Department of Commerce, Community, and Economic Development
Alaska Oil and Gas Conservation Commission
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HomeMy WebLinkAbout170-053
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.~ PLUGGING & LOCATION CLEARANCE REPORT
State of Alaska
. ALASKA OIL & GAS CONSERVATION COMMISSION
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Memorandum To File: API No.
Well Name
Operator
. Location
PTD No. 70 - C9S-~
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Abnd Date '2.(61{0
Completed 12/6 Iyo
Note casing size, wt, depth, cmt vol, & procedure.
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Review the well file, and comment on plugging, well head
status, and location clearance - provide loc. clear. code.
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Location Clearance: y~ - ApEC
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ExxonMobil
Refining and Supply Company
Downstream SH&E-Environmental Remediation
1200 Timberloch Place
The Woodlands, Texas 77380-1046
AI J. Robb III
Major Projects Manager
Major Projects Upstream I Chemical
Room 304
Telephone: 281-296-3594
Facsimile: 281-296-4030
E-mail: AL_J_ROBB@email.mobil.com
EJf(onMobil
Refining & Supply
September 28, 2000
Alaska Oil and Gas Conservation Commission
3001 Porcupine Drive
Anchorage Alaska 99501-3192
Attn.: Mr. Blair Wondzell
REQUEST FOR FINAL LOCATION CLEARANCE
BELl UNIT #1
W. MOQUAWKIE #1
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Dear Mr. Wondzell:
ExxonMobil is in receipt of the letter dated August 28th, 2000 from Daniel T. Seamount,
Jr. to Mr. James Branch with ExxonMobil Production Company concerning Commission
approval of final location clearance for the two referenced sites on the North Slope of
Alaska. As a follow up to our telephone conversation on September 19th, 2000
concerning this matter, I have attached the following documentation to establish that a
favorable site visit occurred and a subsequent drilling reserve pit closure was granted
by the Alaska Department of Environmental Conservation (ADEC) at both of the
referenced well locations:
· Mobil reserve pit closure request submittal to ADEC dated January 15th, 1997 that
documents previous USGS and ADNR site closures and requests closure of the
inactive drilling reserve pit at the Beli Unit #1 wellsite.
· ADEC letter dated April 24th, 1998 documenting favorable agency site visits and
issuance of final closure approval for the inactive drilling reserve pit at the Beli Unit
#1 wellsite.
· Mobil reserve pit closure request submittal to ADEC dated November 3rd, 1998 that
documents clean site conditions and favorable agency site visits, and requests
closure of the inactive drilling reserve pit at the W. Moquawkie #1 wellsite.
RECE\VED
SEP 2. 1) ZOOO
Alaska Oil & Gas Cons. Commissìon
Anchorage
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. ADEC letter dated March 17\t1, 1999 documenting favorable agency site visits and
issuance of final closure approval for the inactive drilling reserve pit at the W.
Moquawkie #1 weUsite.
As discussed on our telephone conversation, E)(J(on Mobil Production Company
requests that final location clearance for the referenced well locations be issued by the
Commission based upon the favorable site inspections previOusly performed by ADEC
and other agencies. Please contact me at the letterhead address or at 281/296-3594 if
you have any questions or require additional information. Thank you for your time.
Sincere\y,
Attachments
Cc: Mr. James Branch, ExXonMobil, Anchorage, w/o attach.
Mr. Robert Dragnich, ExXonMobil, Anchorage, w/o attach.
RECEIVED
SEP 2 ~ 2000
Alaska Oil & Gas Cons. Gommis .
Anchorage .. SlOn
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TONY KNOWLES, GOVERNOR
ALASKA OIL AND GAS
CONSBRVATION COMMISSION
3001 PORCUPINE DRIVE
ANCHORAGE. ALASKA 99501-3192
PHONE: (907) 279-1433
FAX: (907) 276-7542
August 28, 2000
Mr. James Branch
ExxonMobil Production Company
POBox 196601
Anchorage, AK 99519-6601
Dear Mr. Branch:
A recent review of our well history database indicates that ExxonMobil Production
Company is the operator of two wells with a status of "plugged and abandoned" that
apparently have not received Commission approval of final "location clearance" as
required by 20 AAC 25.170 or 20 AAC 25.172.
The attached printout indicates that the location conditions are either "condition
unknown" or "ready for inspection." Please arrange for any necessary location clearance
work to be done and contact Blair Wondzell at (907) 793-1226 within 30 days to arrange
for Commission inspection of the location conditions.
Sincerely,
Attachment
cc: Blair Wondzell
8/23/2000
ALASKA WELLS LOCATION CLEARANCE STATUS
CLEARANCE CODES 3, 4 AND 5 BY OPERATOR
PAGE
WELL STATUS
PERMIT LOC CLEAR API NUMBER WELL NAME STATUS DATE TALLY OPERATOR
170-053 3-COND-UNKNOWN 283-20035-00 W MOQUAWKIE 1 P&A 12/06/1970 MOBIL OIL COR
172-011 4-RDY-FOR-INSP 179-20002-00 BELI UNIT 1 P&A 6/24/1973 MOBIL OIL COR
2
** THIS LIST EXCLUDES WELLS WITH LEASE FED-NPRA **
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TONY KNOWLES, GOVERNOR
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DEPT. OF ENVIRONMENTAL CONSERVATION
DIVISION OF ENVIRONMENTAL HEALTH
SOLID WASTE PROGRAM
410 WILLOUGHBY AVE
JUNEAU, ALASKA 99687
http://www.state.ak.us/dec/deh
Telephone: (907) 465-5162
Fax: (907) 465-5362
March 17, 1999
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Mr. Al Robb III, P.G.
Mobil Business Resources Corporation
P.O. Box 650232
Dallas, TX 75265-0232
Reference: Issuance of Approval for Final 'Closure for fourteen Inactive Reserve Pits located
in South Central and North Slope Alaska
Dear Mr. Robb:
The Alaska Department of Environmental Conservation (ADEC) has completed review, field
inspections, and public notice for fourteen of Mobil Business Resources Corporation's inactive
reserve pit and Closure applications and requests for fmal closure approval. The closure applications
provided the required infonnation describing the history of the site, the present condition of the site,
results of any required water sampling and an assessment of the potential risks posed by the drilling
waste to human health and the environment. ADEC coordinated review of the closure requests with
the Alaska Department of Natural Resources, the Mental Health Trust, Tyonek Native Corporation
and private land owners.
Public notice requesting comments on the closure requests was published January 19 and 20, 1999
in both the Anchorage Daily News and the Peninsula Clarion. No objections to final closure
approval were receiveå in response to the pubìic notice. ADEC has detemlÌned that the reserve pits
at this site meet all the closure requirements of 18 AAC 60.440.
Closure Approval
Under authority of 18 AAC 60.440, ADEC grants final closure approval to Mobil Business
Resources Corporation for the inactive reserve pits at the following fourteen drill sites:
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Mr. Al Robb III
March 17, 1999
Page 2 of3
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Well Name
Echooka Unit # 1
Staines River St # 1
Prudhoe Bay Unit Nom-1 ~
Hemi St 03-09-11
Kuparuk 28243-1
Mikkelsen Bay St 13-09-19
West Kadleroshilik Unit # 1
Gwydyr Bay State Unit # 1
chuit St #1 / fot -0,-0
Chuit St #2 ,=>'2. -0 Zío
Moquawkie # 1
W. Moquawkie # 1
Moquawkie # 2
Ninilchik Unit # 1
Terms and Conditions
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API Number
50-223-20008-00
50-089-20008-00
50-029-20426-00
50-029-20018-00
50-029-20573-00
50-029-20055-00
50-223-20009-00
50-029-20396-00
50-283-10005-00J
50-283-10004-00
50-283-10019-00
50-283-20035-00
50-283-20015-00
50-133-10003-00
Landowner
DNR
DNR
DNR
DNR
DNR
DNR
DNR
DNR
Tyonek Native Corporation
Mental Health Trust
Tyonek Native Corporation
Tyonek Native Corporation
Tyonek Native Corporation
Private Land - A. L. Pearl
This final closure approval is subject to the following terms and conditions:
1) In accordance with 18 AAC 60.440(1), the Department will require additional investigation,
assessment, monitoring or remediation if new information regarding conditions at the reserve
pit facilities indicates that further actions are necessary to protect human health or the
environment.
2) The approval granted by this letter is for the inactive drilling waste reserve pit(s) only.
Closure for the pad as a whole (if required) must be coordinated between the owner/óperator
and the appropriate land owner/manager.
Any person who àisagrees with any portion of this àecision may request an adjudicatory hearing in
accordance with 18 AAC 15.200-310. The request should be mailed to ,the Commissioner of the
Department of Environmental Conservation, 410 Willoughby Avenue, Suite 105, Juneau, Alaska
99801-1795. If a hearing is not requested within thirty (30) days of the date of this letter, the right
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Mr. Al Robb III
March 17, 1999
Page 3 of3
of appeal is waived. Please remember that even if an adjudicatory hearing has been requested and
granted, this decision remains in full effect during the process.
Sincerely,
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Heather Stockard
Solid Waste Program Manager
hstockar@envircon.state.ak.us
cc: Gary Schultz, ADNR, Fairbanks
Wendy Mahan, AOGCC, Anchorage
Don Karabelnikoff, Tyonek Native Corporation
A. L. Pearl, 13710 Algonquin Dr., Reno, NV 89511-7220
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Mobil Business Resources Corporation
P,O, BOX 650232
DALLAS, TEXAS 75265-0232
November 3, 1998
Mr. Judd Peterson
Alaska Department of Environmental Conservation
Division of Environmental Health - Solid Waste Program
555 Cordova Street
Anchorage, Alaska 99501
RESERVE PIT CLOSURE PLAN
SUBMITT AL FOR SITES VISITED
IN 1998
Dear Mr. Peterson:
With this submittal, Mobil provides closure plans for ·15 inactive reserve pits as required under
regulation 18 AAC 60.440(t). Based on the completion of the site visit with the landowners and
the information supplied in the attached closure plans, closure is requested for the reserve pits at
the well sites listed below:
WELL NAME
Chuit St I
Chuit St 2
Moquawkie 2
W. Moquawkie
Moquawkie 1
Happy Valley Unit 31-22
Ninilchik Unit 1
Kuparuk 7-11-12
Echooka Unit 1
Staines Riv 5t I
Prudhoe Bay Unit Nom-I
Kadler St 15-09-16
Hemi St 03-09-11
Kuparuk 28243- 1
Mikkelsen Bay St 13-09-19
API NUMBER
2831000500
2831000400
2832001500
2832003500
2831001900
23 11 0001 00
1331000300
292006200
2232000800
292000800
292042600
292001900
292001800
292057300
292005500
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Page 2
November 3, 1998
Inactive reserve pits at two additional sites (W. Kadleroshilik Unit # 1 and Gwyder Bay St Unit
# 1), previously submitted for closure under 18 AAC 60.440(b), are now also eligible for closure.
Site visits were conducted with ADEC and the landowner on September 15, 1998 in accordance
with your correspondence dated December 30, 1997.
A single check in the amount of $20,500 will be submitted under separate cover to satisfy ADEC
fee requirements for the requested closures. This check will cover payment of the $1,500 fee for
the 13 sites not previously submitted for closure, and an additional $500 each for two sites
(Kadler State 15-09-16 and Kuparuk State 7-11-12) previously submitted but ineligible for
closure under 18 AAC 60.440(b).
Mobil requests closure of the inactive reserve pits at the seventeen well sites listed in this
submittal. I can be reached at the letterhead address or at 214/951-4190 should you have any
questions or comments concerning this submittal. Thank you very much for your time.
Sincerely,
attachments
cc: distribution list attached
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DISTRIBUTION LIST:
Don Karabelnikoff, Real Estate Director for
Tyonek Native Corp.
Chuit St 1
Chuit St 2
Moquawkie 2
Moquawkie 1
W. Moquawkie
Gary Schultz, Alaska Department of
Natural Resources
Echooka Unit 1
Staines Riv St 1
Gwyder Bay St Unit 1
Prudhoe Bay Unit Nom-l
Hemi St 03-09-11
Kuparuk 28243 1
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fiNAL REPORT
INACTIVE RESERVE PIT
CLOSURE PLAN
WEST MOQUA WKIE 1
API NO: 502832003500
Prepared for
Mobil Business Resources Corporation
Dallas, Texas
November 1998
URSteiøerWøødwartl Clyde
ADMsion of URSCorpotation
. 3501 Denali Street, Suite 101
Anchorage, Alaska 99503
986003NA
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FINAL REPORT
INACTIVE RESERVE PIT
CLOSURE PLAN
WEST MOQUA WKIE 1
API NO: 502832003500
Prepared for
Mobil Business Resources Corporation
Dallas, Texas
November 1998
URS Breiner Woødward Clyde
A DMsion of URS Corporation
3501 Denali Street, Suite 101
Anchorage, Alaska 99503
986003NA
S:\PROJECTS\WCC\986003NA\Template Material\west moquawie 1,doc\8-NOV-98\966011 NA\ANC 1
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3.1. Reserve Pit List ............................................................................... ....... ....... 3-1
3.2. Site Well and Reserve Pit History ................................................................ 3-1
3.3. Site Geology, Hydrogeology, and Climatology............................................ 3-1
3.3.1. Geology .................................. ....................... ..................... ............ 3-1
3.3.2. Hydrogeology ..................... ........ ................................... ................ 3-2
3.4. Site Ecological, Biological, Historical, and Human Resources .................... 3-2
3.4.1. EcologicaV Biological Resources .................................................. 3-2
3.4.2. Sensitive and Endangered Species ............................ ..................... 3-3
3.4.3. Historical Resources ........... ........................................................... 3-4
3.4.4. Human Resources ..... ..................................................................... 3-4
3.5. Pit Condition Assessment. .................... ........................................ ................ 3-4
3.6. Sample Analysis Result Evaluation.............................................................. 3-4
3.7. Substantial Effects at Compliance Points ..................................................... 3-5
3.8. Qualitative Risk Evaluation ........................... ........ ........ ............................... 3-5
3.9. Corrective Action Evaluation ....................................................... ...... .......... 3-5
Closure Plan ............................. ...... ................. ....... ....... ....... .......... ...... ... ........... ..... ....... 3-1
2.1. Site History and Records Review.................................. ... ........ ............ ........ 2-1
2.2. Visual Observations ...... ....... ......................................................................... 2-1
2.3. Sample Collection and Analysis .......................... ............... ... .................. .....2-1
2.3.1. Surface Water................................................................................. 2-2
2.3.2. Soil............. ................. .... ... ............................................................ 2-2
2.3.3. Groundwater ..... ................. ...... ...................................................... 2-2
2.3.4. Analyses ............... .................. ........................................................ 2-3
2.3.5. Variations From Regulations Adopted 1996 ................................. 2-3
2.4. Assessment.................................................................................................... 2-3
2.4.1. Chemical Data Evaluation.. ................................................... ........ 2-4
2.4.2. Qualitative Risk Evaluation ........................................................... 2-4
2.5. Corrective Action Evaluation ...... ......... ........................................ ................ 2-4
Clos ure Approach. ..................... .................................................................................... 2-1
1.1. Drilling Wastes and Disposal Practices ................................... ............. ........ 1-1
1.2. Drilling Waste Management Regulations..................................................... 1-2
1.3. Regulatory Requirements............... ...... ......................................................... 1-3
1.3.1. Closure Plan 18 AAC 60.440(F).................................................... 1-3
1.3.2. Closure Conditions 18 AAC 60.440(J) .......................................... 1-3
1.3.3. Landowner Notification 18 AAC 60.440(K) ................................. 1-4
1.3.4. Closure Plan Addition for Pit Not Found 18 AAC
60.440(H) .................................... .. .. .. . . . . ... . . .. . . . . . . . .. . . . . .. . . . . . . . . . . . . . .. .. 1-4
Introduction ...... ............ ............. ......... ............................................................................ 1-1
Section 3
Section 2
Section 1
Acronym List .......... ...................... ........ ....... .......... ................................................................................... i ii
TABlE OF CONTENTS
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TABLE OF CONTENTS
3.10. Corrective Action Proposal. ............. ,.. ...... ..... ......... ........ ... .................... ..... 3-5
Section 4
Summary and Conclus ions. ............................. ...................................... ....................... 4·1
Section 5
References ......... ..... ........ ...... ..... .......... ..... ..................................... ... ......... ... .................. 5·1
LIST OF TABLES
Table 3-1 Results of Risk Screening Model
LIST OF FIGURES
Figure 2-1 Risk Evaluation Methodology
Figure 3-1 Vicinity Map
Figure 3-2 Topographic Map
Figure 3-3 Aerial Photograph
Figure 3-4 Site Map
LIST OF APPENDICES
Appendix A Water Quality Criteria Detennination
Appendix B Risk Screening Methodology
Appendix C Field Notes
ORS Greiner WlHHIwanI C1yrJe
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ACRONYM liST
AAC
ADEC
ADF&G
ADNR/DOG
AOGA
AOGCC
AWQS
BTEX
DRO
EPA
KPB
LUFT
PCB
TEPH
USFWS
USFS
USGS
VPH
Alaska Administrative Code
Alaska Department of Environmental Conservation
Alaska Department ofFish and Game
Alaska Department of Natural Resources, Division of Oil and Gas
Alaska Oil and Gas Association
Alaska Oil and Gas Conservation Commission
Alaska Water Quality Standards
Benzene, tolune, ethylbenzene, xylenes
Diesel range organics
United States Environmental Protection Agency
Kenai Peninsula Borough
Leaking underground fuel tanks
Polychlorinated biphenyl
Total extractable petroleum hydrocarbons
United States Fish and Wildlife Service
United States Forest Service
United States Geological Survey
V olatile petroleum hydrocarbons
URS &reJner WDtJdwanJ CIydø
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SECTIINONE
Introduction
This closure plan is submitted by Mobil Business Resources Corporation (Mobil) for the inactive
reserve pit associated with the West Moquawkie 1 well. It was prepared in accordance with
Alaska Department of Environmental Conservation (ADEC) inactive reserve pit closure
regulatory requirements found in 18 Alaska Administrative Code (AAC) 60.440, and Interim
Site Assessment Guidance for Inactive Drilling Waste Sites (ADEC 1991). Section 1
summarizes historical drilling waste management practices, the history of drilling waste
regulations, and current inactive reserve pit closure requirements. Section 2 discusses the approach
used to fulfill ADEC closure requirements. Section 3 includes all information stipulated by ADEC
closure requirements, and Section 4 provides a summary of the findings and conclusions.
1.1. DRilliNG WASTES AND DISPOSAL PRACTICES
This historical overview traces the waste management' practices that have evolved over the last
half-century of oil exploration in Alaska. This overview is supplementary to the site-specific
drilling records that frequently cannot be located.
During the drilling of oil and gas wells, drilling mud is circulated in the drill hole for a number of
reasons including:
. To bring cuttings to the surface
· To cool and lubricate the drill bit and stem
· To counterbalance formation pressures, thereby reducing the chance for blowouts
· To coat the borehole and prevent loss of fluids to subsurface formations
A portion of formation cuttings and drilling mud generated during the drilling process must be
managed as waste at the end of each drilling project.
Drilling mud is composed of bentonite clay suspended in fresh water, salt water, or oil. A variety
of other additives may be added to give the drilling mud specific properties; the choice of
additives is dependent on the downhole conditions of the specific well, and they generally have
low toxicity.
Drilling waste quantities have been drastically reduced over the years through improved drilling
techniques. Current drilling programs maximize recirculation of drilling muds to reduce both the
raw materials cost and the amount of drilling waste.
Until the mid-1980s, drilling wastes from onshore wells were disposed of in on-site reserve pits.
Reserve pits were designed to provide secondary containment in the event of a spill or blow-out.
Reserve pit structures were built adjacent to the drilling pad. The pit was generally located to
minimize the distance between the well and the pit.
In permafrost areas, gravel berms approximately three to five feet high were constructed to
contain muds and cuttings placed directly on the tundra/land surface. Some of the early pits were
excavated, and muds and cuttings were placed below-grade within gravel berms. Where there
was no permafrost, drilling sites were often constructed by clearing surface vegetation and
digging a below-grade reserve pit.
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SECTIDNONE
Introduction
At the end of drilling operations, liquids that accumulated in reserve pits were often pumped to
the subsurface, minimizing the amount of liquid waste. The remaining reserve pit solids were
customarily covered with gravel or native soils before the site was abandoned.
Since the rnid-1980s, drilling activities have mainly occurred at the North Slope oil fields. Most
on-shore North Slope exploratory wells have been drilled from ice pads. Muds and cuttings are
stored in ice pits until completion of the well. After completion, the muds and cuttings are
ground and re-injected into the exploratory well, or are transported to development areas for
injection or placement in regional below-grade disposal facilities.
1.2. DRilliNG WASTE MANAGEMENT REGULATIONS
Throughout the years, numerous governmental agencies and commissions have regulated
Alaskan oil and gas exploration and production activities, including the handling and disposal of
drilling waste. The table below lists key milestones in the historical evolution of drilling waste
management regulations, and entities responsible for regulatory enforcement and oversight.
Date Event
Pre-1955 United States Geological Survey (USGS) regulates all oil and gas operations in Alaska. At this time, there are no
special requirements for drilling waste management.
1955-1959 Oil and Gas Commission is created to regulate drilling operations including disposal of produced waters, non-
potable waters, and oil field wastes.
1959-1979 Alaska Department of Natural Resources, Division of Oil and Gas (ADNRlDOG) takes over responsibilities
performed by the oil and gas commission.
1971 ADEC is created and given statutory authority for oversight of state environmental matters, including solid waste
management. At this time, no special provisions are made for management of drilling wastes.
1979 Alaska Oil and Gas Conservation Commission (AOGCC) is created to regulate oil and gas activities. AOGCC's
responsibilities include annual site inspection for suspended wells, and final site clearance for wells that have
been plugged and abandoned.
1983 ADEC promulgates 18 AAC 60 for regulation of solid waste.
1983 ADNR/DOG requires that solid waste disposal (including drilling wastes) be discussed in the Plan of Operations
for each drilling program.
1984 AOGCC is granted primacy for oversight of drilling waste disposal to the subsurface (Class 1\ disposal).
1987 ADEC revises 18 AAC 60, and adds design, construction, operation, and closure requirements for new reserve
pits.
1989 ADEC requires closure of inactive reserve pits. No specific closure requirements are stipulated, but oil and gas
operators are required to submit a list of their reserve pits to ADEC within 18 months.
1990 Alaska Oil and Gas Association (AOGA) establishes a Solid Waste Task Force to develop methods for inactive
reserve pit closure. An advisory committee is formed shortly afterward, composed of ADEC, industry
representatives, and environmental organizations. The industry representatives advocate a risk-based,
qualitative decision framework for separating sites with negligible risk from those where corrective action should
be considered.
1991 ADEC releases draft reserve pit closure guidance, Interim Site Assessment Guidance for Inactive Drilling Waste
Sites. This document contains guidance on recommended number and type of sampling points, analysis
parameters, site observations, risk assessment screening methodology, and possible corrective actions.
1993 ADEC releases draft revised regulations 18 AAC 60 for public comment. These draft regulations contain specific
requirements for closure of inactive reserve pits.
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SECTIDIONE
Introduction
1996 ADEC revises 18 AAC 60 and adds closure requirements for inactive reserve pits,
1.3. REGULATORY REQUIREMENTS
The ADEC enacted revised regulations for Solid Waste Management (18 AAC 60) on January
28, 1996. Section 440 of these regulations require the following for closure:
· Closure plan (18 AAC 60.440(f))
· ADEC approval for closure (18 AAC 60.4400))
· Landowner notification (18 AAC 60.440(k))
If a reserve pit is not found, the closure plan must include documentation of a reasonable search
according to 18 AAC 60.440(h).
The regulatory requirements for closure are discussed in greater detail in the following sections.
1.3.1. Closure Plan 18 AAC 60.440(f)
The table below cross-references closure plan regulatory requirements with the specific sections
of the report where the infonnation appears.
