Nechelik #1 well) are as follows. The calculations use the standard
Archie correlation and log derived data to obtain an Rwa value using the following
fOffilula:
Rwa = (porosity) m (Rt) / a ........... with the following definitions:
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Rwa
Porosity
Rt
m
a
Resistivity of water necessary to make a zone 100 % wet
Porosity in decimal from logs
FOffilation resistivity from logs
Cementation exponent
Assumed to be 1.0 per the Archie correlation
The cementation exponent is the variable of least certainty. The best source for
deteffilining this value is from special core analysis (SCAL) when available. No SCAL is
available for the Albian interval; however, such data does exist for analogous fine to very
fine grain sand in the area. This data has yielded:
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Alpine section SCAL from the Alpine # 1 well
Sag River SCAL as documented in ARCa
TSR 95-46, internal report
m = 1.55
m = 1.6
The following exponents will be used in these salinity calculations.
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Shallow intervals (4000- 5000 feet)
Sag River Formation
Ivishak Formation
m = 1.6
m = 1.7
m = 1.8
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· Nanushuk Shelf Sand: (Bergschrund #1 well depth 4220 feet)
This shelf sand is evident in two wells at approximately 4200 feet subsea.
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Rt = 4.0, Raw density = 2.28, m = 1.6, Porosity = (2.65-2.28) / (2.65-1.0) = 0.224
The calculation yields an Rwa equal to 0.356. Using Schlumberger Chart Gen-9 and a
formation temperature of80 degrees F, gives a salinity of 15,000 ppm NaCl equivalent.
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· Albian Interval: (Alpine #1 well depth 5150-5204 feet)
There is a collection of thin sands in this well and a complete set of logs is available.
Rt is taken from the shallow MWD tool because of minimum exposure time to invasion
and superior vertical resolution in three foot thick beds. Porosity comes from the density
log.
Rt = 3.2, Raw density = 2.28, m = 1.6, Porosity = (2.65-2.28) / (2.65-1.0) = 0.224
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The Calculation yields an Rwa equal to 0.293. Using chart Gen-9 from Schlumberger
chart books with a formation temperature of 100 degrees F, gives a salinity of 15,000
ppm N aCl equivalent.
· Sag River Formation: (Nechelik #1 well depth 8432-8480 feet)
This is a thick, clean, uniform sand interval with a complete set of logs.
Rt = 1.9, Raw density = 2.32, m = 1.7, Porosity = (2.65-2.32) / (2.65-1.0) = 0.20
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The calculation yields an Rwa of 0.145 and with a formation temperature of 165 degrees
F, produces a salinity value of 18,000 ppm NaCl equivalent.
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· Ivishak Formation: (Nechelik #1 well depth 9420-9460 feet)
This lower sand member has the lowest resistivity and greatest SP excursion.
Rt = 3.3, Raw density = 2.35, m = 1.8, Porosity = (2.65-2.35) / (2.65-1.0) = 0.18
The calculated Rwa equals 0.15 and with a formation temperature of 185 degrees F, a
salinity of 17,000 ppm NaCI equivalent is obtained from the Schlumberger chart.
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Water Sample Analyses
The following water samples were obtained from drill stem and production tests in the
general Colville Delta area.
· Colville #1 well 7922 feet
· 14 miles Northeast
· 22,485 mg/l TDS (tested)
Shublik Formation
· Colville # 1 well 9073 feet
· 14 miles Northeast
· 24,004 mg/l TDS (tested)
Lisburne Formation
· Kalubik #1 well 5050-5250 feet Albian Interval
· 17 miles Northeast
· Flowed 151 barrels to surface
· 24,300 mg/l TDS (average of tests)
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· Kalubik Cr. #1 well 9047-9188
· 21 miles East
· Flowed 325 barrels of water
· 21,847 mg/l TDS (tested)
Lisburne Formation
· Mukluk well 7490-7520 Ivishak Formation
· 23 miles North
· Flowed 984 barrels of water
· 11,000 ppm chloride tested
· 18,150 mg/l TDS (calculated)
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· Mukluk well 8145-9860 Lisburne Fonnation
· 23 miles North
· Flowed 1750 barrels of water
· 11,000 ppm chloride tested
· 18,500 mg/l TDS (calculated)
Laboratory data and other reports can be made available if desired. Reference is also
made to the Class I Well Pennit Application, Appendix D, previously submitted to the
Commission in September 1997.