ADEC Closure Plan Requirements Report Section
(1 ) List of reserve pits known or believed to exist at the site 3.1 Reserve Pit List
(2) A brief history of the construction and use of the reserve 3.2 Site Well and Reserve Pit History
pit, including current status
(3) Site geology, hydrogeology, and climatology 3.3 Site Geology, Hydrogeology, and Climatology
(4) Site economic, biological, ecological, historical, and human 3.4 Site Ecological, Biological, Historical, and Human
resources Resources
(5) An assessment of the pit's existing condition, based on its 3.5 Pit Condition Assessment
use,age,andlocation
(6) The results of the sampling and chemical analysis 3.6 Sample Analysis Results Evaluation
(7) Qualitative discussion of substantial effects on water, 3.7 Substantial Effects at Compliance Points
groundwater, soil, or sediment
(8) A qualitative discussion of material, probable risks to public 3.8 Qualitative Risk Evaluation
health or the environment posed by the pits, and any
feasible corrective action that might eliminate, mitigate, or
abate the risks
(9) Analysis of the feasible corrective actions 3.9 Corrective Action Evaluation
(10) A proposal to implement or refrain from implementing 3.10 Corrective Action Proposal
corrective action
1.3.2. Closure Conditions 18 AAC 60.4400)
Section 3 of this report documents how the site fulfills the closure conditions of 18 AAC
60.4400). Closure conditions include:
· 0)(1) Pit is not found
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Introduction
· 0)(2) No further action if no material or probable risks to public health or environment is
present as detennined by:
- levels at the point of compliance are below Alaska Water Quality Standards (A WQS) or
background
- the pit contains exposed drilling waste but does not hold water
- evidence of ponded water is present and an A WQS has been violated, but the violation
presents no material risk to public health or the environment, or the violation is not
caused by the drilling waste
· 0)(3) Corrective. action to the satisfaction of the Department is implemented
· 0)(4) Owner/operator demonstrates that the effects of feasible corrective action exceed the
benefits
· 0)(5) Owner/operator demonstrates that the water pollution is diminishing
1.3.3. Landowner Notification 18 AAC 60.440(k)
Section 18 AAC 60.440(k) requires notification of private landowners at the time of the
pennanent site closure request. ADEC and landowner representatives accompanied Mobil
personnel and contractors, as part of the site visit in September 1998. Section 3 of this report
lists site visit dates and names of field participants, including landowners. This closure plan will
be sent to the applicable landowner(s), as documentation of the closure request.
1.3.4. Closure Plan Addition For Pit Not Found 18 AAC 60.440(h)
If the pit is not found, additional supporting documentation must be included:
· Names of persons conducting the search
· Field notes documenting the search
· Recent aerial photograph of the area searched (photograph scale of 1 inch equals 200 feet)
The minimum reasonable search shall be one of the following:
· Four man-hour search by foot using a 7.5 minute series quadrangle topographic map
· One-half hour helicopter survey
· Aerial magnetometer survey
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Closure Approach
The closure requirements of 18 AAC 60.440 were met using the following components:
· Site history and records review
· Visual observations made during a site visit
· Sample collection and analysis
· Assessment including a qualitative risk screening
· Corrective action evaluation (if necessary)
This section describes the approach taken to ensure that this assessment program meets the
closure requirements.
2.1. SITE HISTORY AND RECORDS REVIEW
All known and readily available ADEC and AOGCC files and records were researched to locate
information about the reserve pit associated with the West Moquawkie 1 well. This information
was used to evaluate the site history and environmental setting to fulfill closure plan
requirements 18 AAC 60.440 subsections (f)(2) through (f)(4).
2.2. VISUAL OBSERVATIONS
The field personnel noted observations on field checklists and in field notebooks, and
documented field conditions with photographs. Specific field information required to support
the closure plan submittal included:
· General site information such as date of visit, field personnel, and weather conditions
· Photographs showing site conditions
· Biological, hydrological, ecological, geological, and economic observations
· Assessment of reserve pit condition
· Site map showing site observations
2.3. SAMPLE COLLECTION AND ANALYSIS
Sample collection and analysis requirements for inactive reserve pit closure were generally based
on the Interim Site Assessment Guidance for Inactive Drilling Waste Sites dated 1991. The
regulations were finalized in 1996, five years after the sample collection site visit. The type of
samples, sampling locations, and analyses taken are based on all of the following:
· Sampling methodology described on page four through six of the guidance
· Site specific conditions
· Historic information about waste disposal practices at the site
· Statistical significance desired to be achieved with the information gathered
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2.3.1. Surface Water
· Measure surface water conductivity and pH around the perimeter of the site. Use 50-foot
intervals and take measurements as close as possible to the site.
· Collect water samples at the two locations within 50 feet of pad perimeter which have the
highest conductivity and/or pH field readings. If two locations can not be identified, take
water samples at the two closest downgradient locations.
· Collect a water sample for any standing water in the reserve pit or any standing water in drill
pad depressions exceeding 50 square feet. Measure pH and conductivity for the sample.
· Collect water samples at two upgradient locations at least 200 feet from the edge of the pad.
· Collect a water sample of any seepages from the drill pad; measure conductivity and pH of
the sample.
A water body was considered to be appropriate and was sampled only if the data could be used to
evaluate whether a release had occurred from an upgradient reserve pit. For some of the Mobil
sites, the only downgradient water body within 1,000 feet of the reserve pits is a flowing stream,
or a large coastal water body such as Cook Inlet or Prudhoe Bay. Not only would contaminants
from the inactive reserve pit released to these types of water bodies be quickly diluted and
dispersed, but potential influence from contaminant sources other than the targeted inactive
reserve pit would cause difficulty in fonning conclusions. Thus, no water samples were
collected from these type of water bodies because analysis of any data obtained would not be
representative of surface water conditions affected by the reserve pit.
Analytical results for samples collected from background (upgradient or cross-gradient) water
sources are used to assess natural conditions at the site. Background water samples are collected
from water bodies that do not appear to have been or could have been adversely impacted by
human activities, and have similar characteristics with downgradient water bodies.
2.3.2. Soil
· Collect soil samples of reserve pit drilling muds.
· Collect one background sample.
While not required for reserve pit closure under 18 AAC 60.440( e), discretionary soil samples
were typically coll~cted and analyzed when visual evidence of a release was present (e.g., a large
area of stained soil, distressed vegetation).
2.3.3. Groundwater
· Groundwater will be sampled whenever there are public water systems groundwater
withdrawal points within 1,000 feet of the site.
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2.3.4. Analyses
The samples were analyzed for selected organic and inorganic constituents. Analyses for organic
constituents included benzene, ethylbenzene, toluene, and xylenes (BETX), Total Volatile
Petroleum Hydrocarbons (TVPH), Total Extractable Petroleum Hydrocarbons (TEPH), and
polychlorinated biphenyls (PCBs). Analyses for inorganic constituents consisted of the
following metals: aluminum, barium, cadmium, chromium, lead, mercury, nickel, potassium,
sodium, zinc, and chloride.
Water collected for inorganic analyses were submitted as both unfiltered and filtered samples.
Samples were filtered in the field using disposable 0.45 micron filters. Unfiltered samples were
analyzed to measure total metals and filtered samples were analyzed to measure dissolved
metals. F or chloride, only total chloride was measured. In addition, field measurements of water
samples were taken for pH, conductivity, and temperature.
2.3.5. Variations from Regulations Adopted 1996
· The differences between the guidance followed during Mobil's 1991 assessment program and
the regulations now in place are relatively minor. Differences include:
· The 1991 guidance did not specify a maximum distance for a surface water sample near the
reserve pit. Samples up to 50 feet :trom the pad were collected during the Mobil sampling
program. The regulations extended the range of perimeter surface water samples up to 1,000
feet :trom the drill pad, and denoted samples within 50 feet as the point of compliance.
· The 1991 guidance methodology screened conductivity and pH readings of water around the
perimeter of the pad to select surface water sample locations. The regulations specify
sampling locations in reference to the reserve pit location.
· The regulations added arsenic, nickel and hardness (based on calcium and magnesium
analyses) as analytes. The guidance listed mercury, PCBs, aluminum, cadmium and
potassium as analytes, not required by regulations.
· The regulations have sodium as an analyte, while the guidance listed chlorides and salinity.
· The regulations do not require collection of any drill mud or soil samples.
· The organic analyses in the 1991 guidance document were Total Extractable Petroleum
Hydrocarbons and Volatile Petroleum Hydrocarbons using EPA 8015M meeting the
California LUFT program. The regulations required Diesel Range Organics and BETX using
EP A 8100M. These methods are all gas chromatograph methods which differ slightly in
target carbon ranges that they are designed to measure.
2.4. ASSESSMENT
The assessment has two components: chemical data evaluation for compliance point samples,
and qualitative risk evaluation to detennine whether a material or probable risk to public health
or the environment exists.
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2.4.1. Chemical Data Evaluation
The chemical data evaluation establishes whether the compliance point sample exceeds
applicable water quality standards. Appendix A presents a detailed discussion of how water
quality standards were selected from among the relevant water quality criteria.
2.4.2. Qualitative Risk Evaluation
The risk screening process from Section III of ADEC's Interim Site Assessment Guidancefor
Inactive Drilling Waste Sites (ADEC 1991) was used to detennine risk, since 18 AAC 60.440
does not specify a qualitative risk screening approach. Only the risk screening section of the
guidance document (Section III) has been incorporated. Sections I, II, and V of the guidance
document have been superseded by the regulations in 18 AAC 60.440 and Section IV was not
applicable. Based on discussions with ADEC staff, two modifications to the risk screening
guidance were made:
· The requirement to evaluate corrective action is eliminated from Step 1, if risk is found to be
negligible
· An option to perform a risk assessment is added to Step 2, if the risk screening approach
indicates significant risk
The risk screening process employs a two-step approach to evaluate risk. The first step
establishes if there is a basis of concern. A basis for concern is established if evidence of a
release or a mechanism for potential release is present (based on visual observations and review
of analytical results from water samples), and there is proximity of the reserve pit to biological
receptors. If there is none, the risk is determined to be negligible and site closure is warranted.
If there is a basis of concern, the second step is to evaluate whether the concern constitutes a
significant risk. The finding of significant risk is based on the likelihood of exposure and the
likelihood of adverse consequences of exposure. If the risk is not significant, then site closure is
warranted. In cases where risk is determined to be significant, a corrective action plan is
developed, approved by ADEC, and implemented; or a risk assessment is performed. A risk
assessment is more rigorous than the risk screening process described above, including a detailed
analysis of all site-specific conditions.
Figure 2-1 presents a flow chart of the risk evaluation methodology. Appendix B contains a
detailed discussion of the process.
2.5. CORRECTIVE ACTION EVALUATION
The site assessment may indicate that corrective action should be evaluated for the site.
Corrective action is considered if there is evidence of a release of contamination to water at the
point of compliance, and a risk evaluation detennines that there is a material or probable risk to
public health or the environment. The responsible party may then:
· Propose corrective action and an implementation schedule
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Propose a monitoring program to establish whether contaminant levels are increasing or
diminishing.
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EVALUATION CRITERIA
*SteD 1. Basis of Concern Criteria:
** SteD 2. Sianificance of Risk - EXDosure Criteria:
** SteD 2. Sianificance of Risk - Conseauence Criteria:
· Evidence of release of chemical contamination in
excess of Alaska Water Quality Standards, OR
mechanism for potential release, AND
· Proximity of site to receptors
· Contaminant release mechanisms are significant,OR
contaminant migration potential is significant, OR chemical is
environmentally persistent
· Duration of frequency of exposure AND EITHER,
· Quantity or concentration of one or more contaminants exceeds
federal or state water quality standards or other protective
standards, OR chemical exhibits high acute toxicity
FIGURE
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Closure Plan
West Moquawkie 1 is located on the west side of the Cook Inlet, 4 miles inland from the coast. Figure
3-1 is a general location map, and Figure 3-2 is vicinity topographic map showing the site
location.
Chris Holden and Diana Evans (Woodward-Clyde) along with John Winston (Mobil) conducted
a site assessment during August 1991. Al Robb (Mobil), Judd Peterson (ADEC), and landowner
Don Karabelnikoff (Tyonek Native Corporation) conducted the site inspection on September 17,
1998. Appendix C contains the field notes for the site visits.
3.1. RESERVE PIT LIST
West Moquawkie 1 (API Number 502832003500) was the only well drilled from the pad.
Review of drilling files did not establish the existence of a reserve pit. A reserve pit location
could not established during the site visits. The pad was level without subsidence or benns
which indicate reserve pit location. However, based on drilling practices used at the time when
the well was drilled, it was assumed that a reserve pit was used to store drilling wastes.
3.2. SITE WELL AND RESERVE PIT HISTORY
This well was originally completed as an exploratory well by Mobil Oil Company in 1970. The
current well status is plugged and abandoned. The legal description of the well location is
Section 36, Township 12N, Range 12W, Seward Meridian. Longitude/Latitude readings
indicated that the revegetated gravel pad is· the location of West Moquawkie 1. A well marker
found at the site provided positive identification. The well marker was found in brush in the
central/western edge of the pad, cut off from the well head. An area in the center of the pad with
wood debris and grout piles is the likely wellhead location. No ADEC or AOGCC records were
located during the record search.
Figure 3-3 presents an aerial photograph of the site taken during the 1991 site visit. Figure 3-4 is
a site map made based on observations during the 1991 site visit. Drill pad boundaries
encompass an area of approximately 250 feet by 280 feet.
3.3. SITE GEOLOGY, HYDROGEOLOGY, AND CLIMATOLOGY
3.3.1. Geology
As previously stated, West Moquawkie 1 is located on the west side of the Cook Inlet.
Geomorphologic features resulting from Pleistocene glaciation are evident throughout the Cook
Inlet region, and are responsible for many distinctive land features, including glacial troughs,
extensive U-shaped valleys, scoured valley floors, broad outwash plains, and marshy lowlands.
Unconsolidated glacial deposits, typical of the lowland areas surrounding Cook Inlet, have been
deposited and reworked by three main agents: glacial ice, flowing water in streams or deltas, and
still water in ponds, lakes, and marine estuaries.
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3.3.2. Hydrogeology
3.3.2.1. Groundwater
Groundwater tends to flow toward Cook Inlet from lowland regions. No specific infonnation
about local ground water at the site was available. During the site visit, no drinking water wells
were found within 1,000 feet of the drill site.
3.3.2.2. Surface Water
There are several small rivers and streams in the area, such as the Beluga and Chuitna Rivers.
Tyonek Creek is approximately ~ mile southwest of the site. Area rivers and streams are
generally silt laden, with a high sediment load. There are numerous lakes and ponds in the area,
most of are frozen from November to May. Area streams may freeze later and thaw earlier than
the lakes and ponds.
The West Moquawkie 1 site is situated on a relatively level area and surrounded by dense
vegetation. There was no obvious drainage pattern at the site, but it is assumed that surface
water runoff from the pad eventually drains towards Cook Inlet. Except the Tyonek Creek, there
was no surface water evident in the vicinity of this drill site within 'l2 mile.
3.3.2.3. Climatology
Coastal areas of Cook Inlet experience weather conditions that are characteristic of a transition
climatic zone. Generally, the transition zone consists of a band of varying width between the
maritime and continental climatic zones. Climate at the site is variable; it may be continental,
maritime, or a combination, resulting in temperatures and precipitation that are more extreme
than maritime, but less than continental.
Cook Inlet is a major factor moderating area climate. Temperatures seldom rise above 80°F in
summer or drop below -30°F in winter. Wind velocities rarely exceed 38 knots and average
about 6 knots in lowland areas. Annual precipitation converted to rainfall ranges from 15 to 20
inches. Snow cover is typically present at the site between mid-November and mid-March.
3.4. SITE ECOLOGICAL, BIOLOGICAL, HISTORICAL, AND HUMAN RESOURCES
3.4.1. Ecologicall Biological Resources
The West Moquawkie 1 site is located in a spruce/hardwood forest (ADF&G 1984). There is a
fairly dense mixed forest in the site vicinity. The plant community is characterized by spruce
(Picea spp.), birch (Betula spp., quaking aspen (Populus trem ulo ides ), black cottonwood
(Populus balsamifera spp. trichocarpa), and balsam poplar (Populus balsamifera spp.
balsamifera) (ADF&G 1984, Fall et al. 1984). Shrubs include willow (Salix spp.), alder (Alnus
spp.), rose (Rosa spp.), high bush cranberry (Viburnum edule), and raspberry (Rubus idaeus
subsp. melanolasius).
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Numerous species of birds and mammals occur in the vicinity of the West Moquawkie 1 site
(Fall et al. 1984, USFWS 1985, ADF&G 1988). Evidence of moose (Alces alces) was observed
during the site inspection. Although not observed, many other mammals are common to the
community. Larger mammals include bear (black Ursus american us and/or brown Ursus
horribilis arctos), coyote (Canus latrans), and gray wolf (Canus lupus). In addition small
rodents such as mice, voles, and bats, and fur bearers such as snowshoe hare (Lepus americanus),
red squirrels (Tamiasciurus hudsonicus), muskrat (Ondatra zibethicus), red fox (Vulpes vulpes),
weasels (Mustela nivalis), wolverines (Gulo gulo), marten (Martes americana), mink (Mustela
vison), lynx (Felis lynx canadensis), river otter (Lutra canadensis), and beaver (Castor
canadersis) are found.
Bird species likely to be present in the vicinity of the West Moquawkie 1 site include various
species of songbirds which may nest in forest habitats such as sparrows (Passerculus
sandwichensis Spizella arborea and Junco spp.), warblers (Dendroica spp.), flycatchers
(Empidonax trailli and Contopus borealis), swallows (Iridoprocne bicolor), blackbirds
(Euphagus spp.), chickadees (Parus spp.), and thrushes (Hylocichla spp.). Raptors include the
great homed owl (Bubo virgin ian us ), marsh hawk (Circus cyaneus), goshawk (Accipiter genti/is
laingi), bald eagle (Haliaeetus leucocephalus), and osprey (Pandion haliaetus).
Upwards of several hundred thousand ducks and geese use the coastal areas of the upper Cook
Inlet as feeding and resting areas during spring and fall migration (ADF &G 1988). However,
these waterfowl are generally concentrated in the wetlands seaward of the site. Trumpeter swan
(Cygnus buccinator) nesting and breeding habitat is located on the east side of the Beluga River,
approximately 20 miles northeast of the site (ADF&G 1984).
Spawning, rearing, and migration of Dolly Varden (Salvelinus malma), whitefish (Coregonus
clupeaformis), rainbow trout (Salmo gairdnerii), and king, pink, coho, sockeye, and chum
salmon (Oncorhynchus spp.) occur in streams throughout the area (ADF&G 1984). It is unlikely
that these commercially valued resources would be exposed to site reserve pit contaminants,
since there was no evidence of a release or mechanism for potential release present.
3.4.2. Sensitive and Endangered Species
As shown in Appendix B, Table B 1, certain threatened, endangered, or species of special concern
have been identified for Alaska. Although none were observed during the site visit, the
following describes the species that may be encountered in the vicinity of West Moquawkie 1:
· American peregrine falcon (Falco peregrinus anatum), United States Fish and Wildlife
Service (USFWS) endangered species, and Peale's peregrine falcon (Falco peregrinus
paelei), United States Forest Service (USFS) sensitive species - depend on cliffs for nesting
sites but may be casual visitors or may pass through the vicinity of the site during migration.
· Trumpeter swan (Cygnus buccinator), USFS sensitive species - utilize nesting areas located
to the east of the Beluga River, and may be visitors to the vicinity of the site.
· Osprey (Pandion haliaetus), USFS sensitive species - utilize river, lake and coastal habitats,
nest in dead trees, rock pinnacles and on ground surfaces, and may be in the vicinity of the
site.
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· Northern goshawk (Accipiter gentilis laingi), Olive-sided flycatcher (Contopus borealis),
black-poll warbler (Dendroica striata), and gray-cheeked thrush (Catharus minimus), Alaska
Department ofFish and Game (ADF&G) species of concern - all may be found in mixed
forests typical of the West Moquawki~ 1site (ADF&G 1988).
· Townsend's warbler (Dendroica townsendi), ADF&G species of concern - usually found in
deciduous forests of the region (ADF &G 1988) but may rarely occur in mixed forests typical
of the site.
· Lynx (Felis lynx canadensis), ADF&G species of concern - has a limited distribution
confmed primarily to the northern boreal forest, prey primarily on snowshoe hare which are
ubiquitous in the mixed forest habitat, and therefore may be found in the vicinity of the West
Moquawkie 1 site.
3.4.3. Historical Resources
Basic regional industries include oil and gas production, fishing, fish processing, recreation,
tourism, transportation and support services, mining, and timber harvesting.
Natural gas was discovered in the Beluga River area in 1962. Since that time, refmeries and
processing plants have accompanied development of oil and gas fields in the site vicinity.
Chugach Electric Association Beluga Power Plant has been in operation since 1963.
Recreational and commercial fisheries (both salmon and halibut) are also important economic
resources for the Kenai Peninsula.
3.4.4. Human Resources
The site investigated in this report is in the northwest portion of Kenai Peninsula Borough
(KPB). The village ofTyonek, the closest permanent human settlement, is approximately 6
miles east of the site. Tyonek is a Native community with a population of 148. Located 43 air
miles from Anchorage, with no connecting roads, Tyonek is isolated from other populated areas.
Tyonek residents participate in subsistence harvest of natural resources, and commercial fishing
provides livelihood for some residents.
3.5. PIT CONDITION ASSESSMENT
No evidence of a reserve pit was present during the site visit. The wellhead location was not
determined, since the well marker was found cutoff on the pad. The surface of the drill pad was
covered with gravel, and no standing water was present. Potential contaminant release
mechanisms are absent, since no surface water is in contact with or perched over probable
reserve pit wastes.
3.6. SAMPLE ANALYSIS RESULT EVALUATION
No samples were collected at West Moquawkie 1 since there was no pad or perimeter water
present at the stie.
URS BreIner WIJødward Clyde
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SECTIINTHREE
Closure Plan
3.7. SUBSTANTIAL EFFECTS AT COMPLIANCE POINTS
There was no surface water present at the drill site perimeter during the site visit. No drilling
waste was in contact with surface water. Therefore, mechanisms for potential release and
significant migration pathways are absent, indicating that the substantial effects at surface
compliance points are limited.
There were no drinking water wells within 1,000 feet of the drill site location. Both the 1991
guidance and regulations do not require evaluation of a groundwater pathway unless a public or
private groundwater withdrawal system is located within 1,000 feet of the reserve pit boundary.
No impacts through groundwater are possible if water receptors are not present.
3.8. QUALITATIVE RISK EVALUATION
The qualitative risk screening process introduced in Section 2.4.2 was used to make the risk
screening evaluation. The risk screening process uses two steps to make this determination. The
first step establishes if there is a basis of concern. If there is none, the risk is determined to be
negligible and site closure is warranted. If there is a basis of concern, it is necessary to determine
if that concern constitutes a significant risk. If the risk is not significant, then site closure is also
warranted. In cases where risk is determined to be significant, a corrective action plan is
developed and implemented. Screening methodology is discussed in detail in Appendix B.
Results of the risk screening model are summarized in Table 3-1.
The inactive potential reserve pit and associated drilling waste are assumed to be covered. There
was no visual evidence of contamination associated with the reserve pit. Therefore, no evidence
of a release of chemical contamination was present. In addition, no mechanism for release was
present since the potential reserve pit was covered, and there was no surface water perched over
the probable reserve pit.
There are biological receptors present and nearby. The site is accessible by road, and the town of
Tyonek is located approximately six miles from the site. Visits by area hunters and local
inhabitants are possible. Evidence of site use by wildlife existed; however no wildlife, including
threatened and endangered species, was present during the site visit.
Although receptors were identified in the site vicinity, any risk posed by the site is negligible,
since no evidence of contaminant release or mechanism for release was found.
3.9. CORRECTIVE ACTION EVALUATION
The results of the risk model indicate any risk , currently posed is negligible. Therefore, a
corrective action evaluation is unnecessaÍy.
3.10. CORRECTIVE ACTION PROPOSAL
Since negligible risk has been demonstrated for this site, the recommended corrective action is
no action.
UII$ SreInIIr WlHHIwanl C/yIJÐ
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SECTIINTHREE
Closure Plan
TABLE 3-1
RESULTS OF RISK SCREENING MODEL
WEST MOQUAWKIE 1
Criterion
Outcome
Rationale
Conclusion
Is there a reserve pit? Yes Below-grade reserve pit is Potential target
assumed but probable location constituents on
can not be detennined. Entire site
pad surface covered with
gravel, no evidence of
exposed drilling waste.
Evidence of release? No No visual evidence of No evidence of
contamination (no water or release
soil samples collected).
Mechanism for potential No No surface water in contact No potential
release? with or perched over reserve release
pit wastes. mechanism
present
Receptors present or nearby? Yes Accessible by humans. Receptors
Evidence of human use and present
wildlife in area.
,Exposure criteria met? NA Not applicable.-No basis for concern.
Consequences criteria met? NA Not applicable.-No basis for concern.
RISK CONCLUSION: Risk is negligible.
Ull$1lreJnør WDødwanI C/Jf/Ø
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SOURCE: USGS MAP
TYONEK (A-3). ALASKA. SERIES 1 :63.360
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COOK INL.ET AREA
ALASKA
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SECTIONFOUR
Summary and Conclusions
The qualitative risk screening presented in Section 3.8 established that there is no basis for
concern_ Therefore, Mobil requests that the West Moquawkie 1 reserve pit be closed under
regulation 18 AAC 60.440 (f), based on the following:
· There is no visual evidence of chemical contamination (e.g., large area of stained soil,
distressed vegetation) on or around the drill pad.
· The drill site (including the .reserve pit) is assumed to be covered with gravel, and no exposed
drilling waste is present. Therefore, mechanisms for potential contaminant releases are
absent.
· No drilling waste is in contact with surface water. Also, no surface water is located on the
pad. Therefore, significant migration pathways are absent, indicating that mobility of
possible contaminants are limited.
· No drinking water supplies are endangered by the site.
· No threatened or endangered species were seen at the site during the site visit, and no
economically or commercially important species are endangered by the site.
· Representatives of ADEC and landowner Don Karabelnikoff (Tyonek Native Corporation)
inspected the site on September 17, 1998.
IJRS BreInIJt WøødwanI C/Jf/B
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SECTIINFIVE
References
Alaska Department of Community and Regional Affairs, Division of Community Planning.
1997. Tyonek Community Profile.
Alaska Department of Environmental Conservation, (ADEC), January 28, 1996. Solid Waste
Management Regulations (18 AAC 60), Juneau, Alaska.
Alaska Department of Environmental Conservation (ADEC). June 1991. Interim Site
Assessment Guidance for Inactive Drilling Waste Sites.
Alaska Department ofFish and Game (ADF&G). 1988. Susitna Flats State Game Refuge
Management Plan. Prepared by the Divisions of Habitat and Game, ADF&G,
Anchorage, Alaska.
Alaska Department ofFish and Game (ADF&G). 1984. Susitna Basin Area Plan, Fish and
Wildlife Element. Prepared by Division of Habitat, ADF&G, Anchorage, Alaska.
Alaska Geographic, Vol. 9, Number 4, 1982. Alaska's Oil/Gas and Minerals Industry.
Baroid Drilling Fluids, Inc. 1990. Manual of Drilling Fluids Technology.
Fall, J.A., D.J. Foster, and R.T. Stanek. 1984. The Use ofFish and Wildlife Resources in
Tyonek, Alaska, ADF&G Division of Subsistence, Technical paper No. 105.
Jones, F.V., C.M. Moffitt, W. Bettge, R. Garrison, and A.J.J. Leutennan. Nov. 1986. Drilling
fluids finns respond to EPA toxicity concerns. Oil and Gas Journal 1986:71-77.
United States Fish and Wildlife Service (USFWS). 1985. Kenai National Wildlife Refuge Final
Comprehensive Conservation Plan, Environmental Impact Statement.
Zenone, Chester, and Gary Anderson. 1978. Summary Appraisals of the Nation's Ground Water
~ Resour.ces,....AJaska~ ..USGS·,PFofessional.P.aper. 8.l3~P-......·,~...".......
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Appendix A
Water Qualitv Criteria Determination
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Appendix A
Water Qualitv Crileria Delenninadøn
Alaska Water Quality Standards (A WQS) in 18 AAC 70 specify standards for the protection of
aquatic life and human health for marine and freshwater bodies. Sample salinity determines
whether to use freshwater or marine aquatic life criteria at a specific site. Freshwater aquatic life
criteria are applied where salinity is less than or equal to 1 part per thousand (ppt) [40 CFR
131.36 (c)(4) and 18 AAC 70.040]. However, salinity was not included as a sample parameter in
the 1991 field program. Therefore, the application of the marine or freshwater aquatic life
criteria are based upon the waterbody type. The site included in this report is inland and not
within a marine waterbody. Therefore, the freshwater aquatic life criteria are appropriate for this
location. Alaska regulations specify water quality criteria for each protected use class (18 AAC
70.020). As codified in 18 AAC 70.050, waters of Alaska are protected for all usage classes
unless the waterbody is specifically excluded. This site is not specifically excluded or
reclassified (18 AAC 70.230). Target constituents of concern for the inactive reserve pit closure
program are shown in the Alaska Department of Environmental Conservation (ADEC) Interim
Site Assessment Guidance For Inactive Drilling Waste Sites (June 1991). The discussion below
pertains only to the parameters measured for the reserve pit closure program. Samples were
collected to provide data on constituents in the following regulatory groups (18 AAC 70.020):
· Toxic and Other Deleterious Organic and Inorganic Substances
· Petroleum Hydrocarbons, Oils and Grease
· pH
· Dissolved Inorganic Substances
Toxic and Other Deleterious Organic and Inorganic Substances
The Toxic and Other Deleterious Organic and Inorganic Substances-Freshwater group does not
specifically state numerical levels for target constituents; rather it incorporates the following by
reference:
· EP A Water Quality Criteria as referenced in 18 AAC 70.020, Note 5
· Alaska Drinking Water Standards (18 AAC 80)
Water quality criteria applicable to this site are presented in Table A.l. The EP A Water Quality
Criteria reference encompasses pre-1985 federal water quality criteria documents. Applicable
EP A Water Quality Criteria are shown in the A WQS column on Table A.l. Detailed footnotes in
Table A.l indicate the source values for the various criteria.
The AWQS under 18 AAC 70.020 (b) and 18 AAC 70.040 dictate how the applicable water
quality standards are determined from the list of criteria. For target constituents under Toxic and
Other Deleterious Organic and Inorganic Substances - Freshwater, the most stringent of the
Alaska Drinking Water Standards (ADWS), the EPA Water Quality Criteria for Water, or
applicable NTR criterion is selected. The most stringent criteria (i.e., the controlling standard)
are shown in the last column.
The National Toxics Rule (NTR) criteria (40 CFR 131) imposed selected criteria to bring Alaska
into compliance with federal water quality requirements. Not all criteria are applicable to
Alaska. In Table A.I outlined values represent NTR criteria which have not been promulgated
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APpendIX A
Water Qualitv Criteria aetennlnadon
for Alaska. Therefore, these values were not considered when identifying the most restrictive
criteria.
Freshwater aquatic life criteria for chromium, lead, nickel, and zinc are hardness dependent. The
1991 field program did not include hardness as a sample parameter. The NTR allows hardness
values of 25 to 400 mgIL for hardness dependent criteria. Lower hardness values result in more
stringent criteria. Therefore, the minimum hardness value of25 mgIL was used for hardness
dependent criteria. Criteria shown in Table A.I are calculated for the minimum hardness values
allowed by the NTR (25 mg/L).
Petroleum Hydrocarbons, Oils and Grease
Total extractable petroleum hydrocarbons (TEPH), total volatile petroleum hydrocarbons
(TVPH) , and benzene, toluene, ethylbenzene, and xylene (BTEX) are specified as parameters in
the Interim Site Assessment Guidance For Inactive Drilling Waste Sites (June 1991). In 18 AAC
70.020 there is no numerical standard for TEPH or TVPH; however, petroleum hydrocarbons,
oils and greases may not cause films, sheens or discoloration on the surface or floor of the
waterbody. Total BTEX may not exceed 10 µg/L and benzene may not exceed 5 µgIL.
pH
pH values characterize the acidity (or alkalinity) of an aqueous solution and numeric standards
are present inI8 AAC 70.020. The most restrictive A WQS values for pH are found under the
"Water Supply -Aquaculture" classification and specify that the pH of a waterbody may not be
less than 6.5 or greater than 8.5. Additionally, the pH may not vary by more than 0.5 pH units
from natural conditions. Variation of pH for waters naturally outside the range must be toward
the range.
Dissolved Inorganic Substances
The numeric criteria in this regulatory group principally address total dissolved solids (TDS)
content and TDS is not a target constituent of the reserve pit closure program. Conductivity
measurements are, however, required. Although conductivity may be viewed as an indirect
measure ofTDS, there are no numerical standards for conductivity in 18 AAC 70.020.
In 18 AAC 70.020 there is a 200 mgIL standard for chlorides. This value is shown in table A.I.
However, the A WQS value for chlorides is being reviewed and the May 4, 1998 public review
draft of the A WQS includes a proposed value of 250 mg/L. This would make the A WQS
chloride value consistent with the State and Federal drinking water regulations.
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Appendix B
Risk Screening MethodologV
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Appendix B
Risk Screening MethodoloUV
Closure plan requirements in 18 AAC 60.440 (f) include submitting a qualitative discussion of
material and probable risks to public health or the environment posed by the inactive reserve pit.
The regulations do not specify a particular risk evaluation procedure, so the risk screening
process in Section ill of ADEC's Interim Site Assessment Guidancefor Inactive Drilling Waste
Sites (June 1991) was used Sections I, II, and V of the guidance have been superseded by 18
AAC 60.440.
Based on discussions with the ADEC, two modifications were made to the risk screening
guidance:
. The requirement to evaluate corrective action if risk is found to be negligible was eliminated.
· An option to perform a risk assessment was added if the risk screening approach indicates
significant risk.
The 1991 guidance outlines a screening process for determining if an inactive reserve pit poses a
risk to human health or the environment. This risk screening process is qualitative, and uses a
decision analysis approach. This is a helpful tool to differentiate drilling waste sites with
negligible risk from those sites that present significant risk. The 1991 guidance approach is
consistent with current state and federal procedures for performing risk assessments.
The risk screening process uses two steps to determine risk. The first step establishes if there is a
basis of concern. If there is none, then risk is determined to be negligible, and site closure is
warranted. If there is a basis of concern, the second step is necessary to determine if that concern
constitutes a significant risk. If the risk is not significant, then site closure is warranted. In
cases, where risk is determined to be significant, a corrective action plan is developed and
implemented.
The following sections discuss each of these steps in greater detail. Figure C 1 presents a
flowchart of the risk evaluation methodology.
B.1 STEP 1 - IS THERE A BASIS OF CONCERN?
The first step in the decision analysis is to detennine if a basis of concern can be established. If
there is no pit or the pit cannot be located, the site is declared eligible for closure without risk
screening. Some wells were drilled without storing the drilling wastes in a reserve pit. If site
records indicate that no reserve pit existed at a site, then there is no basis for concern, and the
inactive reserve pit is closed.
In some cases it is not possible to locate reserve pits. ADEC specifies that if the reserve pit
cannot be located, it will allow closure if the pit cannot be found based on a reasonable search.
The definition of what constitutes a reasonable search is presented in 18 AAC 60.440 (h)(I).
If a reserve pit is present or likely to be present, then the risk screening process is initiated. Since
the regulations only identify compliance points for water (18 AAC 60.440 (e)), water is the
pathway for which it is necessary to determine if there is a basis for concern. There are two
primary criteria that must be met to establish a basis for concern. The criteria are as follows:
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Appendix B
Risk ScreenlnU'Melhodolouv
· Evidence of release of any target constituents in excess of applicable Alaska Water Quality
Standards 18 AAC 70, or mechanisms for potential release, and
· Proximity of the waste site to any biological receptors.
B.1.1 Evidence of Release or Mechanisms for Potential Release
The evidence of release criteria is satisfied if a water sample collected on or within 1,000 feet of
the reserve pit has levels of target constituents above applicable water quality standards relative
to background concentrations. Evidence of release is based upon visual field observations when
no samples are collected.
Mechanisms for the potential release of target constituents include the following:
· A reserve pit dike with unstable sloped, breached, or eroding dikes
· Significant negative disturbance of site thennal processes
· Standing water in a clearly observable depression on the pad or in the reserve pit
· Standing water on the reserve pit cover material
Field observations were used to identify if any of these potential release mechanisms were
present. Additionally, historical infonnation was used to supplement this visual evaluation.
B.1.2 Proximity to Biological Receptors
A site is considered to be in close proximity to biological receptors if there is evidence of
biological receptors at the site. This includes proximity to nearby towns or villages, or habitat
suitable to support wildlife species mown to frequent the area. Certain sites would receive
increased scrutiny during the decision analysis process, including those:
· With state or federal endangered species habitat
· Which supply unique or important food sources
· With certain state and federal land designations
8.1.2.1 Threatened and Endangered Species
The USFWS lists threatened and endangered species under authority of the Endangered Species
Act of1973. The ADF&G lists endangered species and species of concern under authority of the
State Endangered Species Law. Table Cl summarizes these species that potentially may be
found in areas where AAI has inactive reserve pits.
Sites within or near habitat that supports these species will be given additional consideration by
the risk screening process. Habitat which supplies unique or important food sources is identified
and evaluated on a case-by-case basis.
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Appendix B
Risk Screening Melhodolouv
8.1.2.2 State and Federal Land Designations
Critical habitat areas are designated by the state and federal governments. The Alaska State
Legislature has classified game refuges, critical habitat areas, and game sanctuaries essential to
wildlife and fisheries resources. Only the Susitna Flats State Game Refuge on the west side of
Cook Inlet, and the Yakataga State Game Refuge located along the Gulf of Alaska, west of Icy
Bay, contain inactive AAI reserve pit sites.
Federal lands designated for habitat conservation include National Forests and National Wildlife
Refuges (NWR). There are 16 federally designated areas in Alaska. Only two federal areas contain
inactive AAI reserve pit sites: Chugach National Forest and the Kenai National Wildlife Refuge.
Inactive reserve pit sites occurring on state or federal lands designated for conservation are given
additional consideration by the risk screening process.
B.1.3 Establishing a Basis of Concern
If evidence of release is found or there is a mechanism for potential release, and proximity to
biological receptors is established, then there is a basis for concern that the reserve pit could
present a significant risk to human health and the environment. Screening then proceeds to Step
2, to evaluate significance of the risk. Absent a basis for concern, risk is determined to be
negligible, and the site is declared eligible for closure without corrective action or further
investigation.
Note: At this point, the methodology used for these reserve pit closures deviates slightly from the
1991 guidance. The guidance suggests that a corrective action plan be prepared for sites at
which there is no basis of concern, and for which risk has been determined to be negligible. This
revžsed screening approach allows the site to be declared eligible for closure without corrective
action or further investigation based solely on establishing that there is no basis of concern.
8.2 STEP 2 · IS RISK SIGNIFICANT?
Step 2 is the decision point to detennine if conditions at a specific site constitute a significant
risk to human health and/or the environment. Two sets of criteria are used to make this
determination: the likelihood of exposure and the consequence of that exposure. Both exposure
and consequence criteria must be met before a site is determined to pose a significant risk.
8.2.1 Exposure Criteria
Receptor exposure is considered to be likely if any of the following conditions are met:
· Contaminant release mechanisms are significant
· Potential for contaminant migration is significant
· One or more contaminants are environmentally persistent
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Appendix B
Risk Screening MelhodoloDV
B.2.1.1 Contaminant Release Mechanisms
Contaminant release mechanisms are considered significant when a target constituent is detected
in a water sample from the site (at detectable levels using standard analytical measures), and/or if
the site has physical properties that make further release possible. High aqueous solubility and
low soil sorption potential are examples of properties which may increase the probability of
additional releases. Table C2 summarizes chemical, physical, fate, and persistence infonnation
for target constituents.
Site specific conditions may increase the potential for releases. Mechanical disturbances of muds
and cuttings by wind or wave action, thennokarst activity, or animal disturbance are examples of
site-specific considerations.
B.2.1.2 Potential for Contaminant Migr2tiQQ~
To directly estimate contaminant migration potential, sample data for locations downgradient of
the reserve pit must be available. Migration potential may be indirectly estimated by evaluating
the likelihood that a mechanism exists to move contaminated waters away from the contaminant
source. Migration mechanisms may include: wind action, freeze/thaw cycles, topography, lack
of penna frost barriers, and general area hydrology.
8.2.1.3 Environmental Persistence
Environmental persistence is indicated by the current levels of the contamination relative to the
age of the pit or natural persistence in the environment. The target parameter's half-life in
surface water (Table C2) can be used to indicate its resistance to biological degradation, chemical
fixation, mineralization, and photolysis.
8.2.2 Consequence Criteria
If none of the exposure criteria are met, then a finding of negligible risk is made. The site is
declared eligible for closure without corrective action or further investigation. If any exposure
criterion is met, then the risk screening process proceeds to evaluate consequence criteria.
Adverse consequences of exposure to target constituents are considered likely if:
. Duration or frequency of exposure is sufficient to cause adverse health or environmental
effects, and either
. Quantity or concentration of contaminant( s) exceeds applicable federal, state, or other
protective water quality standards, or contaminant(s) exhibits high acute toxicity.
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Appendix B
Risk Screening MelhodoloUV
8.2.2.1 Duration or Frequency of Exposure
The likelihood that exposure duration and frequency would be sufficient to cause adverse human
health or environmental effects are evaluated by reviewing human and wildlife use patterns at an
inactive reserve pit site. Human use patterns means detennining the population(s) most likely to
use the site (e.g., nearby residents, children, campers/hunters, site workers) and the activity
perfonned at the site (e.g., recreation, food-gathering, year-round living). Significance of
wildlife exposure is evaluated based on the species most likely to use the site, and the activity for
which the site may be used (e.g., migratory stop, nesting, brood-rearing).
Site accessibility, such as proximity to airstrips or roads, is an important factor for evaluating
human exposure. Surrounding land use and migration patterns would influence the likelihood
and significance of wildlife exposure. Other accessibility factors affecting both human and
wildlife exposures include the availability of other water resources in the area, snow cover, and
the uniqueness of the water or food sources.
Groundwater and surface water use influences the significance of exposure. The way the water
resource is or could be used (e.g., drinking water supply, contact recreation, subsistence food
habitat) directly affects the potential duration and frequency of exposure to a contaminant.
Professional judgment must be used to detennine if there is sufficient duration or frequency of
exposure to cause adverse health or environmental effects.
8.2.2.2 Quantity or Concentration of Contaminant(s) Exceed Applicable Water Quality
Standards
Measured contaminant concentrations are compared with applicable health and environmental
standards and criteria to detennine if the quantity or concentration risk criterion is met. When
only human populations are at risk, health criteria are used. Other environmental criteria are
used when comparing to non-human populations. Both human and environmental criteria are
used if both human and non-human populations are potential receptors.
8.2.2.3 Acutely Toxic Contaminants
The National Institute for Occupational Safety and Health (NIOSH) toxicity rating system is
used to identify chemicals highly toxic to mammals. This infonnation is used to detennine
whether a target constituent exhibits acute high toxicity. Chemicals with high acute toxicity are
those which can threaten life or cause pennanent physical impairment from a low number of
exposures. Toxicity is categorized as unknown, not toxic, slight, moderate, or severe. Highly
toxic substances are defined as those with:
· An oral lethal concentration fifty (LCso) equal to or less than 50 mg/kg
· A dennallethal dose fifty (LD so) equal to or less than 100 mglkg
· A inhalation LCso equal to or less than 43 mg/kg
A similar national rating system is not available for aquatic organisms. Based on the 1991
guidance, an aquatic toxicity LCso value of 1 mglL is used as a criterion for identifying chemicals
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Appendix B
Risk Screening Methodolouv
highly toxic to aquatic life. Additionally, toxicity testing data for species of concern may be
used when it is available. Toxicity data for target constituents is presented in Table C3.
8.2.3 Significant Risk Evaluation
If either the exposure or consequence criteria in Step 2 are not met, then a finding of negligible
risk is made, and the site is declared eligible for closure without corrective action or further
investigation. If both the exposure and consequence criteria in Step 2 are met, either a risk
assessment is performed, or a corrective action plan is developed.
Note: The option of doing a risk assessment is not included in the 1991 guidance document.
However, this option was added in the event that a more detailed assessment of the risk at a site
is warranted based on data obtained during the qualitative risk assessment. A risk assessment
would follow current state and federal protocols for risk assessments.
8.3 REFERENCES
Alaska Department of Environmental Conservation (ADEC). June 1991. Interim Site Assessment
Guidance for Inactive Drilling Waste Sites.
Alaska Department of Environmental Conservation (ADEC). 1996. Petroleum Cleanup
Guidance. Background on Development of Regulations for Soil and Groundwater
Cleanup Levels at Sites Contaminated with Petroleum Products. Public Review Draft.
December.
Alaska Departmént of Environmental Conservation (ADEC). Janmuy 28, 1996. Solid Waste
Management Regulations (18 AAC 60).
Alaska Department of Fish and Game (ADF&G). May 25, 1993. State of Alaska Species of
Special Concern List.
Alaska Department of Fish and Game (ADF &G), Habitat Division. 1996. State of Alaska
Refuges, Critical Habitat Areas, and Sanctuaries
American Society for Testing and Materials (ASTM). 1995. Standard Guide for Risk-Based COlTective
Action Applied to Petroleum Release Sites.
Budavari, S. (ed.). 1989. The Merck Index, 11th edition. Merck & Co.
Peny and Chilton (ed.). 1973. Chemical Engineers Handbook, 5th Edition. McGraw-Hill, Inc.
Sax, N. lIving. 1984. Dangerous Properties of Industrial Materials, Sixth Edition.
United States Environmental Protection Agency (EP A). 1986. Superfund Public Health Evaluation
Manual. EP A/540/1-86/060.
United States Environmental Protection Agency (EP A). 1988. Review of Ecological Risk
Assessment Methods. EP A/230-10-88-041.
Woodward-C1yde (ì
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Appendix B
Risk Screeninu Methodologv
United States EnvironmentalProtection Agency (EPA). 1989. Risk Assessment Guidance for
Superfund: Volume I - Human Health Evaluation Manual, Part A. Interim Final. Office
of Emergency and Remedial Response, Washington, DC December.
United States Environmental Protection Agency (EP A). 1989. Risk Assessment Guidance for
Superfund. V olume II (RAGS II): Environmental Evaluation Manual (RAGS II). Interim
Final. Office of Emergency and Remedial Response. EPA/540/1-89/001.
United States Environmental Protection Agency (EP A). 1992. Framework for Ecological Risk
Assessment. Risk Assessment Forum. EPA/630/R-92/001.
United States Forest Service (USFS). 1994. Alaska Region Sensitive Species List.
United States Fish and Wildlife Service (USFWS). 1998. Endangered, Threatened and
Candidate Species in Alaska. Unpublished report. Office of Ecological Services.