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Aquifer Exemption
20 AAC 25.252 (c) 11
Aquifer Exemption
No underground sources of drinking water (USDW) have been identified within the
Colville River Unit area. In the absence ofUSDW's, an aquifer exemption is not
applicable.
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Offset Well Status
20 ACC 25.252 (12)
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There are only 3 wells currently penetrating the disposal interval within 1/4 mile of the
Colville River Unit boundary.
Well WD-02 operates under Disposal Order No. 18 and an EP A Class I permit. It is
currently disposing of camp waste in the Ivishak. Mechanical integrity is demonstrated
annually. Completion reports are on file with the Commission, and additional information
will be provided upon request.
The Fiord #1 (Permit #91-147) is an exploration well drilled and abandoned in 1992. It's
completion report and abandonment schematic are on file with the Commission, and
additional information will be provided upon request.
The Sohio Nechelik #1 an early exploration well drilled and abandoned in the 1980's.
No corrective actions at this time are planned for any of the above wells in preparation for
additional drilling.
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Colville River Unit Location Map
LPINE
River Unit
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200
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327 ft gross
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Exhibit 4
ARCO Alaska Inc.
Alpine Project
Seismic Section
SW - NE Transect
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Structure Map
Kingak Depth
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Structure Map
Sag River Depth
---..-..-------------
Structure Map
Lisburne Depth
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Class II
Exhibit 8
roposed Completion Diagram
9-5/8" to Surface Casing
set below 2200'
and cemented to
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Drilling Mud
TOC @ +/-6600' TVD
(500' above Alpine Reservoir)
16" Conductor below 75' MD
Base Permafrost @ +/-1500 ft TVDss~
Subsurface Safety Valve (SSV) below the
Permafrost at +/-1700' TVD
2-7/8" up to 4-1/2"
tubing to the packer
Packer Fluid:
8.6 ppg KCL brine
with diesel freeze protection to +/-2000'
Permanent Packer
set within 200' of the
injection interval top
to 7" Intermediate
Set in or below the Sadlerochit
and cemented above the Alpine
Injection perfs
River and Sadlerochit
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Exhibit 9 - Wellhead Schematic
10.5 "
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Exhibit 10
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Alpine Injection Order
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Affidavit of Michael D. Erwin
STATE OF ALASKA
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THIRD JUDICIAL DISTRICT
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I, Michael D. Erwin, declare and affmn as follows:
1. I am the Alpine Production Engineer for ARCO Alaska, Inc., the designated operator of the Colville River Unit
(which includes the Alpine Pool).
2. On February 3,2000, I caused copies of the Area Injection Order Application to be provided to the following
surface owners and operators of all land within a quarter-mile radius of the proposed injection area:
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Operator:
ARCO Alaska, Inc.
Attention: Mr. Mark Ireland
P.O. Box 100360
Anchorage, AK 99510-0360
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Surface Owners:
State of Alaska
Department of Natural Resources
Division of Oil and Gas
P.O. Box 107034
Attention: Mr. Mike Kotowski
Anchorage, AK 99510
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Kuukpik Corporation
Attention: Mr. Isaac Nukapigak
P.O. Box 187
Nuiqsut, AK 99789-0187
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Dated: fehWC\f13> ,2000.
~/v .?~"
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Micna .1 D. Erwin
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Declared and affirmed before me this ;)-- day of íW(ùJ,..'~:J ,2000.
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Notary Pu c ill and for Alaska
My commission Expires: '?j·t \ -5 l20C ¡
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