Woodward.clyde (ì
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Appendix B
Risk Screening Melhodolouv
TABLE Bl
STATE AND FEDERAL
THREATENED AND ENDANGERED SPECIES LISTINGS
Species Common Name Regional Occurrence Status/Agency
BIRDS
Diomedea albatrus short-tailed albatross Gulf of Alaska & Bering Endangered - ADF&G
Sea
Numenius borealis Eskimo curlew No longer occurs in Alaska Endangered - ADF&G,
USFWS
Accipiter gentilis laingi northern goshawk Southcentral Species of Concern -
ADF&G
Histrionicus histrionicus harlequin duck South central (coastal Species of Concern -
waters) ADF&G
Sranta canadensis dusky Canada goose Prince William Sound Sensitive - USFS
occidentalis
Cygnus buccinator trumpeter swan Southcentral Sensitive - USFS
Pandion haliaetus osprey South central (coastal Sensitive - USFS
waters)
Fa/co peregrinus anatum American peregrine North Slope & Endangered - USFWS
falcon Southcentral
Fa/co peregrinus pealei Peale's peregrine falcon South central Sensitive - USFWS
Fa/co peregrinus tundrius Arctic peregrine falcon North Slope Species of Concern -
ADF&G
Somateria fisheri spectacled eider North Slope Threatened - USFWS
Polysticta steJ/eri Steller's eider North Slope Threatened - USFWS
Contopus borealis olive-sided flycatcher Southcentral Species of Concern -
ADF&G
Catharus minimus gray-cheeked thrush North Slope & Species of Concern -
Southcentral ADF&G
Dendroica townsendi Townsend's warbler Southcentral Species of Concern -
ADF&G
Dendroica striata blackpoll warbler Southcentral Species of Concern -
ADF&G
MAMMALS
Felis lynx canadensis lynx South central Species of Concern -
ADF&G
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Appendix B
Risk Screening Methodolouv
TABLE B2
CHEMICAL, PHYSICAL, FATE, AND PERSISTENCE DATA FOR TARGET
CHEMICALS
INACTIVE RESERVE PIT ASSESSMENTS
Parameter Solubility in Water(1) Vapor Pressure(2) Half-Life in
at 20-25°C, neutral pH Surface Water(3)
Oraanics:
Benzene 0.188g/100g 100 mm Hg at 26.1°C 5 - 16 days
Ethylbenzene practically insoluble 10 mm Hg at 25.9°C 3 - 10 days
Toluene 0.067 g/100g 37 mm Hg at 30°C 4 - 22 days
Xylenes practically insoluble 6.7 mm Hg at 21°C 1 - 4 weeks
Inoraanic:
Arsenic insoluble 1 mm Hg at 372°C NI
Barium varies, depending on form 10 mm Hg at 1049°C NI
Calcium varies, depending on form 10 mm Hg at 983°C NI
Chromium varies, depending on form NI NI
Lead varies, depending on form 1 mm Hg at 973°C NI
Magnesium varies, depending on form 1 mm Hg at 621°C NI
Nickel insoluble 1 mm Hg at 1810°C NI
Sodium varies, depending on form 1.2 mm Hg at 400°C NI
Zinc insoluble 1 mm Hg at 487°C NI
Notes:
NI indicates that no information was available
(1) Data from Merck Index, 1989
(2) Data from Sax's Dangerous Properties of Industrial Chemicals, 1992
(3) Data from Handbook of Environmental Degradation Rates, 1991
Woodward-C1yde Cì
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Appendix B
Risk Screening Methodolouv
TABLE B3
TOXICITY OF TARGET CONSTITUENTS
INACTIVE RESERVE PIT ASSESSMENTS
Parameter Oral Toxicity Dermal Toxicity Inhalation Toxicity
m Ik m Ik
Organics:
Benzene Moderate (rat) LOso 3,306 Moderate (mou) TOLo 1,200,000 Toxic (rat) TCLo
1,200 ppm/6H
Ethylbenzene Moderate (rat) LOso 3,500 Mild (rab) LOso 17,800 Mild (rat) LCLo
4,000 ppm/4H
Toluene Moderate (rat) LOso 5,000 Mild (rab) LOso 12,124 Mild (rat) LCLo
4,000 ppm/4H
Xylenes Mild (rat) LOso4,300 NI NI Mild (rat) LCso
5,000 ppm/4H
Inorganic:
Arsenic Toxic (rat) LOso 763 NI NI NI NI
Barium Toxic (rat) LOso 118 NI NI NI NI
(as barium chloride)
Calcium Moderate (rat) LOso 6450 NI NI NI NI
(as calcium carbonate)
Chromium (as Toxic (rat) LOso 1,870 Toxic (gui) LOLo 202 Toxic (mou) LCso
chromium chloride) 31,500 µg/m2/2H
Lead Moderate (mou) TOLo 4,800 NI NI NI NI
Magnesium Toxic (dog) LOLo 230 NI NI NI NI
Nickel Toxic (rat) TOLo 158 NI NI NI NI
Sodium Moderate (rat) LOso 3,000 NI NI NI NI
(as sodium chloride)
Zinc Toxic (rat) LOso350 NI NI NI (rat) LCLo
(as zinc chloride) 1960 mg/m3/10M
Notes:
NI - no information available
H - hour
M - minute
(gui) - guinea pig
(mou) - mouse
(rab) - rabbit
LCso - lethal concentration fifty
LDso - lethal dose fifty
TDLo - toxic dose low
LCLo - lethal concentration low
Source: Data from Sax's Dangerous Properties of Industrial Materials, 1992
Woodward-C1yde fì
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-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
..
NO
Risk is
Negligible
YES
NO
YES
NO
CLOSE
INACTIVE
RESERVE
PIT
YES
YES
NO
Develop Corrective
Action Plan
Implement
Corrective Action
)
EVALUATION CRITERIA
"Steo 1. Basis of Concern Criteria:
.... Steo 2. Sianificance of Risk - Exoosure Criteria:
.... Steo 2. Sianificance of Risk - Conseauence Criteria:
· Evidence of release of chemical contamination in
excess of Alaska Water Quality Standards, OR
mechanism for potential release,AND
· Proximity of site to receptors
· Contaminant release mechanisms are significant,OR
contaminant migration potential is significant. OR chemical is
environmentally persistent
· Duration of frequency of exposure AND EITHER,
· Quantity or concentration of one or more contaminants exceeds
federal or state water quality standards or other protective
standards, OR chemical exhibits high acute toxicity
FIGURE
IIIIS t:rølner Wøødwanl Clyde
RISK EVALUATION METHODOLOGY
B-1
Q:\FILES\PROJECTS\WCC\98COO3NA\MOBIL\OCT98\RISKFLOWB-1. VSD
APpendix e
Field Notes
-...
~,
·~í
SltalWell Name:
wee Site ID: l/'-i~ ~)o=?Z-3S~ 0
API Well Number: _ _ _ .
F'.d Information
Pg. _ of
., ,'"\, 'J
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.j,-, ~ ,-T (\/1 ~., :~ "r.\·~'\,¡< It'
f-/
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I Dat-3: ~(~/?~ì/ ~0'
.,~flCC Project No.: 91 C0650A
~'::,~lient Name: Mobil Oil EXDloration and Producina
I Time of Arrival at Site: }/~ I~
Date Samples Submitted: ~/VI(;I.jt
I Generallnfonnation
I
#1
Leave Site:
Lab Name:
~ :~ - I 0 jJ ~~
I
WCC Field Crew: Diana Evans, Chris Holden
Other Field Crew: i/ ¡.: If k: ~..II,;{,I s- 7t.·I_'
Weather Conditions: ./J. . /~ d!, . - -A'-~
I ) Mode of Transport I From:
location Inlonnation
A",· f!",r~1f-'Pilotl Company.:
r /_> ,c.
. '- ../,~ ~'; ,7'~_T
I Quadrangle Name:
Section:
Latitude:
I Other Map and Location Info:
I
Region:
Township/RangA'
Longitude:
Photo Log
I ., I
"I·~-rilm Roll No. ~ for Frame No. ~ througÞ
\ __ :ilm Roll No. _ for Frame No. _ through..--
Film Roll No. _ for Frame No. _ through..--
Film Speed and Roll Size: ::J:.)D ^D~
I Aerial Video of Site: "0
I
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1IM1 FlDINFOÆV A.X1. tIIIl:i/J¡;jj
~==:eC;þ~iq~
'~_~;NCC Project No.: - 91 C0650A
I Client Name: MabIJø Oil !;xploratÎQD
I SITE OBSERVATIONS
Pit
.1) An obvious Pit on the site? (If NO goto next page)
No':g)Ves 0 Describe:
I
I
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·
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I
·
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I
I
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Field Information
Pg. _ of
~:,,::,e: ~t!q~41A,f!/g--#/
API W.. Number:
( H applicable, note Items on site map)
1 a) Condition of Pit dike . Intact?
No OVes 0 Describe:
P~t / PCA.J.. b", lId Dz.ed o.Jif,
!J o.¡¿ v' I~ cJ prl-- welt
~~ ~^ c,,,,,,,r þç..ç.. ~ ..
l o",q~h> "'" (; '" f"'~ ; j
Il , IL j ~ 4Io-~:Y fZe-' t ¡(.v ~
aflu.~J,.. .
Breached?
No OVes 0
Describe:
Eroded?
No OVes 0
Describe:
1b) .ð!J!L. evidence of wind or water erosion of pit dike?
No IL::jVes 0 Describe:
1c) Does sl~ of dike appear stable?
No OVes 0 Describe:
1d) Does the tl ¡nlain any substance? (liquid,solid,sludge,coIor, uniformity)
No OVes Describe:
1 e) Evidence of backfilled pit?
No OVes EZJ Describe: ~~
&""
c..~
p: + ^O+
~ Q.pfr e., j ~ ,~
1f) jY rœnce of erosion of pit contents?
No Ves 0 Describe:
19) Þ!tt evidence of subsidence of dikes or pit contents?
No~Yes 0 Describe:
1h) Standing or RJnning water in pit?
No ~ves 0 Depth: Descrme:
1 i) Surface water in contact with edge of pit dikes?
No ~y~ 0 Describe:
1j) Evidence of seepage from pit?
No.~Yes 0 Describe: t\0 f'(((...:I"-~
V-E..).t. -k -h ~
1k) Evidence of overflow of pit to surrounding area?
~yes 0 Describe:
11) Is the surface of the pit contents cracked? Water in crack?
No Dyes D Describe:
No DYes D Describe:
Co.-) A-4uL. c:> IL
:s~-'~
1 m) Pit conte. ~Iling away from the edges of the pit?
No OYes L-J Describe:
~ AI"~(l...
Gf";'J:^" l
"'" .. + c.- 0-
I"~
'"" ; j I· ~tJL
'OJ
I~:F~REV~XL
. Wooclwa~.ctyd. Consultants fit
~"'atéandTlme: ?/~7/91
. '".;lCC Project No.: 91 c'0650Á
.1 ClIent Name: MobH Oil Exoloration
;~
~
SlteIWeU Name:
wee SIte 10:
API WeU Number:
Field Information
--Pg._ðf
kI MOCŸl/Ilv..IKI e-iÞ/
It s'- ., D l'
SITE OBSERVATIONS ( If applicable, note Items on alte map)
11n) ~. ~ in Pj area that may hold standing ~me instances? .
No Yes Depth: Describe: G ~ 0 ""' " Á , ~
I ,,~~aJ... 0"", ptA~.
10) Evidence of animal intrusion of pit (tracks ,burrows ,etc.)?
No ~Yes D Describe:
1 :ï' Any standing or running water on pad?
I No ~YesD Depth: Describe: .fPt-Á.. 6{"Y
3) ~roIeui hvd,rocarbon sheens or odor on the pad Ot pit when soil Of water is disturbed ?
I No LC:JYes Describe:
~:rt'J
1e,J~( ~. ~~
I
.. 4) Sta~~ areas or obvious burial sites?
No YesD Describe:
-'9 j ~iion of a refueling area on pad? (i.e. diked area on pad, fuel stand)
1 ;;0 YesD Describe:
I 6) ~ i~ment areas on the pad other than the pit?
No Yes L-.J Describe:
17) ~nsite?
No YesD
Describe:
t'v. I^ l 1- I b'" v\.e..& ~ ha I bw lId CJ Z~J
~;;n > ,(j¿~" r
I
7a) Can debris be burned or buried on site?
No Dyes D Describe:
IS) Evidence of ¡nv jntainers on-site (i.e. dru'!JS,pallels, bags)?
'. No ~Yes Describe: ç' , ~ <...~~
~"" .s:~.
~ .....
1'\0
4ÎØI\.s(., 0,- óc-" (
I
I
9) ~ence of buried trash?
No ~YesD Describe:
I 98) Is Waste visible?
" No DYes 0
I
I
88) Estimated amount of waste and condition of containers:
Descrbe:
Describe:
9b) ~evidence that trash had been burned prior to disposal?
No L-IYes D Describe:
. ,~
t~,~REVUl Q
,W, ooctiNanl.cJyde Consultants Y( /) ~
I'~e and TIme: ~ l Ci (
, " ',/ce Project No.: 91 C0650A t
I Client Name: Mob' DiI F~ion
"W. "oca",,"'_ -.,
GE~ERALOBSERVATlONOFAREA (Includ.ln_etchH~llcable) .~" Sl'C. Y',w,~ 11'.....,$1-\
I' 10) ~~ication of 9PØf'8ting company? (signs , stickers, ete) " P, Px." So 7... ~ ~þ D 3S ' I
No ~Yes D Descrbe: /I L L
I U~~1n
. 11) Identifying marks on well head? t, _ n
No Dyes œJ Describe: Ma..'fN::'O(
1~~f¡~edorunusuaUy~shv-c:~na~a? ~~c~ f~tlr:;;^;~~ :1~ :~/j
I D (Iâ. .._:\11>.....',... 0'\-1.. <:( \:L . ·-c 1. j5
1f.(~~eJ 3r~ +('~ I> ()
, '13) Evidence of natural events (e.g. fIõod~, mud flows, freezelthaw heaving)
...-..,
Field Information
Pg. _ Of
SltelWell Nllme: t,U. ~
wee SIte ID· J ~-
APt We. Nu~ber: - - - - ~
1 Water
- 14) r jrface water in area? (Streams. creeks etc.), < r-.............. 6........ .: I ( +z,
No Yes ~ Distance from pit: 3~_o Describe: ,.... ¿QI' ."
I 14a) D~nJ~~~(wak~~? '5 'I~ ." ,,.,.~ 5f1.c...~ of fJt"J.
CaA. ,GI\ ~. \\ ffO~ðl~ v I. \.." I ( 6~ 1 ,.11;,
5ð"'~~ ó.\~"'..1 ..,tOW ~ ·
1__ ~,~I Any petroleum ydrocarbon sheen or odor produced when water/soil disturbed?
No Yes D Distance from pit: Describe:
115) I Any rkes. P.Qnds or swamps in area? t/ ...; I c..
No Yes ~ Distance from site: z... Describe: ~ ~'(
I 5..", ~I,. ..~ s :~
Wildlife
16) ð!:!l...,fIowing water within 1/4 or within 1 mile of site that may be habitat for fish?
I No L..jYes ~ Distance from site: ,...' DescriIe: ..H·/"<·...'""'
,... 17) j" ¡idence of wildlife in area? Where?
: No Yes ~ Distance from site: Describe: ·
Tll\.l J t " ~ -h"", Òo\.C C){." c>r& 1'1'" "" ,-5
I Humans
. 18) ~ ¡idence of human habitationl use within 1/4 or within 1 mile of site?
No Yes D Distance from site: Describe:
119) Is site easily accessible to humans? (Road to site. nearby village or hunting area) ì ('" v¿( \ ~ w ~W
I. No ~Yes CJ Dista~ from site: Describe: ,.J - Ù. ~(){rÁlI wea oo~~ I ~
0: I"~ ~ ..'.a.6.S . I..... ¡.I/JI..A.. C . "" l.l ~ v\. 1 'u \1' T
it) of! TV .s
. ",'0) ~ ,e of ItImlins at site? (Beer cans. vehicle stracks. camp fires .etc.) · . 1\
I No . Yes D Describe: v<..1L-¡ l·"'TT"" It. ~;.s
(4,~ &tl ( .
I 't,. kA... .f-o
+"'-
~
oSC->
I
~
t · -; ·
I' 7;=rd~e Consun,nts lft
. ~'?ate and TIme: ~ .,. 1- ~ (
-NCe Project No.: Q1 C06SOA
I Client Name: Md>iI Oil E''CpIoralion
,~"
SlteJWell Name:
wee SIte 10:
API w.n Number:
r
I
t' loD
- ----~(
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cf ð''' ~~~
1 ,\11 ),/'
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..-...
Field Information
Pg. _ ftf
4/1.Jf ~ Q Q.II\~~/t.'e. :# I
213 -z.... 3':"0 ~
þt~(. _or Il-
II Well Head Location
sz: Water Sample Location
)I( SoiL'S1udge Sample Location
. Background Soil Sample
2 Background Water Sample
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It.
,
?Q
~
--\
. \ 't.~
~
------......
o
o
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\~
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~
SITE MAP OF AREA Legend:
I Sample ID: (Clienl)(WCC Sile IDH)-WA-(Sample 110.##)
I Sample 10: (Client)(WCC Site IDH)-SO-(Sample no.l#)
. Example:CIB01-WA-01
wee Site ID: PB- Prudhoe Bay
lAP-Alaska Peninsula
. SC.Kenai PeninsulalSouth Central
BR.Brooks Range
liB-ICY Bay
(
,
/1
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.
t ~, ;~REVAXL ~
~==e Consultants .,
, wee Project No.: 91 C0650A
Client Name:, Mobil Oill;~ploration
~
SlteJWell Name:
wee Site ID:
API Well Number:
Field Information
Pg. _ ~f
tµ. 11 () alA. ~ k I <..
~ ~ c.. - ¿) -:t-
rl
I
I SAMPLE COLLECTION
20) General description of area and its condition:
I
I
I Water and Soil Samples Collected
Site Map No. Sample Number
1
I
I 2
I-
I 3
1\
I 4
I
I 5
I 6
I
I
I
Chain of Custody Number:
('
)
No
5>1 jY) ft6
Feeld Tests
PH-
T emp=
Conduct-
Description
PH-
Temp-
Conduct-
PH-
Temp.
Conduct-
PH-
Temp.
Conduct-
PH.
Temp.
Conduct-
7
PH-
Temp-
Conduct.
PH- .
T empa
Conduct-
Mobil Business Resources Corporation
P O. BOX 650232
DALLAS TEXAS 75265·0232
January 15, 1997
17o-0S-3
A laska Department of Environmental Conservation
Division of Environmental Health/Solid Waste Section
555 Cordova Street
Anchorage, Alaska 99501
Reserve Pit Closure Submittal for:
Deli Unit 1
API No: 1792000200
Completion Date: 6/24/73
Plugged and Abandoned: 6/24/73
Latitude: 69.71077 Longitude: 146.53550
Legal Description: 8 04N 023E
Surface Land Ownership: State of Alaska
With this submittal, Mobil Oil requests closure of the subject reserve pit in accordance with the Solid Waste
regulations, 18 AAC 60.440 subsection (b)(l) through (b)(4). In accordance with the regulatory requirements, the
following documentation is attached:
field checklists, photographs, and water sample lab results (for sites with water on the pit)
which document that water does not accummulate in direct contact with drilling waste
an explanation of why further action at the pit is not necessary to protect human health
and the environment
site location map from USGS topographic map Mt. Michelson C-5
recent site photos including aerial dated 12-Aug-91; approximate scale: 1" = ] 1 0'
letter(s) from USGS & DNR which documents pre-September 20, 1987 closure
The Woodward-Clyde site visit was made on August 12, 1991 by Mr. Chris Holden and Ms. Jane Thomas.
A check in the amount of$1000.00 to cover filing fees in accordance with 18ACC 60.440(a)(2)(b) will be
forwarded to your office under separate cover. Please contact me at the letterhead address or at (214)951-4190
should you have any questions or require additional information to support this request,
Thank you for your time.
Sincerely,
9- (y. tdJj¿c-II(~
A.J. Ro~,P.G,
Attachments
cc: Mr. Leon Lynch 1 Mr. Gary Schultz, ADNR
Mr. Jack Winters, ADF&G
RECEIVED
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SUMMARY OF SITE DOCUMENTATION
1Ó- 05:3
B'eli Unit i
API # 501792000200
A DNR memorandum dated 9/17/74 documents a September 3, ] 974 visit to the Beli Unit 1
site. It stated that previously unsatisfactory items had been corrected and the location was
approved for final abandonment as of September 3, 1974. At this time, the well marker \vas
in place, the pit was filled, and the site was clean and fairly level. It also described some
standing water and tracks in the filled pit area due to heavy rain during recent work at the
location. A subsequent letter from USGS to Mobil Oil Corporation dated 10/16/75 agrees
with the approval of final abandonment at this location, but informs that the land on which
the well is located has been transferred to the State of Alaska and the final abandonment
approval would have to be made from the appropriate State agencies. Another letter from
DNR dated October 23, 1975 confirms the satisfactory condition of the Beli Unit 1 location.
Field notes from an August 12, 1991 investigation by Woodward-Clyde located the reserve
pit on the southern portion of the pad. It was covered with gravel which had some
depressions that contained water. There was no evidence of seepage or overflow to the
surrounding areas and the pit dike appeared to be intact and stable. There \vas no petroleum
hydrocarbon odor, stains, or sheen evident anywhere on site, either on soils or \vater.
Chemical analysis of the water from each of the two ponds in the reserve pit sho\ved al]
constituents tested to be within Alaska Water Quality Standards except for Aluminum, \vhich
exceeded the standards slightly. The eastern pond exceeded the drinking standards for
aluminum by 0.2 mg/L and the limits were exceeded in the western pond by 0.4 mg/L. The
aerial photo shows the site to be clean and partially re-vegetated. Another site photo indicates
vegetation on the reserve pit to be similar to the natural vegetation surrounding this location.
The topographic map shows Beli Unit 1 to be located far from any areas of human activity or
means of access. It also shows that the site is not located in an area that is likely to be eroded
by rivers or tides, because of distance from water bodies.. The 1991 field notes indicate that
there was no evidence of human activity or habitation which could be affected by the site,
such as dwellings or water wells.
Conclusion: This reserve pit should receive Agency closure without further action since the
reserve pit has been filled in, no mechanism for any waste to be exposed to the environment,
and the site is in an area that is not susceptible to future disturbance of covered waste. The
site has made no impact to the surrounding vegetation or the human environment. Aluminum
was the only analyte (from the sampling required with the 1991 ADEC reserve pit closure
guidance) which slightly exceeded A WQS. This detection may indicate some contact of
water with waste, but it is not conclusive since other common drilling waste constituents
were not detected. Because the aluminum is only slightly higher than the stand~, ~tŒsE I V E D
unlikely the A WQS would be exceeded at the point of compliance. This location has begun
to re-vegetate naturally and any further activity at this site may disturb natural resto)£tror[~ J 7{i00
processes.
S '\PROJECTS\WCC\9660 12NA \CLA IT ACH. DOC 0 I-I 0-97
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Scale: 1 inch = 1 mile
Beli Unit 1
USGS Map: Mt. Michelson C-5
1955 (Minor Revisions] 973)
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...... VM Al1_ ucI I .... .n bI bts ~trac.tor. 1Ir. ....,.., Ck,~. who was tn
charg. of the Iecbte1 COftStructtOll crw tMt pel ~.H the clean-up wort for
PiKid. Mr. Clark drove us to the Iìa.r Ahw1S Heliport where we contracted
for a helicopter to carry u to the locaticm. We then wen~ on to the ftabor's
cup "'re .. had 1.-cb. Following lunch .. returned to 6Q A1rwys and de-
parted in a Jet Ranger at 1:38 p....
Placid's ~ Point SuPPly SbJtng Area - We new ~ -ectly to the Beeche,y
Point Stag ng area on the ocean. ust north of the Beechey Point .11. cirr.led
GAœ to take pictures and landed to 1ns~ the location on the ground. '1
took Photo '1. froa tfte air. aDd Photo 12 (111 photos attached) from the ground.
Both photos show the nut stacks of pipe,. supplies ani folded pf1low tanks; elNn
~th gnyel pad and berMCI gravel fuel revetllent. The location ts stfl1 ctean
and in a very neat candltton. ..
1M six full tuts of diesel f., tMt hid origtnally bMft stoct piled at the
staging I.... had been .-pt1ed and transferred to .notner operator and the pillow
tanl:a I'"eIJGftd ~ th.. f.l pit. rolled up and stacked on top ~ the cas1ng that
is stiil stock piled on the location. As a .tter of interest. tir. Van Al1en'1n-
fo~ __ n. bad calcullted that. .tn1.um of 13.000 gallons of diesel fuel hid
been stol. f.-. the pt110w taDk stongi' this past year. .,
Af:'r wa'ktng the peri_Þr of the pad. tt appeantcl that t. location WlS sttll
just AS cleo as tt hacI been .1ut yør when I had flo.n OYer (9/19/73) and the
prerlous year when t had tnspected tM location on the gTOunci (9/13/72). W.
went back to t.61e hel :coptar and after circling the 1ocatton again. f1ew one
. 1II11e south to tM Beechey Point .11.
P1ac1d's Placid et a1 Pll~ Beechey Point No. 1. Sect~~ 113M, Rl1E,·U.M.
(PIA. Januar J 12. 1!J71'.. is well was pl ugged and ~bi! on soon _fur being
dril1¡a-1n 1971. ~~t ~. rig ~s stacked on the location until this past .1ntlr,
'~'i\¥.~:.'~;'" ," ; "1<,.c,SJ~te .1 Alaska"
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~'(;.., ~~ .... Ii ~ .'. ''',,~.-.¡ ~':. .... .:.. MIi:. ~ U '~"1974 ·
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':'~". 0': M. Itar 5-.r;.. 'ð:"I..-. .' .~.......,!-,~.-:r. .,' '_. ....., : 0 ~ . ".. . ~- . j
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.- L~te C. W..~- .. ~ . _ ~ Ft.1d Trip .,.t - ,,'-.
........ bøtMI.. ~ JRSPKtt- - 1M IortII 51.-
4' 1'1 - hC :<. for P1ec1... Stagl....Arø ..~.
I '0 L.r \...-' ::A..J P1ad. et a1 P1,-, . IJCbey 'Did II ¡ . '\
I . ~'s PDtIlt S~ 11; "'11's .:.
, "11. IItt_l1. llest ltad1......t1t.. '1 ~
Ind ~~ laY S~ta I!.
~t ~..:r4 A J _t Plldd 1iIo1ogtst. 1Ir. Itl1 Van A1l_ a~
at _ botII boardH . 7:30 .... flight for DHcIhorse.
arrtwt.. aftar sa. .1QS at 10:G.... ..tl. _ .... _t"'''I .. our 1uggage
at . airport I .... cœtactH by ....tl·s canstruct10n npresentatt.. 1Ir. .1f.
T..,lor. ... tate.... _ lie .....-ttar. .-111 I'Hq for . ,...1 cl-..p tnspection
Md ..1c11tb for _ to·Y1s1.t u.. .tther that ."'111 after I ws through
wib the Pladd wrt or tile Mat ., 1f J COtI1d stay ower. J assured hi. that
I COlI'" rta.t ower .. ...14 ..te arranøe-ats ·1eter that: afternoon to ristt hts
locaU-S. . . -.
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We approached the location f~ the West and I took an 31!r1a1 photo. Photo '7,
which shows the 1ocltic" on ~h1ch can be !een the PIA marker and the filled
pi t area. We landed ana I walked the locatton and took MIoto '-'_. whtch shows
On the return flight I requested that we stop by an Exxon location that was on
our way so that I cou1d ..lea a brief inspection., Mr. Vln Allen '''eldtly agr!ed
to this and we hid preY10usly discussed whether or not we wu1d split the cost
but since it was such I minor a.MIftt of tt_ involved. and not out of the way.
he salo that there NOUld be no cost to the state for Vlts stop and that Plåcid
wou1d take care of the ~leta chopper ticket. I filled out . Field Inspec-
tion Report fol'll (attached) for the 8eeche1 Point Staging area indicating a
sattsfactory condttion and showing all fuel had been I"eIIOved and the p1110v
tanks stacked. I .1so filled out. similar report ~O... (attached) for the
P1K1d-P1agtll 3eechI.y Point fto. 1 well indicating the &.ØISItisfacto", work and
the corrective _asures requtred.
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'.__ ~. . ..,..11 ::.--:~;.~~~:~:~.,~:>~. ~~~ "., .~~. ' ,.." '..SqtIIINr 7. 1974
. . '~""-~..~.~' ':'-~.'.:~-:~.~~~:.~..~~~':.'.:.:.:./ . .... .
&lid ... "'\ tt 1M .....~,.. ... ~ 10atiGl ~1"" .;. - WIn suppoHCl11
att.. a ft..-1 1~'" the 1ocat1_. We c1rc1ed U. 1ocatt- IIMI I took
....~ lIIIicll ,~ &tie -.jor\toJ ., tile pMI wtth tile pit ..... t. the tackgrouDd.
It c1ør11 tM .-ost. t':at lIaS ~... be~ Þø ..,1 lata across
tM fll'. pit ...... ., the tine ...,.,... .....~ oa tM pad .1so show up to
~ 11.f~- . ~
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MIl ,.... MIl I .. mP M. .tell .... tile .IA ....... tile ..ti11... ca11....
ce"ma 'II" _tell I up __ the .....1 1øe1 .... a110 sewn1 raws of .
,t1. _'IcIa ..... Mt art off .., .øa all .... .... $0 ."." ron.... WIth
...1. tMt .....1 ~~.. ~1 ~ ~.. u.. All'··
PlIo_ 1," _u.r yt_.f tile PIA....ur KI'OSS . ..n ........ - of tile
pH. to II ts . c1osa-ap of tile ..... cut MtlJII- U. - ..11 lakes
MIl -'lOSS _ ptt 1111 ana. I t.~_d 1Ir. Yu .,1. tAt add1t1..., .rt
-.14 be racpltnd. ... cttsaassed tbe .n that htd to .. ,.rfo"" - the
1ocati- vttb tbe c.tnctor. Mr. aart. Aft ungraded .... of dirt an the eASt
edge of * pM __ 1..,1111. _ ..... on tbe ...u.est comer of the peel
Deeds gndtlll aDd safl'tcteøt gn_1 .111 haw to be pu11" ",. .. al'HS of
the pM tit nfl11 tile erost. ~1 tMt has occurnd'be-- the be lates
KrOSS tile ptt ft11...... I .1so astecl that additional graft1 be p1aœc1 ower
Ute pi 1 t... so that· ....1 ..theI'1ng ...1d not expose tbeII ucI that the cel1~r
boards be. Jved.. the ce11.r ft11" with grave1. They both assured me that
tbere ....1d be no prob1_ to do thtrlclcltdona1 wort and .. huded bade for
Deadborse.
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tM n.... .11....;,... tile ?U ~~r .1dH 0.. top. ,..,IA _rbr cor-
rect" ta-ttttes 1M .,1 with ~ tøfDNatt_ 011 tt. ........ tile ca11ar .
s.... ta t~1'" '*'_ tt Is unfl11.. ltas 100M boerds . top ..tell
....,.. be IllLhd -'lor c:oønd; u4 ..t of tbe I~ pipes ~ ... wt
eft or ...t .... 1M ~ .... Ie sba11_ ...... tile.....' that .....1 _tberi..
wt11 .~ .11 ~ s..nl 10G1e boards a... 1.YI81 a""" ..... tile ratilo1. cue- '
_t t.s att11 Ittcttlll lIP- . . ·
. .
PMta " ts . 1ttt1e farther., fr_ the _11~ but IIIows the PÚ _rker
1. a. ......11. SewnI 100se ...... .... apoud .. tile gra.'. .... .
s_1 .... I. 1M r........l_d. ~ f1G fs·to the eut sf. of tile _11l1en.
off of 1M ..... Md It .... I ¡¡;¡¡&¡. beat 301.t of pipe Md . porttan of .
be1ft1. ~ t. off of U. seuu. edge of tbe pad aad sIIrvs Msce11aneous
ClIPS. CI8S~ '
I bH .....taas1, *'<, t8d Juñ .....t eVW7 t_ _ttOMd tn the abene photos
fn .. prntoss Yis1t . JHr 19o. wltb sfM1.r photos. sbcwlng these s-. boards~
_tal buds. tnsIa. 1M pteces of pipe 1Q1ng ... W" off of the pH. It is obYfous
what.2ftr a.tnctlDr ..rf.... -d tM c1.....up wrt for Exxon on1.1 did a ..,1
...t of ..-k ArOiM tIaa .11......
;',
I 1111ad out II Ft.ld Trip lD!pecttcalReport (attached) indtcating the unsatis-
factory condition of the c1N1t-Up aad what needled to be done to correct It. I
oaly speat. 15 II1nutes 08 the 1ocation and at 3:15 p.a. __ took off and departed
for DNdhorse.
After arrtYing at Deaclhorse. _ retumecl to the Nabor's camp and the Bechtel
tiff1œ. where I provided Mr. Vln A11en with copies of the Field Reports and
we a~in went ever the ~irenents for satisfactory completion of the clean-
up on the P1ac1d 1ociltion.'
I then cc..,tactecl Mr. J1. Taylor. contractor for the Mobil 011 Corporation. and
lnade provisions to spend the night at "abor's camp at Mr. Taylor's request. At
4:30 p... 1 left with Mr. Taylor and his pilot in the Mobn chartered he11co,ter
and headed for the West ICadleroshi1ik location.
1101;11' s West Kadleroshl1 it No.1. Sectton 14 151 R14E tJ .M. PIA March 18
1974) - This wel1 is one of several leases an we s wave n trans-
1eñ=êd f". fedenl luthortb to state authority. This was ~ second visit to
l.his locatton. I had tnspected thts locatton and requested additional woñ to
be perfoYWd before tt could be satisfactorily CGIIp1eted.
Photo 112 was tlken neftr the tce airstrip 1ocatton and it shows a pile of
tundra grass and _tanll that ..5 scooped up when an area WIS cleared of
snow. The snow Ind tee ts just about ~1l ..lted now. leaving just a pile of
tundra grass. There SeeIIS toO ~ no probl. here since there appears to be
no tundra dØIIgl.
Photo 113 tl a picture of the reseeded airstrip area. Close inspection .
showed this to be in verJ good condition wit.., the new seed growth coartng on.
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~17.1174
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tt:fi:l\. -:.:-.::=- .r~ l~ t::. w:.'M..":iip,.:, :- t= :;....
., ttnt visit lids _rtIIr ..s .11'Mfb' t. pIKe. At ':oM request of tile 0.5.'.s.
It .. .1.... tit the ... of t." Ittgh ...'1~Nd nther -:MIl _ tile tap of Ute
top n_ . tMt tt _1d be 1es. ftOticult1. (.a:orwJtng tð . U.$.1.5. rep.)
I .,,''' It .. .. ..... ewe tIIauP tt 'I .t the .,..1 tnsta11atb.
1M 1H1t ..... t8 tM ,........ .. tile ptt .,... .... t... grave1 bou1ders
M4I ... .... ud .. _ ....1.. ... __th.
PMto m Is a ptct.n of I portt_ of tile ptt ..... .nd a. ~ .,. -tft
~ MelEg'.... PbotD 11' t. . cttttm.t wt. of the pit aNa'" tbe .11-
... wttla tM .... of ifrt cawrt.. tile ..,1.....
, .
PhotLt1' ~. sIDfs . areas of the ClllPlita when ..œ dcðr1s ..... trash
laM ..... c1 up. 111t1 1ocatt.. .. ~1J .11 c1..... ..., and 100ks
WfI7..... I cœp11.-1 .. ..... t.,1oro. tile .-p1eÙDØS of till' _rlt. stnce
I bH DO ~'t'" Ft.ld Trtp Report 'ONS wftla _ I took 1Ir. TQ'1or's copy
of tM prwt_ ft.1d Trip IIpoñ fonI of 7-31-74 IDd wrot:II .. tM bottal '
that tbe .-.tts1adør.1 tc.s .. been COllected ... thlt tbe -F1na1 abandon-
.at ad 1ocatto. c1..1I .. ...,..-d 1-3- ·4.-
. "
Photo '20 Is . c1ose-up of the we11 pad. with the PIA marker and a D)und of
d1rt around the wel1hNd shown tn the center. .t:.lt:~,"'I;J;n·k_""qufte . -bit
durtng 'the ~ on th11,.1~~~.. and water is st1'" standing ,1n .11- the ~
, tJ;-acQ_·'~the',!lß1- ,p1t: .rea~ The foreground of the picture is very wet
and I.!!~, ca.p1.te1,,' s.oth ~_ to '"the- vehicle' "(cat)- tracks. t
Afbr c1rc1tng the 1ocatton we 1anded. With t.'1e wind sti11 very high the
chopper pt10t staved In the lircnft. Mr. Taylor anti I Wl1I~ecI the location.
I took Photo 121 t ~ the souu.st comer of the pad lrel. 100king across
the ft11ed pit toward tile w11heed. As I mentioned in 1'1 pnY10us report. the
so cal1ed -gn.'· used on this 1ocatton is "111, I II'Ixture of cong1~:Jerate
rocks with dtrt and would be . very cOðrse texturetl surface even under the
_,st 1dea1 grading cond1t~on~~,,~ ~.~ld' ,te11 that considerable work had bee~
dòM",s1Iidí,,'pmtõus visit iûIa that thë pit area WlS 1n"IÌiÍIdI"better-COncI't1~.
J toot Photo 122 sundtng on the aound of dirt by the PIA ..rker and looking
toward tn.. southlMst across tl!. ft11ed pit arel. I Wllked up to tIN! short
road leadtng to the aintr1p and took Phob ~23 of the supply pad area.. I
then wllked b,ck to the north along the east edge of the pad and took Photo
124, looking west toward the "fel1head m.lrker and helicopter. -
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~ L. ..,..11 -5- ~~ 17. 1914
">~cl.ï'·A1t:¡'è:·~¥Ú;~tj~,-..... ~~:_'. "...... "lit IDII tile.
411ft --. .... .... .........~ AII1~ aiM! ft-, 'IQ)...... COW of Ute ".,...
ne... ....'_ IIfor't .w .." 31. 1V74, I mte .,tøs ~tM. ''''1 .
~. jL IU t .. '1eatto. c'~~n .. ..... ~..... ~,'" . "'~'IIÞ 1974.·
~ ~"r ~. I
.. 1.... ** \Ide ... (Iw J J ~ _... bHdN for tIae Hi tlat 1... IQ State 1oa-
,teL ."
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.... .." I
ta.Ibø
. .. KA" : PeL
... It 8t.' I toot thne ....tos of Ibis 10a ttoa a11 ,... apprarl_bt 1.1
U. s-. ..Ie ... ,11 ,.,. ... Itr. ~ uQ 11- a png..,stN17 closer
wtw 9' 1M .," c,..... ... -1...W pM vitia 1M cttrt ~ aruund the .11-
..... ... . PM __ .... c._.
De ttnt pIIOtD. ..... 125 .11ows OM to see u.. 1abs around the location
aIMI tM .... 1~.. off &.0 tINt .tntr1p. Photo 121 ts esMllt1a11y a close up
of tM ... ..... wiD . road 1udtDg off to the afrs~D tll the background. I
COII1d 1M ,... tJl1s yt., tMt tbe 1a.,.. -.at of trash. ..tar..l. &Ad tron ~t
had .... 10catIMI .. th MIItbMut corner of the pM III"'N had bee.. ptcked up
.... · ~... As.. ~ c1..... I toot Photo '27. showing just the pAd .~. wi th
tile ~u. ~ ...,..1. tM dirt IIOIIftded .lrowMI tIMI _11 heAd III wi th the PIA
-~. .~
Fol1owtag thts pbotD .. circ1ed onr the location. so thAt I cou1d ,,1_ a~as
where trasIa had bMa I-..¥ed. I cou1d .1so see the w11 filled and gnded
arM 011 the northwest comer of the pad where I had cJisccr1er~ a sunken are.
with at pudd1. of ot1 on .., preytous Yistt..
We th-!n heided for Bullen Point. Mobt1' s supp1y depot. on the DNlufort SN
co. st11 ne.. I noted on ~. T&,)'1or' s copy of ~ previous Inspection report.
dated July 7. 1974 that an uns.atisflctory 1teas Nd been ·co~cted and
FiM1 ab.1ndoœ1ent ind location clean-up was approYed September J. 1974.·
We arrived at Mobt1's Bunen Point supply depot It 1:00 p.m. with the high
winds sttl1 in progress. We could see that isH of the available C~ we~
out trying to eonutn the pillow unks and pit l1ners which were trying to
b10w out of postttun. Atter llnding and anchoring down the helicopter we
ill aided in tying down the pillow tank liners and later had dinner.. We
~turned to Deadhorse It 9:15 p.lI. The d'topper pl10t droppeo IbI! off at the!
r&abor's CAq) where I spent the ntghL
Thursda,ll S~~r 4, 1974 - I _de plans to deplrt Oeldhorsl! on the 9:45
a.II. f1 ight ind ~1tar obtafntng trlnsportation to the airport. found t.~
flIght WIIS delayed. FfMlly. the plane arrlnd And we deptlrted at 12715 p.lIiI.
I arr1ftd in Anchorage. after stopping in Fairbanks, It approximately 3:00 p.."
(M this n.ld trip 1 IDlde . preliminary fnsp!'Ct1on of P1acfdts Beer.~y Point
1lJCJt1on. where I ~utred idd1t1or..l wort to be perlonœd.. and wen's Point Sto..... .
It.?"en 1ouUon, whent I likewise will requ1re additional won to be perlo~_ "
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UNITED STATES
DEPARTMENT OF THE INTERIOR
GEOLOGICAL SURVEY
P.O. Box 259
Anchorage, Alaska 99510
October 16, 1975
Mobil Oil Corporation
P.O. Pouch 7-003
Anchorage, Alaska 99510
17(7-053
Gentlemen:
Attached hereto is an approved copy of the "Subsequent Notice
of Abandonment" for your ep 1 i JIm t No.1. Lease F -034405,
located in the SWt;SE-t, gection,.8, T. .8 N., R. 25 E., Umiat
meridian, and for your West K.adle_:r,P9_b,jJ,"i~J19_._J, Lease
F-03269.8, located in SWkSWk, Section 14, T. 5 N., R. 14 E.,
Umiat meridian.
Attached hereto are a few representative pictures o~ the
locations as they appeared in September 1975 when a joint
inspection of the locations was made by representatives of
the Alaska Division of Oil and Gas, Bureau of Land Management
and this office.
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At the time of the visit, the clean up and restoration of the
two locations was satisfactory. However, the lands on which
the above wells are located have been transferred to and are
now under the jurisdiction of the State of Alaska. Final ) _.-...--_~ .'-" , ,,' I .
approval of the location's conditions will have to be obtainec!,/ ê,,: / .'~. ~:;,;,~ '~/.
from appropriate State agencies. /' k$~
Sincerely yours,
(ORIG. SGD.) R. A. SMITH
Rodney A. Srni th
Oil and Gas Supervisor
Alaska Area
Attachments
cc: ~aska Division of Oil & Gas
Alaska Division of Lands
Bureau of Land Management
.MEMORANDUIV1
DEPARTMENT OF NATURAL RESOURCE
Division of Oil and ~ ~
TO O. K. Gilbreth, Jr. ~'~
Director ~
THRU: Hoyle H. Hamilton ;êltf~
Chief Petroleum Engineer
FROM: Lonnie C. Smith -¡ (' \
Petroleum Engineer
State of I,¡aska
DATE October 23~ 1975
FILE NO:
TELEPHONE NO:
/ "7Ó - 053
SUBJECT: North Slope Abandonment Inspection
with USGS and 8LM, Mobilis Bel;
Unit No.1; Sec. 8, T4N, R23E, UM.
Tuesday September 9, 1975 - We departed Texaco's Kad River location at 3:12 PM
heading east for the Canning River area but shortly before reaching the river
we turned south and soon found Mobil's location.
Mobil's Be1i Unit No.1, Sec. 8, T4N., R23 E., UM.; P&A 6/24/73; F-034405
I made two inspections of this location last summer and had given Mobil my
approval on September 3, 1974 (see report of 9/14/74). The USGS and the BLM
people had not revisited the lease since then.
We landed, after circling and making the usual pictures. 1. took Photo No.8
from the air which shows almost all of the well site pad and the camp area pad.
The old pit area is still the wettest portion of the pad with some water stand-
ing in ruts. After landing, I tooK Photo No.9 showing the wellhead marker
with gravel mounded over the casinghead in the background looking across the
worst part of the reserve pit area which still appears to be in good shape and
very similar to the way I left it on my previous visit. Photo No. 10 is a por-
tion of the mousehole pipe with rocks in it sticking up near the mound of dirt
by the wellhead marker. We kicked some more gravel and dirt over this. Every-
one was well satisfied with the condition of this location, so we soon took off
and headed southeast again. immediately after leaving the location we flew
over a hilltop and found the gravel pit that had been used to build the location.
I took Photo No. 11 looking north across this gravel pit area. There is some
snow obscuring the ground but it appeared in relatively good shape.
This is the second of 14 well locations inspected on federal leases ~hich are
to become state leases. In discussing this location with Bill Wunn~ke we
~reed that nothing further needed to be done at this locatinn---
S:-..' " -+ I.~· _ (,....,.... 11S'G'S EÅ",h·,\ }c.. u~-"))(¿·(.)r·'1 ðti~<"LI:-~) SA\.o' +L,'cs
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. . REV A.XL 6::Jà
Jward..Clyde Consultants .-
..ate "and Time: "8/1:J,/ '1{
- wee Project No.: 91 C0650A
Client Name: Mobile Oil Exploration
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SitelWell Name:
wee Site ID:
API Well Number:
SITE OBSERVATIONS
( If applicable. note items on site map)
176 -O$~
Pit
1) An obvious Pit O~lf NO goto next page)
No Dyes ~ Describe:
1a) Conditi~e t Intact? n ~
No DYes ~ Describe: ...'ÐV~'I"" w
~red? -) ,~
NO' ,as E Describe: 'f! # 'l. ~'^-
A '
reded?
No DYes D
Describe :
1 b) Õn evidence of wind or water erosion of pit dike?
No Yes D Describe:
1 c) Does slo~ appear stable?
No DYes,LQ:L Describe:
1d) Does t~n any substance? (liquid,solid,sludge,color, uniformity)
No DYes Describe: ~) fh. ~ ~
1 e) Evidence~kfilled pit?
No DVes ~ Describe:
1fl~ence of erosion of pit contents?
No~es D Describe:
19) !!!i.evidence of subsidence of dikes ~r p~ contents?
No L-.JVes D Descnbe: ~ 'r .fe,L.X-
1h) Standing~waterinQi. _
No DYes.l2S:l Depth: Describe: S~&.'r
1;) Surface ')~aCl w~h of p~ dikes?, ß
No Dyes Descnbe: '"" west <t¿'; ftt¡ G\ fr' r,,15
1j} ~e of seepage from pit?
No~es D Describe:
1~) ~e of overflow of pit to su"ounding area?
N~es 0 Describe:
~he urface of the ph contents cracked? Water in crack?
o ~es B Describe:
No s Describe:
1 m~e~lIing away from the edges of the pit?
No ~Yes L.J Describe:
:iJ$: j.,
· ;r'/·
j
Field Information
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SIIe/Well Name: 0e~,' l)¡,d-"f: J
wee SltelD: M4'8 -0
API wen Number: 1 1-q () 0 0 ~ DO
REV A.XL
d~rd-CIYde Consu"ants tiÞ
ate and Time: ~/ 11./~J
VCC Project No.: 91 COSSOA I
Client Name: Mobil Oil ExDloration
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SITE OBSERV A T10NS ( H applicable, note Items on site map)
1n) Djpr¡Sions in ~a that may hold standing water in some instances?
No ve~ Depth: Describe:
10) Evidence ~rusion 01 pit (tracks,burrows,etcp
No Dyes Describe: t"(~c.r.s 1 ~I ~~...
Pad
2) Any standi';f~ water on pad? _ _ n
No DVes Depth: CIf Describe: ~ ç..vr;JJ- f o,JJ
170 -óS-3
3) ~eui h~drocartJon sheens or odor on the pad or pit when soil or water is disturbed?
No ~es Describe:
4) S~ areas or obvious burial sites?
No ~esCJ Describe:
5) »lOn of a refueling area on pad? (i.e. diked area on pad, fuel stand)
\k) Ves CJ Describe:
6) A, oth¡r i~ areas on the pad other than the pit?
No Yes~ Descrile: west-Ø'lt -D p:t- ~ 'i'p~S 1-0 ~
7) Debris on site? C\ ~aAIiJ£ ~~ ÞL ....ue... . P(aM- p, 1-. fcr~' ,
No Dvã~ Describe: I
~ S,\J...¡j,[ ':¡M~<It" '6 ~,S -r ....,.....le.A ,,',,'-'tJ.f"
7a) Can debris be burned or buried on site?
No Dves ~ Describe:
8) ~ ¡nv jntainers on-site (i.e. drums,pallets, bags)?
No ~s Describe:
Sa) Estimated amount of waste and condition of containers:
Describe:
9) "'ktnce of buried trash?
No VesD Describe:
Describe:
ce that trash had been burned prior to disposal?
Describe:
AEV~ 0
~rd-Clyde Consultants
ate and rarne:
wee Project No.:
. ..- -~. Client Name:
Field Information
Pg. _ of
91 C0650A
Mobil Oil Exploration
~ It "-('11
I
Site/Well Name:
wee Site ID:
API Well Number:
MP~-o 4
't q "000)..00
GENERAL OBSERVATION OF AREA (include in sketch if applicable)
10) Îny i¡dication of 9Perating company? ~signs,stickers, et~) '.
No Ves ~ DescnbeJ. Nto', I Ù I ( L<0 ~.
11) Identifying marks on we~1 L~ q, Sf ~ F 0::' l..{ t-t a..5
No Dves gr ~escribe: 5 £,!~ >
.p J e C ~ T ¡lIt..u T ') '1 EJ J. 1-'1
. e.r IV 't- -!:..' 'rJ... tJ.... Vl"
12~sed or unusually lush vegetation in area? f Z -//
~Yes D Describe: 3 q I......... :~...'" 5.~ j
13) Evidence of natural events (e.g. floods, mud flows, freezelthaw heaving) c.-~ ~
~o ~ ~
~ \,"
7Ô -ð53
(Æ'+#-j
Water
14) illY iUrfac~ area? (Streams. creeks etc.)
No Ves Distance from pit: Describe:
~ fD ,~/I~ (a~)· I'~~~
14a) Direction of surface water flow? a
'fv C ~
.£~Y petroleum hydrocarbon sheen or odor produced when water/soil disturbed?
-. No es D Distance from pit: Descnbe:
15~kes, ~nds or swamps in area?
No ~es D Distance from site: Describe:
\"08_ ':-.- j
. f J ...: J 3 L" S
..... ~ I ß Lt Lo.¿
P i ~ ~'i ~1-- 6;;
~
~- ,. FI'1 '-)
VP 15'1 Cf.S
w'^-'
Wlldllf.
16~ng water within 1/4 or within 1 mile of site that may be habitat for fish?
No ~es D Distance from site: Describe:
17} ¡V iidenl~fe in area? Where?
No Ves Distance from site: Describe:
~1·~C7V rra('~ftl~~r'~.s . ,
Humans ~\ I,. \000 \..VI~ I", t '%. ""ILL 1J 'f', 4e-
18} ~ence of human habitation! use wit in 1/4 or within 1 mile of site?
No es D Distance from site: Describe:
19~5ily accessible to humans? (Road to site, nearby village or hunting area)
No ~es D Distance from site: Describe: .
20~ence of humans at site? (Beer cans, vehicle stracks. camp fires ,etc.)
'JO~es D Describe:
Field Information
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7f'.Ø1 ~ REV A.XL ~
- WoodW8~lyd. Consultant. .,
. _ '1ateand time: tb / I ).. ( Of. I
vee Project No.: 9] C0650~ · 'r=+-
enent Name: Unbil Oil Eyploration
SiteJWell Name:
wee Site 10:
API We" Number:
We" Head Location 0\" ~~
Water Sample Location , '7 (} ,- D 5 ~
SoiVSludge Sample location
Background Soil Sample
Background Water Sample
II
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Legend:
srÆ MAP OF AREA
Sample ID: (CIien\)(WCC Site IDtI)·WA-(SamPIe no.")
Sample ID: (Client)(WCC Site IDN)-SO-(Sampte no.">
Example:C1B01-WA-01
wcc Site lD: PB. Prudhoe Bay
AP.AIaSka PeninSUla ,
SC-Kenai Peninsula/South Central
SR.Brooks Range .
IS-Icy Bay I'll
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ENVIRONMENTAL TESTING AND CERTIFICATION CORP.
320 TESCONI CIRCLE. SUITE G. SANTA ROSA. CA. 95401 (707) 544-5570
AUGUST 31, 1991
CLl ENT :
~WARD-CLYDE CONSULTANTS
701 SESAME STREET
ANCHORAGE, AK 99503
ATTN:
JANE THOMAS
ANALYSIS:
PROJECT:
JOBLINK NUMBER:
MATRIX TYPE:
COLLECTED BY:
ALUMINUM, BARIUM, CADMIUM, CHROMIUM, lEAD, MERCURY, NICKEL, POTASSIUM, SODIUM, ZINC
91C0650A
805435
LIQUID
MOBIL OIL EXPLORATION & PRODUCTION
SAMPLE NO_
SAMPLE POINT SAMPLE DATE DATE IN LAB
MPB01WA-01 08-11-91 08-15-91
MPB01WA-02 08-11-91 08-15-91
MPB01WA-03 08-11-91 08-15-91
MPB01WA-04 08-11-91 08-15-91
MPB04WA-01 08-12-91 08-15-91
MPB04WA-02 08-12-91 08-15-91
MPB04WA·05 08-12-91 08-15-91
MPB05WA-01 08- 12-91 08-15-91
MPB05YA-03 08-12-91 08-15-91
MPB05YA-06 08-12-91 08-15-91
MPB05YA-05 08-12-91 08-15-91
MPB06YA-01 08-13-91 08-15-91
MPB06YA-02 08-13-91 08-15-91
MPB06YA-04 08-13-91 08-15-91
MPB07\lA-01 08-13-91 08-15-91
MPB07\lA-02 08-13-91 08-15-91
MPB07\lA-04 08-13-91 08-15-91
MPB07\lA-05 08-13-91 08-15-91
MPB08WA-02 08-13-91 08-15-91
MPB08WA-03 08-13-91 08-15-91
MPB08YA-04 08-13-91 08-15-91
MPB08WA-05 08-13-91 08-15-91
MPB09\.lA-01 08-13-91 08-15 -91
MPB09UA-02 08-13-91 08-15-91
MPB09UA-03 08-13-91 08-15-91
MC3454
MC3455
MC3456
MC3457
MC3458
MC3459
MC3l,.60
MC3461
MC3l,.62
MC3463
MC3464
MC3465
MC3466
MC3467
MC3l,.68
MC3469
MC3470
MC3471
MC3472
MC3473
MC3474
MC3475
MC3476
MC3477
MC3478
This report is "PROPRIETARY AND CONFIDENTIAL" and del ivered to, and intended for the exclusive use of the above
named client only_ Environmental Testing and Certification Corp_ assumes no responsibility or liability tor
the reliance hereon or use hereof by anyone other than the above named client_
Environmental Testing and Certification Corporation_
-& t. f~~~ ~
Thomas E. Gran, Ph.D:, Vice President, General Manager
ETC Santa Rosa
7/'1/11
Date
~
~ITC~
.~
A DECADE OF OUALlTY AND SERVICE
/
-,- I
Se: 'n I &';hain of Custody L..ud Analysis Request psgeL.CJtf
'--
Consultant l)Jtu~A.LJ - CL"O e (~~ !'µ',,'¡'J
Address ~I JtrJ'f14t ST. Woodward-Clyde Consultants Q
JI. II ¿..I" .' a. ~ AI(. ~:1foJ
v
Phone NQ'.~ .5t/-,· 2.ø Fax No.~ S"'J ... 3198 701 Sesame Slreel
Project Manager .1?--Ll fk · "" .....s Anchorage, Alaska 99503
Alternate Contact \A r ~ .1 -t-!ol,oEA Sampler M t)ß;' (!) L I 'E )( I' J 01£1f -I: ~ t Pr"J.. ",+,' ð '"
Project No. 9/(.. 0 b ~o'" P.o. No. 9/~Ð'SoAJ~Doo Regulatory Agency ~D~c..
Section II: Analysis Request fÝ¡.ik : O"J ''1- MLJ-.l.J .I Jþ-t 1/ I;j h l.(,.x- h.e.e-"J ;q.tl.. J-tA..Y e..,º-
~. . .~ . ,c¡ õ Sampling Remarks
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., V\.t S\)~~ ~ - o Røœnt Contaminaåon
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en . . ~E ~E ") .Jq:~ j ~~ " o Monitoring
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Sample u, 10' ~! ~
UJUJ ~~ -~ i~ ~~tù -='" -c ; ~ E
Identification I\t1atrix a.U1 ~~ ~ëtll u ,... q; F- ~ Q 1= ~ o Undervomd Storege Tank
wC'J >111 to- .
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Relinquished by ~/Í^_, 5 ~ fL) ,(1ft d /Tme ReClINed by ~~kL.__ . Lab please initJal the following:
Organizøt;on (/ \,4/( -( - ~'/~ 10, I (ìgøniz8l:ion .£~ /.~ ~ ./... C""c...
Samples Stored in Ice
Relinquished by DøœlTma ' , I Receiwd by Approprillta Containers
10rtI animtion G-gønimf .... Sample& Pre&erwd
VOAs without Heød&pacø
Aølinquishod by - Dota/Tama AeœNød by CormwIt&
.Organization G-g ...iz......
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DATA SUMMARY REPORT DATE: 09/09/91
PAGE: 7 .
Company: WOODWARD-CLYDE CONSULTANTS
Sample Point ID: MPBOIWA-01 MPB01WA-02 MPBOlWA-03 MPBOIWA-04 MPB04WA-Ol MPB04WA-02 MPB04WA-05 MPB05WA-Ol
ETC Sample Number: MC3359 MC3360 MC3361 MC3362 MC3363 MC3364 MC3365 MG3366
SamtJ1e Date: 910811 910811 910811 910811 910812 910812 910812 910812
Faci11ty Code: WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZ\'¡ WWCANCHHZ\'¡ WWCANCHHZW WWCANCHHZ\'¡ WCANCHHZt'J
Parameters Units
EPA METHOD - 6010/7000 SERIES METALS (AR72)
A1uminumt Total mg/L 1.37 .300 <.200 <.200 .420 .671 <.200 <.200
Barium, ota1 mg/L 2.58 .138 .151 .122 .584 .676 .149 .193
Cadmium, Total mg/L <.010 <.010 <.010 <.010 <.010 <.010 <.010 <.010
Chromium, Total mg/L <.030 <.030 <.030 <.030 <.030 <.030 <.030 <.030 -
Potassium, Total mg/L 6.31 9.61 2.16 1.45 3.71 7.15 4.45 1.
Sodium, Total mg/L 142 109 47.3 37.2 79.9 215 217 26.6
Nickel, Total mg/L <.030 <.030 <.030 <.030 <.030 <.030 <.030 <.030
Lead, Total mg/L <.050 <.050 <.050 <.050 <.050 <.050 <.050 <.050
Zinc, Total mg/L .041 <.020 <.020 <.020 <.020 <.020 <.020 <.020
Mercury, Total mg/L <.001 <.001 <.001 <.001 <.001 <.001 <.001 <.001
Sample Point ID: MPB05WA-03 MPB05WA-05 MPB05WA-06 MPB06WA-Ol MPB06WA-02 MPB06WA-04 MPB07WA-01 MPB07WA-02
ETC Sample Number: MC3367 MC3369 MC3368 MC3370 MC3371 MC3372 MC3373 MC3374
Samî1e Date: 910812 910812 910812 910813 910813 910813 910813 910813
Faci1 ty Code: WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW \.¡wCANCIIHZt.J
Parameters Units
EPA METHOD - 6010/7000 SERIES METALS (AR72)
Aluminum, Total mg/L <.200 < . 200 .554 <.200 <.200 <.200 <.200 <.200
Barium, Total mg/L <.040 .429 .359 1.30 1.42 .581 .124 <.040 - ,
Cadmium, Total mg/L <.010 <.010 <.010 <.010 <.010 <.010 <.010 <.010
Chromium, Total mg/L <.030 <.030 <.030 <.030 <.030 <.030 <.030 <.030
Potassium, Total mg/L 1.48 3.82 2.23 4.94 2.45 1.21 1.57 <1.00
Sodium, Total mg/L 13.4 268 186 293 98.1 38.9 35.0 5.86
Nickel, Total mg/L <.030 <.030 <.030 <.030 <.030 <.030 <.030 <.030
Lead, Total mg/L <.050 <.050 <.050 <.050 <.050 <.050 <.050 <.050
Zinc, Total mg/L <.020 <.020 <.020 <.020 <.020 <.020 <.020 <.020
Mercury, Total mg/L <.001 <.001 <.001 <.001 <.001 <.001 <.001 <.001
I
~
09/09/91
1 .
¡---
I
DATE
PAGE
I
DATA SUMMARY REPORT
MPB04WA-05 MPB05WA-Ol
MC3365 MC3366
910812 910812
WWCANCHHZW WW'CANCHHZ\·¡
MPB04WA-01 MPB04WA-02
MC3363 MC3364
910812 910812
WWCANCHHZW WWCANCHHZW
WOODWARD-CLYDE CONSULTANTS
MPB01WA-01 MPB01WA-02 MPB01WA-03 MPB01WA-04
MC3359 MC3360 MC3361 MC3362
910811 910811 910811 910811
WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZ\J
Sample Point ID
ETC Sample Number
Sample Date
Facility Code
Company
Units
(AR55)
Parameters
GONVENTIONALS
Chloride
3
MPB07WA
MG3374
910813
WWCANGHHZ\J
--- ')
17
309
MPB06WA-02 MPB06WA-04 MPB07WA-01
MC3371 MG3372 MG3373
910813 910813 910813
WWCANCHHZW WWCANCHHZW WWCANCHHZ\.J
243
8
57
1
MPB05WA-05 MPB05WA-06 MPB06WA-Ol
MC3369 MC3368 MC3370
910812 910812 910813
WCANCHHZW WWCANCHHZW WWCANCHHZt.J
82
2
61
3
63
95.4
MPB05WA-03
MC3367
910812
WWCANCHHZt.J
mg/L
Sample Point ID
ETC Sample Number
Sam{>le Date
Facillty Code
19.8
Units
(AR55)
Parameters
GONVENTIONALS
Chloride
112
MPB07WA-04 MPB07WA-05 MPB08WA-02 MPB08WA-03 MPB08WA-04 MPB08WA-OS MPB09WA-01 MPB09WA-02
MC3375 MC3376 MC3377 MC3378 MC3379 MC3380 MC3381 MC3382
910813 910813 910813 910813 910813 910813 910813 910813
WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHlIZ\J
4
77
144
489
148
332
38.2
mg/L
Sample Point ID
ETC Sample Number
Sam~le Date
Faci1lty Code
Units
Parameters
7
24
29.1
792
274
515
250
276
117
mg/L
(ARSS)
GONVENTIONALS
Chloride
I . .
( ¡
DATA SUMMARY REPORT DATE: 09/09/91
.
PAGE: 3
Company: WOODWARD-CLYDE CONSULTANTS
Sample Point ID: MPBOIWA-Ol MPBOIWA-02 MPBOIWA-03 MPBOIWA-04 MPB04WA-Ol MPB04WA-02 MPB04WA-OS MPBOSWA-Ol
ETC Sample Number: MC3359 MC3360 MC336l MC3362 MC3363 MC3364 MC3365 MC3366
Sam11e Date: 910811 910811 910811 910811 910812 910812 910812 910812
Faci1 ty Code: WWCANCHHZW WWCANCHIIZW WWCANCHHZ'~ WWCANCIIIIZ'~ Wt'¡CANCHHZW WWCANCHHZW WWCANG1IIIZW WWCANCIIIIZ\.¡
Parameters Units
~PA METHOD 8020 - AROMATIC VOLATILE ORGANICS (ARS8)
Benzene ug/L < . 500 <.500 <.500 <.500 <.500 <.500 <.500 <.500
Ethy1benzene ug/L <.500 <.500 <.500 <.500 <.500 <.500 <.500 <.500
Toluene ug/L < . 500 <.500 <.500 <.500 < . 500 <.500 <.500 <.500
m-Xy1ene ug/L <.500 < . 500 < . 500 <.500 <.500 <.500 <.500 <.500
o+p-Xy1enes ug/L <1.00 <1.00 <1.00 <1. 00 <1.00 <1.00 <1.00 <1. 00
Sample Point ID: MPB05WA-03 MPB05WA-05 MPB05WA-06 MPB06WA-Ol MPB06WA-02 MPB06WA-04 MPB07WA-01 MPB07WA-02
ETC Sample Number: MC3367 MC3369 MC3368 MC3370 MC3371 MC3372 MC3373 MC3374
Samt1e Date: 910812 910812 910812 910813 910813 910813 910813 910813
Faci1 ty Code: WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZ\·¡
Parameters Units
EPA METHOD 8020 - AROMATIC VOLATILE ORGANICS (AR58)
Benzene ug/L <.500 < . 500 <.500 < . 500 <.500 <.500 <.500 <.500
Ethylbenzene ug/L < . 500 <.500 <.500 <.500 <.500 <.500 <.500 <.500
Toluene ug/L <.500 <.500 < . 500 <.500 < . 500 <.500 <.500 <.500
m-Xy1ene ug/L <.500 < . 500 <.500 <.500 <.500 <.500 <.500 <.500
0+p-Xy1enes ug/L <1.00 <1.00 <1.00 <1.00 <1.00 <1.00 <1.00 <1.00
~--
Company: WOODWARD-CLYDE CONSULTANTS
Parameters
Sample Point ID:
ETC Sample Number:
Sam{>le Date:
Facillty Code:
Units
CALIFORNIA LUFT ORGANICS (AR62)
Diesel
.
DATA SUMMARY REPORT
\
/
DATE: 09/09/91
PAGE: 5
.
MPB01WA-01 MPB01WA-02 MPB01tJA-03 MPB01tJA-04 MPB04tJA-01 ~IPB04WA-02 MPB04tJA-05 HPB05WA-Ol
MC3359 MC3360 MC3361 MC3362 MC3363 MC3364 MC3365 MCJ366
910811 910811 910811 910811 910812 910812 910812 910812
WWCANCHHZt.¡ WWCANCHHZ\'¡ WWCANCHHZW t.J1JCANCHHZt.¡ w\'¡CANCHHZW WWCANCHHZt.¡ WWCANCHHZt.¡ w\'¡CANCHHZ\.¡
ug/L <1200
<1200
2400
<1200
<1200
<1200
<1200
<1200
Parameters
Sample Point ID:
ETC Sample Number:
Sample Date:
Facility Code:
Units
CALIFORNIA LUFT ORGANICS (AR62)
Diesel
MPB05WA-03 MPB05WA-OS MPB05WA-06 MPB06WA-Ol MPB06WA-02 MPB06WA-04 MPB07WA-Ol MPB07WA .-,
MC3367 MC3369 MC3368 MC3370 MC3371 MC3372 MC3373 MC3374
910812 910812 910812 910813 910813 910813 910813 910813
WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZ\~
ug/L <1200
<1200
<1200
<1200
<1200
<1200
<1200
<1200
Parameters
Sample Point 1D:
ETC Sample Number:
Sam{>le Date:
Facility Code:
Units
CALIFORNIA LUFT ORGANICS (AR62)
Diesel
Gasoline
ug/L
ug/L
MPB07WA-04 MPB07WA-05 MPB08WA-02 MPB08WA-03 MPB08WA-04 MPB08WA-05 MPB09WA-01 MPB09WA-02
MC3375 MC3376 MC3377 MC3378 MC3379 MC3380 MC3381 MC3382
910813 910813 910813 910813 910813 910813 910813 910813
WWCANCHHZW WWCANCHHZW tJtJCANCHHZtJ WWCANCHHZW WWCANCHHZtJ WWCANCHHZ\'¡ WWCANCHHZW WWCANCHHZW
2400
2100
4000
2100
<100
<100
-
-
-
-
-
-
-
-
<100
<100
~~
09/09/91
~
9
\i
DATE
PAGE
..
(
DATA SUMMARY REPORT
WOODWARD-CLYDE CONSULTANTS
MPBOlWA-Ol MPBOlWA-02 MPBOIWA-03 MPBOlWA-04 MPB04WA-01 MPB04WA-02 MPB04WA-05 MPB05WA-01
MC3359 MC3360 MC3361 MC3362 MC3363 MC3364 MC3365 MC3366
910811 910811 910811 910811 - 910812 910812 910812 910812
WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANGHHZ\
Sample Point 10:
ETC Sample Number:
Sam(Jle Date:
Facility Code:
Units
Company
<3.80
<3.80
<3.80
<3.80
<3.80
80
80
80
80
80
<3
<3
<3
<3
<3
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
(AR99)
<3
<3
<3
<3
<3
80
80
80
80
80
(PCBs)
80
80
<3
<3
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
POLYCHLORINATED BIPHENYLS
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
Parameters
EPA METHOD 8080
PCB-I016
PCB-1221
PCB-l232
PCB-1242
PCB-1248
HPB07WA-02
MC3374
910813
WWGANGHHZ\·
MPB05WA-03 MPB05WA-05 MPB05WA-06 MPB06WA-01 MPB06WA-02 MPB06WA-04 MPB07WA-Ol
MC3367 MC3369 MC3368 MC3370 MC3371 MC3372 MC3373
910812 910812 910812 910813 910813 910813 910813
WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW WWCANCHHZW
Sample Point ID:
ETC Sample Number:
Sample Date:
Facility Code:
Units
PCB-1254
PCB-1260
Parameters
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3 . 80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
(AR99)
<3
<3
<3
<3
<3
80
80
80
80
80
(PCBs)
80
80
<3
<3
80
80
<3
<3
80
80
<3
<3
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
<3.80
POLYCHLORINATED BIPHENYLS
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
I!:PA METHOD 8080
PCB-I016
PCB-1221
PCB-1232
PCB-1242
PCB-1248
PCB-1254
PCB-1260
'..
1996 Water Quality Criteria Standards Applicable to Inactive Reserve Pit Closure t
Drinking
CCC Value CCC Value Freshwater Sa/lwater Water Selected
Freshwater Dissolved from 82 from C2 Chronic Calculated CCC Chronic Calculated CCC Standards * AWaS Limit
Compound · Conversion Factor Hardness DeDE ndent Factors (uglL) ** (ugIL) ** em ill) em ;¡/L) 'mail) emg/l)
Acute Chronic ma ba mc bc Dissolved Total DissolveCl Total
Aluminum - .. - .. .. .. .. - - - - - 0.2 0.2
Arsenic - .. - .. .. .. 190 36 0.19 0.005 0.036 0.036 0.05 0.01
BarIum - - - .. .. .. - .. .. 1 .. .. 2 1
Cadmium 0.911 0.876 1.128 -3.828 0.7852 -3.49 1 9.3 0.0018 0.0021 0.0093 0.0093 0.01 0.0021
Chromium III 0.316 0.86 0.819 3.688 0.819 1.561 180 .. 0.34 0.39 .. 0.0056 0.10 0.10
Chromium VI - .. - .. - - 10 50 0.010 0.011 0.050 0.050 0.10 0.011
Lead 0.677 0.677 1.273 -1.46 1.273 -4.705 2.5 8.1 0.0058 0.0086 0.0081 0.0056 0.015 0.0086
Mercury .. .. - - - - 0.012 0.025 0.000012 0.000012 0.000025 0.000025 0.002 0.000012
Nickel 0.998 0.997 0.846 3.3612 0.846 1.1645 160 8.2 0.30 0.30 0.0082 0.0083 0.1 0.1
Sodium - - .. - - - - - - - - 71 250 250
Zinc 0.978 0.986 0.8473 0.8604 0.8473 0.7614 100 81 0.20 0.047 0.081 0.088 5 0
Benzene § - - - .. - .. - - - - .. - 0.005 0.005
Ethylbenzene § - .. .. - .. .. - - - .. .. - 0.7 0.7
Toluene § .. - .. - - - .. .. - .. - - 1.0 1.0
Xylene § .. - - - .. - - .. - - .. .. 10.0 10.0
PCBs-1260 - .. .. - .. - 0.014 0.03 - 0.000014 - 0.000030 0.0005 0.0005
DIesel Range
Organics §§ - .. .. .. .. .. .. - .. - .. .. .. -
Notes:
Hardness dependent values are based on the area background average of 218 mgIL CaC03
t ADEC Water Quality Standards (July 1996, 18 AAC 70.020) incorporate Federal Standards in 40 CFR 131.36.
Criteria based on 18 AAC 70.020 (1)(c) water use. If a Federal standard does not exist then Alaska Drinking Water Standards were used.
tt EPA Water Quality Standards from 40 CFR 131.36 (b) (1) matrix.
* Bold compounds Indicate parameters listed In current Inactive reserve pit closure table in 18AAC60.440
** Minimum Hardness Is 25 mgll and Maximum Is 400 mgIL (40 CFR 131.36 (c)(4»
Values In EPA Water Quality matrix are based on a hardness of 100 mgIL
CCC=Crlterlon Continuous Concentration CMC=Crlterlon Maximum Concentration
§ The TAH In the water column can not exceed 10 ugJL (sum of 8020 results), 18 AAC 70.020 (1)( c)
§§ No numerical standard.
* Drinking Water Standards from July 1996 Alaska Drinking Water Regulations (18 AAC 80). Metals values are for total recoverable. No MCL for lead. ..
Lead value shown Is the lead action level.
** Metals values are for dissolved metals with the exception of mercury which is a total recoverable value.
AWaS-USE.XLS
Page 1
1/1 O/~H
·
4 ... ..
SITE NAME:
WELL DRILLED:
wee SITE ID:
DA IE VISITED:
Beli Unit # 1
1973
M PB-D4
8/12/91
1. Aerial view of site, looking east.
2. View of reserve pit cover material, looking south. Vegetation on
reserve pit cover is similar to surrounding vegetation.
,.
t'
.-...-.....-.-~
".. ; .... - ,I , "- ~ . _
. ,:\ :; .. j \ :: I I':
~ I 1 I I . ,
~ I !J [jìj ~ ;--
.-" .... -- -
..
I . I I
. .", I . ,'\ \, ~ . ,l,
¡J' 'u ".... u\
, !: I \ . : \\
. .-... I "- ~'~v· " . ,....... \
.... ',~ ~ u ~ ,-' .J .~ Lo '-'
TONY KNOWLES, GOVERNOR
\ UJ i!
',---- .~
DIVISION OF ENVIRONMENTAL HEALTH
SOLID WASTE PROGRAM
410 WILLOUGHBY AVE
JUNEAU, ALASKA 99687
http://www.state.ak.us/declhome.htm
I
f
I
I
/
i
DEPT. OF ENVIRONMENTAL CONSERVATION
Telephone: (907) 465-5162
Fax: (907) 465-5362
April 24, 1998
170-0S3
Mr. Albert Robb m
Mobil Business Resources Corporation
P.O. Box 650232
Dallas, TX 75265-0232
Reference: Issuance of Approval for Final Closure for Seven Inactive Reserve Pits
Dear Mr. Robb:
The Alaska Department of Environmental Conservation (ADEC) has completed review and public
notice for the Mobil Business Resources Corporation closure applications and requests for final
closure approval for inactive reserve pits. The closure applications, received January 21, 1997,
provided the required information showing that previous closure was approved by a state of federal
agency and that water does not accumulate in direct contact with drilling waste. The documents also
provided acceptable aerial photographs of the site and a statement explaining why further action is
not necessary to protect public health or the environment. ADEC coordinated review of closure
requests and field inspections of the sites with the Alaska Department of Natural Resources (DNR),
Bristol Bay Native Corporation, Tyonek Native Corporation, the Kenai Peninsula Borough, and fee
simple private land owners. Public notice requesting comments on the closure requests was
published January 30 & 31, 1998 in the Anchorage Daily News and February 2 & 3, 1998 in the
Peninsula Clarion.
No public comments were received in response to this public notice. ADEC has determined that the
reserve pits at these sites meet all the closure requirements of 18 AAC 60.440(b).
Closure Approval
Under authority of 18 AAC 60.440(c), ADEC grants final closure approval to Mobil Business
Resources Corporation for the inactive reserve pits at the following seven drill sites:
Well Name
1. Beli Unit #1
Landowner
DNR
- ':. ~.............,." ~ ~ :":::"I.~"·'"
, t
Mobil Business Resources Corporation
April 24, 1998
Page 2
Well Name
Landowner
2. Kuparuk 9-11-12 & Mobil
Phillips Tract Well 13-t5-tl-12
3. W Staines St. 18-09-23
DNR
DNR
4. Great Basins #1
Private
7. W. Tyonek #1
Bristol Bay Native
Corporation
Tyonek Native
Corporation
Kenai Peninsula Borough
5. Great Basins #2
6. Three Mile Creek State #1
Terms and Conditions
This final closure approval is subject to the following tenns and conditions:
1) In accordance with 18 AAC 60.440(1), the Department will require additional investigation,
assessment, monitoring or remediation if new infonnation regarding conditions at the reserve
pit facilities indicates that further actions are necessary to protect human health or the
environment.
2) The approval granted by this letter is for the inactive drilling waste reserve pit(s) only.
Closure for the pad as a whole (if required) must be coordinated between the owner/operator
and the appropriate land owner/manager.
Any person who disagrees with any portion of this decision may request an adjudicatory hearing in
accordance with 18 AAC 15.200-310. The request should be mailed to the Commissioner of the
Department of Environmental Conservation, 410 Willoughby Avenue, Suite 105, Juneau, Alaska
99801-1795. If a hearing is not requested within thirty (30) days of the date of this letter, the right
of appeal is waived. Please remember that even if an adjudicatory hearing has been requested and
granted, this decision remains in full effect during the process.
Sincerely,
.-../} /ì ,~1 ,., -
./ ~ _ / t:" 1,-, . :. ".";~;. :.
-
" 7 'L
-.. -"' -
~
Heather Stockard
Solid Waste Program Manager
r
,.
Mobil Business Resources Corporation
April 24, 1998
Page 3
cc: AJ Ou, ADF&G, Fairbanks
Windy Mahan, AOGCC, Anchorage
Don Karabelnikoff, Tyonek Native Corporation
Lisa M. Parker, Kenai Peninsula Borough
Nancy Welch, ADNR, Fairbanks
H:\HOME\RJPETERS\RSVPI1\MOBll..\FINCLOMO.WPD
//
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,..-,
\,
MOBIL OIL CORPORATION
ALASKA EXPLORATION DIVISION
POUCH 7-003
ANCHORAGE, ALASKA 99501
DATA .J:'RANSHITTAL RECOED
._---~-----.-_._--_..._---_._-~' .--...-- .'-"- - ~_._.. ~~.
TRANSFERRED TO:
State of Alaska
Division of Oil & Gas
-..---. -~._--_-.-....-- .
3001 Porcupine Drive - ~chorage, Alaska 99501
."....,._.~'..."_.
TRANSFERRED BY:
W. J. Hendy
DATE: 12/30/70
DATA DESCRIPTION
WEST MOQUAWKIE #1:
1 sepia and 1 B/L
IES log, 100'-8015'
1 sepia and 1 B/L
Mud log, 100'-8015'
2
Form P-4
2
Form P- 7
2
Well History
/////////////1/////////////////// LAST ITEM ///////////////////////////////////
_,.1 ,
PLEASE CHECK SHIPMENT THEN SIGN AND RETURN OR1C:.J:A1__9:2f.!
De~criptors to include when applicable:
-.---,----
1. Number copies or copy numbers
2. Type of print:: Field or Final
3. Type of copy: Film, Sepia,
Blueline, Velum
4. Series, Sequence or Interval
numbers
RECEIVED BY:
~'7W
1- Lf --r¡/
_A"-~_"'_u._.--..._... ..__.......,_ ....
DATE:
Porm No, P-4
,""""
:REv. g-:ìO-67 5, API Nl7:\fERlCAL CODE
OIL AND GAS CONSERVATION COMMITTEE 50-283-20035
, -
MON1'HL Y RlPoRr Of OIt'LL'NG 6, LEASE DESIGNA'I'10N AXD SERrAL NO,
AND WORI(OVER OPERAtIONS Cont. #1420_ 0300-1362
1, 7, IF INDIA»; ALoTTEE OJ? TRIBE NAME
OIt 0 GAS 0 -Wj,ldcat Nati~e Village of Tyonek
'WELL WELL OTHER
2, NA.ME OF OPERATOR 8, UNIT, F A.R.A1 OR LEASE NAME
Mobil Oil CorpOration Wes t MoqUawkie
3, ADDRESS OF OPEItATOR 9, WELL!\O
p. O. PouCh 7-003, AnchoraRe, Alaska 99501 #1
4, LOCATION OF WELL 10, FIELD A...\Tl) POOL. OR WILDCA.T
1200 FSL, 2390 FEL. Sec. 36, T121V, R12W, S.M. Wildcat
ll, s~~,. (Bo'M'OM HOI..F;
Sec. 36, T12N, R12W, S.M.
12, PE:R.1\UT NO,
70-53
STATe OF ALAsKA
.~
SUBMIT IN DuPLICA.TE
13, RE»QRT TOTAL D>:!>T¡; AT END OF lVONTII, C1Lu.rGEs IN ROLE SIZE, CAsING AND CEMElvnNG JOBS INCLtJDING DEPTII
SET AND VOL_ tJSED, PERFORATIONS, TEsTS AND FU;;s tJLTS , FISHING JOBs, J!JNl{ IN ROLE AND SlDE-TRACl<:ED HOLE
AND ANy 0'I'HErt SIGNIFICANT C1Lu.rDEs IN R04: C()jIlDI'l'IONS,
T.D. at end December 8015', P.B. to 0'.
p. &'A. 12/6/70.
Drilled 12-1/4" hale 7815~ to 8015 r.
CONFiDENTIAL
RE(t~VtD
in'i1
JJ\N 4 ",\I,
O~l AND GAS
OF '\
D1Y1SiO:t-ICHOR,AGI
14, 1 hereby
SlG1'I:ED __ Di~ision Geolo2ist OAT'>: 12/30/70 _ .
...- ::; - - - =- '-
NOTE-R,pOrt on this form Is r'<¡Ulred for each calendar month, regardless of the st..us of OP'rations, and mUst ... fil'd in duplica"
whh u.. Division of Mi.... & Mi"",.,s by the 15th of the SUCCeeding "0 11th, unl,ss otherwise directed.
(,\
,.
DATE
·1970
,~
~\
./
",.
NOB IL 0 JL _ºQR 1.: 0 10_~eI Q!'i
"""
HISTORY OF OJ-I, 01\.5:-=-'\,S HELL
. CONFIDENTIAL
OPERATOR
FIELD Wildcat
Mobil Oil Corporation
-------
WELL NOo
West Moguawkie #1
R_~W ____~ 8M _
36
T 12N
SEC.
DATE
12/10/70
'----;,/ ,. . ' .
. '. ' / C:lc (c'{ ( ~
-¡--------------
SIGNED
/ (,,'
., i ,,·>'''ì. -"'¿' '
TIlLE t(~,LJ~J/',.'1, /'l ,.',
-;
'd "
{/ {I- (~"I C,'~: ,-¿.. (
IJ -
----------
--------
--------'"
-._-----
-_.----~-------------.._-------
Th:hs well \.7aS drilled by Reo B. Montgomery Drilling Company using rotary rig 113/'¡,.
on location 1200' FSL, 2390' FWL, Seco 36, T12N, R12W, S'oMo
All depths refer to, Kelley Bushing elevation of 499', 20' above ground level
unless otherwise noted.
10/12-10/2~, );>et30" conductor and r!L~.
Drilled 24'1 conductor hole to 35 " ,opene'd to 48" and drove l~8n to 38'. Drove
30" pipe to 82' belQw ground level and cement w/230 sx, class "G" w/2% CaC12~
Pull 48" csgo, ,spot 30 sx, class f'G", around top of 30".
10/28-10/29 Drilled 17...1/2" hole 102'to 795'. Spud well 6:30 A.Mo 10/28/7ù.
10/29-10/30 Ran Schlumberger lo~~o T.Do 795'.
rES 100-804
BHC, 100-794
Attempted 16 sidewall cores, recovered 13, no shows.
10/30-11/4 'Set 20" ~.
Reamed 17-1/2" hole to 26". Ran 19 jts., 791', 20", 9411, 'H··40 csg. @ 790' ,
cemented w/1200 sx, class "G"" 2% GaC12, 'cement circu1ated~ Tested csg. to
100011. Test Hyaril to 1000#. .
, .
11/Lp·-ll/6
11/6"'11/7
11/7-11/11
Drilled l2-l/L~" hole 795' to '2520' eo
RFCf.\VFD
J ~\N 4: ' 19"7\
OIL AND GAS
DiViSiON Or ,
At-oICHORAGI
Ran Sch1umberger logs. T.D. 25201.
rES, 80l}-2519
BHC-GR 794-2494
lIDT 786-2511"
Attempted 29 sidewalls, recovered 29, no shows.
Set 13-3/8" _~.
Ream 12-1/4" hole to 17...1/2". Set 61 jts., 13-3/8", .I-55 csg. @ 25150 D.Vg tool @
1393. Cemented w/743 sx, class "G", through shoe. Opened D(JVo tool and circulated
hole (circulated out approximately 3 sx), and cemented w/1480 sx, class "G" + 2%
CaC12 through ~oVo tool. Cemen~ circulated, good re~urns at surfac~. Nippled up.
Pressure test BoO.P. w/3000#, test csg. w/1500#. Dr1l1 out cement and shoe.
'"
(~(~;
'- ?.¡ I
~ í\ 'N' / ,iiO'r
,Jh\" .} !,). \
DIVISION Or Oil AND GAS
ANCHORAGI
R t (' t , V t: D
. '
CONFIDE·NTIAL.·
h
Tn@. ¡J(u...... W""'> fÒf"\.~+ù(l 11,.... ~q~.JI,i "6>Sf- (tI,~/
surface pipeo
p. & A well.
Set 90 sx-cement plug 4875-5000'.
Set 133 sx cement plug 2910-3100'0
Set 100 sx cement plug 2435-2565' bottom
Set 15 sx cement plug at surface.
Capped with a steel' plate.
Release rig at noon 12/6/700
Ran Sch1umberger logs. T.D. ·S'o15'.
IES 2511.- S013
BHC-GR 2512-S006
lIDT 2509- S020
SNP 2514-8013
Attempted 29 sidewa11s~ recovered 24, no shows.
Drill 12=1/4" hole 2520' to SOlS' 0
Stuck pipe at 7073, recovered all pipeo
-:--_--~--_._-_.~-----------_._--~-------------------------'-
-_._--~-_._~~~----~~._------------->-~_._-_.._------_._-.__...._.._----.._..._-_._~._--:-----
/-\
/~
-----~--------
HISTORY OF OIl. OR GAS . HELL
. ':J?AGE 2
12/5-12/6
12/3-12/5
11/11- 12/3
DATE
--
~"
.,
""...",
/<\
\ ,-)'
SUBMIT IN DUPLICA'TE·
ST ATE OF ALASKA
OIL AND GAS CONSERVATION COMMITTEE
(S('(' other In-
st ruct ions on
reve¡'se side)
5. API NUMERICAL CODE
b. TYPE OF COMPLETION:
NEW D WOnK D
WELL OYER
)2. NAM~ OF OPERATOR
D
6. LEASE DESIGNATION AND SERIAL NO.
W~~~^,_ǺM.ek~TIQ~ ,Q~.B~ÇQMPL,.~IIQ~.; ggepRT A~ND LOG *
TYPE 011. D GAS D V'VI
WELL WELL DRY ~ Other
ont. #14-20-0300-1362
7. IF INDIAN, ALLOTI'EE OR TRIBE NAME
DEEP-
EN
PLUG D
DACK
IHFF, D'-
, f.f;SVR.
~,~þ i 19!.1Çprp OJ:." ª t,io1:J"..
~. ÁnDRESS OF OPERAToa
'P. O. Pouch 7- 003 Anchorage, Alaska
LOCATION OF WELL (Report location clearly and in accordance with anJl State r~quirem6nt8)·
At surface 1200' FSL, 2390' FEL, Sec. :}6,T12N" R12W,B.M.
Wildcat
11. SEC., T., R., M., (BOTTOM HOLE
OBJECTIVE)
At top prod. Interval reported below
At total depth
Same
CONF\OEN~\\l
ec. 36, T12N, R12W, S.M.
12. PERMIT NO.
70-53
16. ELEvATIONS (DF, RKB, RT, GR,!:rC)· 17. ELEv. CASINGHEAD
499 K.B. (Ref.)
479
. IF MULTEPLE COl\$PL.,
HOW MANY·
JNTERV ALSDRILLED BY
CABLE TOOLS
Ö
22.¡PRODUCING INTERVAL(S), OF THis COMPLETIOiN-TOiP,
None
23. WAS DIRECTIONAL
SURVEY MADE
No
24.1 TYPE ELECTRlC AND OTHER I;.OGS·¡tUN
¡rES, Sonic, SNP, D~pmèter
25.
-,
CASING RECORD (Report all strings set in wdl)
" .
CASING SIZE WEIGHT; LB/F'Ì'. GRADE DEPTH SET, (MD) HOLE sIZE CEl\1LNTING RECORD AMOUNT PULLED
30" l54l¡' " 1 102 48" -c; 260
ne pip sx. None .
20" 94# H-40 790 26" 1200 sx Non'e
, 1 i-1/ R " (;1#' .1-1)1) 21)11) 17-1/2" '. 2221 ~x N' nnp
( ; "
,
~6. LINER RECORD < 27. TUBING RECORD ,
, SIZE TOP (MD)' , ,BOTTOM (MD) SACKS CEMENT* SCREEN (MD) SIZE . DEPTH ~ (MD) PACKER SET (MD)
: , ,
, ! ,
.
: .
. ..
28J PERFORATIONS OP~N TO PRODUC nON <Interval. size and number) 29. .... ACID" SHOT, FRAC"I'URE. CEMENT SQUEEZE, ETC.
DEPTI.¡~n."TERVAL (MD) . I AL'VrOUNT AND KIND OF MATERlAL usED
"
None
.
.
, .
32. LIST OF ATTACHMENTS
Mud Log, rES log, '.. Well History
33. I hereby certify that the foreg~iílg and attached Information 18 complete and correct as determined from all· available records
PRODUCTION
DATE FIRST PRODUCTION
WELL STATUS (Producing or
f;!1ut-in)
DATE OF TEST,
PROD'N FOR O~BEL.
TES'r PERIOD
--..
GAS-MCF.
GAS-OIL RATIO'
FLOW TUBING CALCULATED O~BBL.
PRESS, 24-HOUR RATE ;
).
31. DISPOSITION OF GAS (Sold, "-,ed tor uel, 'Vented, etc.)
GAS-MCF.
...........
TITLE Division Geologist
DATE
12/30/70
* (See Instructions and Spaces for Additional Data on Reverse Side)
INS TRUCTIONS
General: This form is designed for submitting a complete and correct well completion report and log on
all,types of lands and leases in Alaska.
Item: 16: Indicate which elevation is useq as reference (where not otherwise shown) for depth measure-
ments given in ether spaces on this form and in any attachments.
Items 20, .nd 22:: If this well is completed for separate production from more than one interval zone
(multiple completion). so state in item 20, and in item 22 show the pr c.:Jucing interval, Of¡ intervals,
topes), bottom(s) and name (s) (if any)- for only the interval reported in item 30. Submit a separate report
(pag,e). on this form, adequately identified, for ea'ch. additional intel val to be s~perate',ly produced, show-
ing the additional data pertinent to s(,ch interval.
.iem26: "Sacks Cement": Attacheds'úpplemental records for this well. should show the details of any mul-
; tipl~ stage cementing and the 'locaHon' of the cementing tool. '
.': Item 28:,Submif a separate completion report on this form for each J intetval to be separately produced.
(See instruction for items 20 and 22 above);'
-'~-'~'''''''"':J4. .!?PMMARY OF FORMATION TESTS INCLUDlN,G INTERVAL TESTED, P~URE DATA AND RECOVERIES OF OIL, GAS,
: '..1. ~
" ~. .'
i..I;
35. GEOLOGIC' MARKERS
NAME
MEAS, DEPnt U1: VERT, DEP111
U.. Kenai 270
. M. Kenai 3142
"
,''¡
~....,.'~
..^
J.
DESCRIPITIONS OF LITHOLOG;V. .PO~OSITY; FRACTURES,· APPARENT DIPS
AND :.DETECTED SHOWS OF OIL, G~ OR WATER.,
~
i
. I,
:',;\
:.~!
:.J
'.. ¡
,I''r...;
;jí :::j
?:.; 'i;)J
,;,'~~
,/
Form.P~3
REV .9-36-67
/~
Submit "mtentions" in Triplicate
& "Subsequent Reports" in Duplicate
.........
99501
I DIR.~
-c-GEÓL-
I c. ENG "¡-
-~1' ENG--~
6. LÈASE DESIGNATION AND SERIAL NO. -L~: '-ENG~
Cont 1114-20-0300-1362 ~__~ ENG I
4 ENG I
7. IF INDIAN, ALLOTTEE OR TRIBE N 5 ENG I
Native Village of Tyo ,.
, GEOl I ~
-'-2 GEOLIL
----- EOLL
-¡REV':a(T'
----'AFT-I--
'S€<c:-T"
FILE:, .1.+
5. API NUMERICAL CODE
50-283-20035
5T ATE: ()f AlASKA
OIL AND GAS CONSERVATION; COAi\MITfEE
SUNDRY NOTICES AND REPORTS ON WILU
(Do not use this form for proposals to drill or to deepen or plug back to a diffierent reservof:r,
Use "APPLICATION FOR PERMIT-"for such proposals.)
1.
Wildcat
OIL 0 GAS 0
WELL WELL OTHJOR
2, NAME OF OPERATOR
Mobil Oil Corporation
8. UNIT FARM OR LEASE NAME
Wést Moquawkie
3, ADDRESS OF OPERATOR
P.O. Pouch 7-003, Anchorage, AI<
9, WELL NO.
No. 1
4. LOCATION' Û'F WELL
10. FIELD AND POOL, OR WILDCAT
13. ELEVATIONS (Show whether DF, RT, GR,etc.
499' kb
. . I
Check Appropriate lox To lindi'C81e Nature of N~tice, Røport, or Other 'Data
Wildcat
11. S c., T., R., M., (BOTTOM HOLE
OBJJï;CTIVE)
At surface
1200' FSL and 2390' FEL, Sec. 36, T 12 N,
R 12 W, S.M.
S.M
14.
NOTICII OB'INTIINTION TO :
IUB811QUIINT RIIPoaT 01':
PULL OR ALTER C.ASI~G ~ WATIIR SHUT-or!' § OmlRlNO WOLL II
MULTIJ;'LE COMJ;'J.ETE B'RACTURII TRIIATKIINT ALTERING CASING
ABANDON- = SHOOTING OR ACIDIZING - ABASDONMIDNT- X
CHANGE J;'LA~Ø (Other)
- (NOTE: Report results of mUltiple completion on Well
Completion or Recompletion Report and Log form.)
15, D¡';SCRIBE PROPOSED OR CO~{J;'LETED OPERATIO~S (Clearly state all pertinent details, and give pertinent dates. Including estimated date of starting an;r
proposed work. . , . '
TEST WAT_ERSHUT-OB'J' §.
FRACTURE TREAT
SHOOT OR ACIDIzm
REPAIR wmLL
( Other)
In accordance with the previous Notice of Intention to. Abandon, the following
abandonment work has been completed.
12-5-70 With open end drill pipe at 5000', displaced a 90 sack class G cement plug.
Calculated top of plug at 4875'. (125 linear féet).
Pulled up to 3100' and displaced a 133 sack class "G" cement plug.
Calculated top of plug at 2910'. (185 linear feet).
12-6-70 With open end drill pipe at 2565' displaced a 100 sack class "G" cement plug.
Calculated top of plug at 2435' (120 linear feet). Note: Heavy drilling fluid
(10.5 #/gal.) was left below all cement plugs.
Removed well head and spotted a 15 sack class "G" cement plug at the
surface and capped with a steel plate. An abandomne,nt marker will be erected and the
location cleaned up after rig demobilization is 'complete. The U.<S .G.S. office will be
notifiedcafter location clean up is completed to arrange for fi'I\avrrtif\7 f D
OLe l,i
("~.
u
DIVISION Of OIL AND GAS
SIGNED
TITLE Division Engineer
DATE
12-7-70
APPROVED BY
CONDITIONS OF APPROVAL, IF ANY :
TITLE
DATE
CONFIDE TI t
See 1n,structions On Reverse Side
Approved Copy
Returned
CONFIDENTIAL
P'orm P-3
REV. .9-300067
~".~
C (-1. ~ I r m Ie, V ,. ~,B T·· I It l
"'ub. .mit ......tentioru¡" in TriPlicate"....··... ::'~'. '..~ i;.~.. ~.': r.,...~.·. .' ~i [f::'-J ;.'.~.';: (~ ~.' \ .Ira
'" ..,u .ØIII(;... ~.\:! ~ ~ ~ ~.' ..' /,w ' ~1t1.' ti. . ~~ ,!
& "Subsequent RePorts" in Duplicate . .. . II Á2 Y ¡j ~ iD -¡
STATE OF ALASKA
OIL AND GAS CONSERVATION ÇOMMITTEE
5. API NUMERICAL CODE
50-283-20035
6. :J;.EASE DESIGNATION AND SERIAL NO.
SUN'DRY NOTICIS AND REPORTS ON WELU
(Do not use this form for prO'posals to drill or to deepen or plug back to a diffierent reservoir.
Use "APPLICATION FOR PERl\a:IT-" fø.r such proposals.)
Cont. #14-20-0300-1362
¿'
1.
7. IF INDIAN, ALLOTTEE OR TRIBE N
Nati.ve V; lla.ge of Tyon
8. UNIT, FARM OR LEASE NAME
West Mo ua.wkie
9. WELL NO.
~~LL 0 ;:ESLL D OTH.ER Wildcat
2. NAME OF OPEEATOR
Mobtl 0;1 Corporation
3. ADD-RESSOF OPERATOR
P.O Pouch 7-003 Anchora.ge AK
4. LOCATION. OF WELL
At surface 1200' FSL and 2390' FEL
Sec 36 T 12 N. R 12 W. S,M.
99501
No
10. FIELD AND POOL. OR WILDCAT
Wildcat
11, SEC.. T.. R., M., (BOTTOM HOLE
OBJECTIVE)
Sec. 36. T 12 N, R 12
5
13.ELEVATION5 (Show whether DF, RT, GR, etc.
\"
-.' ~ ;3W;
-- [~''''J
'L
NO.
'\ r. ., I ." - I
I)' :\- ! .
499' kb
70-53
Check Appropriate ·Box Tol¡nejicate Nlat'ure of NOtice, Report, or . Other Data
sr~c
14.
cONFL-.
FíLE:--'
.J
NOTICBI OB' INTIINTJON TO:
I!IUBUQUIINT RIIPOB'l' 01':
PULL O' 'LT" CAe,"G ~x'" WATBlR SHUT-OF)' § ,"'IBINOW"LL II
M ULTIPLBI COMPLETE lI'RACTURII" TRIIATKIINT ALTERING CASING
....NGGN. eROGT,.G OR ,'CIDIZING - ....DGN M"T'
CR'.G" PU", (Oth,,) =
(NOTE.' : Report· resu...1tB of multiple completion on Well
( Other) Completion or Recompletion Report and Log form.)
15. D¡':SCRIBE l'ROPOSED OR CO~tPLETED OPERATIOXS (Cleurly state ull pertinent details, and giv'é pertinent dates. including' estimated dat~ of starting an~'
proposed work.
It -fs DroDosed to abandon this well at a total denth of BOIS' because of the absence of
significartt hydrocarbon bearing sands and due to the structural position of this well at
total depth, no productive sands could be expected by deeper penetration.
In accordance with verbal approval obtained on 12-4-70, the following abandonment procedure
will be followed:
1. Place a 100' cement plug in the 12-1/4" hole from 5000' to 4900'.
2. Place a ISO' cement plug in the 12-1/4" hole from 3100' to 2950'.
3. Place a 100' cement plug across the 13-3/8" casing shoe at 2515' from 2565' to 2465'.
4. Place a 10 sx cement plug in the 13-3/8" casing at èthe surface.
5. Cap the well with a steel plate and weld a 4" x 4' pipe marker to the plate with infor-
mation as required by Federal regulations.
6. Fill mud pits, level:. andolean-lueat:ion.
Ifote: Heavy drilling fluid will be left in the hole between cement plugs.
TEST W ATI!).ReRv~··1 .1
lI'RACTr:aE TREAT
SHOOT OR ACIDIZII _
REPAIR WELL
-_.~~~_._--
RECFiVfD
DEC 1 (ì 1970
DIVISION OF Oil. A~W GAS
ANCHORAG!
TITLE Division Engineer
DATE 12-7-70
APPROVED BY
CONDITfONB OF APPROVAL, IF ANY:
(?rI /'
¡jé41 7'
DATE
/2 ~//- 70
O f:\' r ~,
\- . ¡;.~ ~-
C.' ...'1 ~j;\~ ': ~>~ ~~ '
, J, ¡) ~''':¡1 f1
~ \. ", ¡ . Ij \;\'
'~\irJ <.i
P[fl
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j~ ~
f1 Ii
\
La
See 'nstructions On Reve"p.~d Copy C 0 ~..\ ~.' [ .~.".' ~.J.\. }.':. .r."!..'~.J ~.:'..;...".' T.'.. '. A / l
Returned i¡·. b r :.: !: ': >.¡ i:f n Ii]
/.2//// /;7ð b \¡ Q & V' ~ Ii \.J ÌJ iI I""
FonnNo.·P-4
REV. 9~30~S7
V Ul·'\I·IJ LJ 1...1.\1..t11:\ f;-,
!",r ...
STATE ç I AL^,A SUBMIT IN Dt."PLICA1'E
-
,.-...,
, , ;--Pi .\1ERICAL CODE
Oil AND GAS CONSERVATION COMMITTEE
50-2133-20035
6, LEASE DES:GNATIO;-': AXD SE!\lAL XO,
MON"{H!. Y REPOR1" Of DRn.lING
AND\VORKOVER OPERATiONS
~~LL 0 ~~6LL U
2.:-:~V.E OF.OPERATOR
Mobi1'Oi1 Corporation
3, ADDRESS OF OPERATOR
OTHER
Wildcat
Cont. #14-20-0300-1362
i. IF INDIA}J'. ALOTTEE OR TRlBE NAME
Native Village of Tyonek
8. L"XIT,FAm.t OR LEASE NAME
West Moquawkie
9, ''v' ELL XO.
1.
Po·Oo Pouch 7-003
4, LOCATIO=-: OF WELL
,Anchorage. Alaska
99501
1
10. FIELD A."-:D POOL. OR \\'ILDCA1'
1200' FSL, 2390'FEL, Sec. 36, T12N, R12W, S.Mo
Wildcat
11. SEC.. T.. R. ~1.. (BOITO:\1 HOLE
OBJECTIVE,)
Sec. 36, T12N, R12W, S.Mo
12, PERMIT XO,
70-53
13. RE?ORT TOTAL DEPTH AT ¡:'''-:D OF MO~TH. CHAXGES IN HOLE SIZE. CASIXG Al'G) CE:\1E.."-:TING JOBS INCLUmXG DEPTH
SET Al\~ VOLUl\TES USED. PERFORATIONS. TESTS A....."D RESULTS. FISHING JOBS. JUNK L"-; HOLE AND SIDE~TRACKED HOLE
'A..'~ A.-..;y qrrlER SIG:-:IFICA.'I¡'T CHANGES IN HO~ CONDITIONS.
ToDo at end November 7815'.
. Set 791' of 20", 9411, H-40 csg @ 790' in 26" hole' w/120Q sx class "G", 2% CaC12'
cement circulated.
Drilled 17-1/2" ~ole 795'-2520':
Set 61 jts. 13-3/8", 6111, J-55 csg @ 2515', cemented w/2223 sx class "G", 2%
cement circulateª.
. 5¡ud bate
~d~
~J/s?R..~ ç r tV.' f D
, r. \" \\._- L
8. 1970
~'\\~\,
f<{:)~
CP~
Drilled 12-1/4" hole 2520'-7815'.
Stuck pipe at 7073, recovered all pipe.
ON1S¡ON OF oa. AND GAS
ANCHORAG~
~
SIGÑLD
DAn::
12/7/70
1,",. 1 hereby
NOTE-Report on this form is required for each calendar month, regardless of the status of operations,' anØ muSt be filed in duplicatt
with the Division of M~es & Minerals by the 15th of the succeeding mo nth, unless otherwise directed.
~;,~
Fornl No, P-4
r~ .
CQ.f}I tpl ~TIAL SUB>1IT L'< DL?LICATE
...
"t- "
REV. 5-30-67 I .
5. API KU:VrERICAL CODE
OIL AND GAS CONSERVATION COMMITIEE 50-283-20035
6, LEASE DES:GNA TIO:-J A;-;D SERIAL :';0, -
lViONiHLY RE.PORY OF D;~H..UNG
- AND \VORKOVER OPERA TBONS , Cont. /114- 20- 0300- 362
-
1- i. IF INDIA», ALOTTEE OH TRll3E NAME
OIL 0 GAS rx1 Wildcat Native Village of Tyonek
wtLL WELL 01'H ER
2. NA.\1E OF OPE..~TOR 8. L"XIT,F.4JU.t OR LEASE NAME
Mob i 1 Oil Corporation West Moquawkie
3, ADDRESS OF OPERA TOR 9, WELL NO,
Po O. Pouch 7-003 Anchorage, AÌaska 99501 1
4. LOCATION OF WELL 10, FIELD A..'I;D POOL. OR WILDCAT
1200 ' FSL, 2390' FEL, Sec. 36, T12N, R12W, S.M. Wildcat
11. SEC,. T" R, M" (BOITO:\1 HOLE
OBJECTIVE;)
Sec. 36, T12N, Rl2W, S.M.
12. PERMIT NO,
70-53
13, REPORT TOTAL DEPT:-iAT E.~D OF MOXTH, CHA.~G:ES I~ HOLE SIZE, CASING A......"D CE:\¡¡;:,.~TI:'\G JOBS INCLt:DING DEPTH
SET A....."D VOLu-:>'ŒS USED. PERFORATIO~S, TESTSA......"D RESULTS, FISHING JOBS, JUNK L~ HOLE AND SIDE·TRACKED HOLE
A....."D A.~Y OTHER SIG~IFICA.."T CliA!''¡'GES IN HO~ COI'-"DITIONS.
'",
I D.lR/
~~GEO~,
¡-C: ENG
-'--1. ENG]
¡-2'-ENG _~
-,-j'-ENG
--1''--4 ENG
--"--5 ENG 1
--1' 1 GEOl I í
-'~'-I"Z ?fOl I'_~
-:r3 GEOL L_,
-~"_-_REV,__L
I DRAFT., I _
----:r-S~G T
'CONFÈR-;--
'-
FILE:
Drove 30" to 102' and cemented w/230 sx.
Drilled 17-1/2" hole to 795'.
.
CONFIDENTIAL
Ref"'"
'l\.E!VFD
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u
DIYLS;~'~;?:~ <, __
....! '(,.J,iAGM
GAS
TITLE Division Geologist
DA "I1:
11/5/70
'OTE.-Report on this, form is required for each calendar month, regardless of t.he status of operations, and must be filed in duplicate
t.he Division of Mines & Minerals by the 15th of the succeeding mo nth, unless otherwise direct.ed.
~
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KEITH H. MIllER, GOVERN
DEPAI.TMENT o.~ .~ISH & GAMt~
I
I
í
/
t~r. JohnH. Marshall
Mobil QilCorporation
P.O. Pouch 7003
Anchor,ager Alaska,
Dea r Sir:
ANCHORAGE 99502
October 15, 1970
Re: West Moquawkie No. J
Mobil Oil Corporation
Operator:
The Alaska Department of Fish and Game has received notice of your intent
to drill in Section 36, Township 12 North, Range 12 West, S.M. As Tyonek
Creek, an anadromous fish stream, lies within this section we need to
know the shortest distance from this stream to your dri 11 pad.
Thank you.
cc:
Denton
Burrell
/
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Ro~nhOld
Habitat ~;~9ist
ADF&G
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fd__ 1.jltrDJIll'l11r~. ~ em'" ·CU-'1cat ~...".
of_. ".t.'~1 ............ 1811 hC....s..a1.ü.... .....
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...... .I..d. .... ....... ....., f11e4 ..._t to AI 31.Ø5.83Ð
... 11M "¡'n~tle .....1_1·. ·......-.1... tIte· ca1Død._ f1le
.. ...... ..1'--1_1__,..1'1..01 d11ea&--. Mtb .f..
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~ ___I ...u......IeC.... ... ._"tie- h eM ....-..
a....._ lie ."":lftll. .. .....,.~.dth _ñ_2161 if- ..
..u....letl... .....
....... Sa tile 4».'....1'....... fUllitC. dd.1J. dta .......
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..... Ii. SJ Ii TI'" 121.. .... UW.I."
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Oct.er 9. 1970
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Mobil Oil Corporation
p. O. Pouch 7-003
Anchorage, Alaska
September 29, 1970
1 DIR 1 ..'
9950 -Tc C:OL 1~
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FILE:
State of Alaska
Dept. of Natural Resources
Division of Oil & Gas
Anchorage, Alaska 99501
COOK INLET BASIN - 775
APPLICATION FOR PERMIT TO DRILL
MOBIL 1F1 WEST MOQUAWKIE
Sec. 36, T12N, R12W, S.M.
Gentlemen:
Enclosed herewith in triplicate is an Application for Permit to Drill
the Mobil 1F1 West Moquawkie, Sec. 36, T12N, R12W, S.M., Cook Inlet Basin,
Alaska, and Mobil's check in the amount of $100.00 for the filing fee.
The well is programmed as a 10,000 foot Tertiary Middle Ground Shoal and
Hemlock test; however, it is anticipated that gas will be encountered in
the same sands as found productive in the Mobil #1 Moquawkie well. In
the event production is not found in the deeper objectives, operator
may desire to plug back and complete as a Moquawkie Gas Field well.
Very truly yours,
~~~~"~~
~~:ì Division Geologist
JHM:c1h
~. "_H~._..~.....~",.~~
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:' .t:'/ ~ c::: !tr .i¡;;;:¡ ) $j
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REV, 9-30-8'/
SUBMIT IN TRIPlE.
(Other instructions to,
reverse side) "
STATE OF ALASKA
API 50-283-20035
Ii.
Oil AND GAS CONSERVATION COMMITTEE
APPLICA TION . FOR PERMIT TO DRILL, DEEPEN, OR PLUG BACK 6. LEASE DESIGNATION AND SERIAL NO.
la, TYPI: 01' .0aK Cont. #14-20-0300-1362
DRILL KJ DEEPEN D PLUG BACK D . IF INDIAN, ALLoTTEE OR TRIBE NAME
b. TYPI: OJ' WIILL Native Village of Tyone
OIL KJ GAS KJ SINGLII D Mt:LTIPI.E 0 8, UNIT,FARM OR LEASE NAME
WELl. WELL OTBIIR ZONE ZONE
2. NAME OF OPERATOR West Moquawkie
Mobil Oil Corporation 9, WELL NO.
3, ADDRESS Of' OPERATOR No. 1
P. O. Pouch 7-003 Anchorage, Alaska 99501 10, FIELD AND POOL. OR WILDCAT
4, LOCATION OF WELL Wildcat
At surface FSL 12001 , FEL 2390 1 , Sec. 36, T12N, R12W, S.M. 11. SEC,. T" R., M" (BOTTOM
HOLE OBJECTIVE)
A t proposed prod. zone
Same Sec. 36. T12N. R12W. S.
13, DISTANCE IN MILES AND DIRECT,ON LtOM NEAREST TOWN OR POST OFFICE* 12.
Six miles N.W. of Tyonek Village
.'
k
M.
14. BOND INFORMATION,
(See Reverse Side)
Amount 10 000.00
17. NO, ACRES ASSIGNED
TO THiS WELL
TYPE Oil & Gas Surety and/or No,
15, DISTANCE FROM PROPOSED-
LOCATION '1'0 NEAREST
PROPERTY OR LEASE LINE, FT, 1200'
(AlSO to nearest drìg, unit, if any)
18, DISTANCE FROM PROPOSED LOCATION-
TO NEAREST WELL DaILLING, COMPLETED.
OR APPLIED FOR. FT, No previous wells on
lease.
21. ELEVATIONS (Show whether DF, RT, GR, etc,)
640
19. PROPOSED DEPTH
10,000
20, ROTARY OR CABLE TOOLS
Rotary
22, APPROX, DATE WORK WILL START"
Est. 450't'
23.
PROPOSED CASING AND CEMENTING ROGRAM
o
SIZE OF HOLE SIZE OF CASING WEIGHT PElt FOOT GRADE
S1ttTING DEPTH
Q!:.\NTITY OJ' CE~I:N-::
"
"
40
---
24" 20"
17 - 1 2" 13- 3 8 "
12-1 4" 9- 5 8"
8-1/2" 7" liner
BOP Equi~ment:
A. 20" casing point to 13-3/8" casing point.
1. Hydril "MSP" series 600 - 2000 psi W.O.G. 20-3/4" nominal.
13-3/8" casing point to 9-5/8" casing pø.int.
1. Hydril "GK" 12" series 900 - 3000 psi W.O.G.
2. Shaffer Double Gate 12'1 series 900 - 3000 f)si W.O.G. complete with 4-1/2" DP,
7" casing and blind rams.
9-5/8" casing point to TD.
.l. 10" series 1500, bag type preventer, 5000 psi W.O.G.
2_ 10" series 1500, double gate ram type preventer, 5000 psi W.O.G.
950
2300
2 00
300
Sacks
Sacks
acks
Sacks
C? ; 'I" Co .
'rC '
\ ,;c. ~
p//1 z(,oo'
B.
C.
IN ABOVE SPACE DESCRIBE PROPOSED PR<XJ.RAM: If proposal 1& to deepen or pIUC back, give data on present productive zone and
propoøed new productive zone. If proposal is to drill or deepen direet:.onally,. give pertinent data ?n subsurface ],ocatlons andmeasureci and
true vertical depths. Give blowout preventer program, r· --. .", e ,
24, I
DATE
9/27/70
t'
~ Alaska DiVa Geologist
CONDITIONS OF APPROVAL, IF ANY:
OTHER REQUIREMENTS:
-.¡ ß .~ '-;>.,
j'---~ iI 1
,.~
C)
~ t, -&
o YES )8....NO SO - 2 g 3 - z.oo3 $''' fjj;::: ~
~ Jo ~ 7:t:Ói t] C'\l ~
Pl:RMITNO -~. APPBOVALDAn: /1- - 'i-,V:.~ l
ApPROYmBV t? L _.4 _ 'Q _ Tm& JJ,i~rechrv,~,OItr&r;i'4 4·-7õ
~~structiOft' On Rev fl. Sid. ~./ /;:, \
~,¿ ....'-
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........~
..... -
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,
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:.....
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. Nationwide Indian Bonu #8027-31-97
$75,000
Federal Insurance Company
INSTRUCTIONS
General A filing fee of $50.00 must accompany application for permit
to drill, to deepen or to plug back. Checks shall be made out to State of
Alaska Department of Revenue.
This form is designed for submitting proposals to perform certain well
operations, as indicated, on all types of lands and leases for appropriate
action by the State agency, pursuant to applicable State laws' and regulations.
Any 'necessary special instíUctions concerning the use of this form either are
shown below or may be obtained from the Petroleum Branch, Division of
Mines and Minerals.
Item 1: Use this form, with a'ppropriate notations, if the proposal is to
redrilf to the same reservoir at a different subsurface location or redrill to
a new reservoir
L
Item 13: Attach hereto a neat, accurate plat or map, drawn to scale,
showing the site or proposed site for this location, distances from section
line, lease line if any, and oth~r information that is Pertinent. Refer. to
Section 2051 of Oil and Gas Regulations.
Item 14: Enclose drilling bond on Form P-2 with this application for
permit to drill, to deepen, orro 'plug back unless' covered by other suitable
bond.
Item 15 and 18: If well is to be, or has been directionally drilled, use
subsurface location of hole in any present or objective productive zone.
'3::. ..
n
(,
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r- - -- - ï -- - - --.-- -- --,- --- --- ï--- - --T-------i
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~------~---~--~------,-------~------~------i
I I I I I I
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II 19 I. 20 21 '22! 23 ! 24 '1.7: 12 N.
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I I .. I I I I
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. 30 I 29 28 I 27 I 26 I 25 I
I: I' WEST MOQUAWKIE No. I
LAT. 61004125.70" I
~ ------J-- - ----t--- -- - -~- _____~.J:.ON<L.~I~I~ Q5.:l3" ----1
I I I I Y : 2,586,779
I : I I I X - 266,554 I
I 31 I 32 I 33 I 34 I 35 I 36
I I I I
I I I I I 2390'
I··· I I I I I-~
_+-__-L__--L___..L-__-1-__--L_~__I_--
I SCALE: ." = I MILE I
1
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18
CERTIFICATE OF SURVEYOR
s~V' ~o-"o
Dare
~J~ e..~-.:....
SURVEYOR
-.~"'\~~
...~~ OF At. ~~
~~ .......~.. 4~ u
IJfif. ~'r.... ~; ....'f- a
III ~ .',;:!" I. "9 \fð
1* 149m:""\' \ 1f!
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f.<A·..~/S~~~··^~~
&~~'/)... e.\'.- co:"'<"'4V
"'b....."'" SUR"~~~
~"~~q¡.tIb'
I hereby certify that I am properly registered and
licensed to practice land surveying in the State of Alaska and
that this plat represents a location survey made by me or
under my supervision, and that all dimensions and other
details are correct.
WEST MOaUAWK'E No. I
Located In
SE 1/4 of Protrocted Sec,36 1:12 N, R.12W. SEWARD MER,~SKA~
Surveyed for
MOBIL OIL CORP.
_~,~. -:0.
Surveyed by
E M. LINDSEY a ASSOC.
LAND a HYDROGRAPHIC SURVEYO'RS
2502 West Northern lights Boulevard Box 4 -08/
AnChOrage~~;~Ë
Company
,..~~. Lease & Well No. 1tA5Þ J7/o,~tv3~hib'
CHECK LIST FOR NEW WELL PERMITS ?~f
Yes No Remarks
. . . .
. .
. .
. . . .
. . . .
Is well to be located in a defined pool.
Do statewide rules apply . . . .'. .
Is a registered survey plat attached
. . . . .
· . . .
Is well located proper distance from"property line
Is well located proper distance from other wells .
Is sufficient undedicated acreage available in this pool .
Is well to be deviated. . . . . . .
. . . .
· . . .
~..
." ',J ,
" .~'-
· . . .
· I'-Q,t.t)~.,
· .
Is operator the only affected party.
· . . .
. t;c/ll;!:t" ,___
. . . . .
Can permit be approved before ten-day wait
o. Does operator have a bond in force .
1.
2.
3. Will
4. Will
5. Will
6. Will
7. Will
· . . .
--
. . . . . . .
· . Æ:~~,,~t-:?4'~ _
· · · · .ift!
. //f)
cement tie in surface and intermediate or production strings ... ~7d
.At~
-.
1//1/
· · · I:l.:-
Is conductor string provided .' . .
. . . . .
. . .
Is enough cement used to circulate on conductor and surface
cement cover a11 possible productive horizons
surface casing cover all fresh water zones ..
surface csg. internal burst equal .5 psi/ft. to next string
all casing give adequate safety in collapse and tension.
8. Does BOPE have sufficient pressure rating
. . . . . .
?
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if;~tot.# .,...,
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NOTICE
The following well logs and oversized
documents have been placed in offsite
storage. If you would like to view the
original documents, please contact the
AOGCC librarian.
AOGCc
3/4/2005
4+
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COMPANV-...!1n b;!
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WELL 1.Je.5-t Mð1~1~TtAl
FIELD Wit C tl
COUNTY ~naL' STATE 4/a.s-ffd
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U ü: -';> U Sec.~{o Twp. IZ..I¥ Rge./2 u) ..511
r:~m~::~~~dl~::~ k' j L ,~O Fl. Ab:':.v·¿fZ~lum Elev.: ~'.~: ~~~.
Drilling Measured From .If- .B '. G.L. Lf 71
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,
Ow OW 0 Sec. 36 Twp. 12N Rge. 12\,<] S)\'1 B .. ":'" :,.
UÜ:-'~ U "U'
.- I
(I) ....
GL 479 u I:
Permanent Datum: Elev. Elev.: K.B. 499 c. I····
f ;(1) '.
log Measured From KB 20 Ft. Above Perm. Datum D.F. 498 I~, .":' .,!'
f
Drilling Measured From KE G.l. 479 (I) :.
r..;' '. '.. :',.'
â) .,:". ;,"..
Date 8 c. 2 9"" ì 0 11- h- ;.' 0 12e, -70 0 '," '" .".
Run No. J::. . ..1.,:; '....'.
1 Two Threc Q)
.r..; ~
Depth-Driller 7S0 2520 801S 0 "
.-0
Depth-logger 805 2519 80lf, -,:¡.. ¡ ..
Btm. lOQ Interval 79!.t 249!.t 800f> c:
0 "
Top log Interval 100 794 2CJl2 "
l- ea.
Casing-Driller 30" @ 3 / tfid ... ¡Jª .'.....;.,'. i"
@ 100 3011 790 13 2 S lS @ c
Casing-loqqer 100 786 2S12 '. }''-., k E
II-! .-'1 C
Bit Size 17 1/2" 1? 1/4" 12 1/4 I....~ ' > '.', v:
I;~' .,......... 1/
Type Fluid in Hole fMC mud RDl 11 R D~ III .'" c
c
Fresh Gel 6"'/ Oìl ,,' I<e I ,...................... I C
Ie ..
Dens. T Vise. 1001 I 84 1102 I 62 10 e r.... r 4h ¡ i1J; ........... I "t
pH I Fluid loss 8 I 27 ml 8,,0 I 8.0 ml 10~1 ] 3 6ml I ml I~t "'t
iB -<I
Source of Sample Flowline F loív 1 í ne Flowli'iP . ..; '.
Rm @ Meos. Temp. 1003 @ 54 of 3086 @ 76 of 2_CJl (â' f>4 of @ of ..~.... i/;:% I Q
Rmf @ Meos. Temp. 7e/ @ 67 of !.to 22 @ 66 of 2 47 @ sc) of (tI of ...... ...~.. C
; , :J
Rm< @ Meos. Temp. 1007 @ 65 of 4.47 @ r: of 2CJ') @ S1 of (ri' of . en , ...
uu .
Source: Rmf R m< >1 ¡ M M I M ;1 T M I ...... N 1
.!X
Rm (@ BHT 1002 @ 56 of 1086 @ 106°F 1037 @ 139 of @ of ....·..·ii .~
Time Since Circ. 1 Bro 8 Hours 16 Hrso '..' c
Max. Rec. Temp. of of 139 of of t (,/) ..
56 106 ' ::.:=. .
;!~. ..~ G
Equip. I location· 342 I 4612 C-342 ! Anc~ 342 ¡ AK ! c
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Recorded By Bvd CII Redd ReddjChaffev 'r ~ c
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Witnessed By /'..lovqnnor ~ 1 px;::¡ndpr/Wnnn' 1,7:1,'r1 Woodward .. 0:: ~
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FIELD
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STATE .Al·'1ska
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Permanent Datum: CL
log Measured From 1< ß
Drilling Measured From KG
, Elev. 479 ,.
Ft. Above Perm. Datum
Elev.: K.B.
D.F.
G.l.
!+99
498
4ì9
20
8·,29-70
1
750
805
11-{J-70
Two
2520
2519
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794
30'¡ @ 790
786
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HDl 11
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100
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8 Hours
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