HomeMy WebLinkAboutItem M February 14, 2000
STAFF REPORT
To: Mayor Yost and Members of the City Council
Attention: Keith R. Till, City Manager
From: Lee Whittenberg, Director of Development Services
Subject: APPROVAL OF COMMENT LETTER TO
COASTAL COMMISSION - DECOMIVIISSIONING
OF BELMONT ISLAND
SUMMARY OF REQUEST
Authorize Mayor to sign comment letter with any amendments determined appropriate. Receive
and File Staff Report. Instruct staff to forward to Planning Commission and Environmental Quality
Control Board for information purposes.
DISCUSSION
The decommissioning of Belmont Island has been proceeding through the permitting process. In
June 1999, staff provided a status memorandum to the City Council regarding the proposed
Mitigated Negative Declaration ("MND") prepared by the State Lands Commission and the
proposed Permit Waiver by the California Coastal Commission. In December, 1999, the State
Lands Commission approved the MND for the Belmont Island Decommissioning Project and the
Decommissioning Project itself, which includes transfer of the rock rip-rap to the Bolsa Chica
Artificial Reef ("BCAR"). The Coastal Commission is scheduled to consider Permit Number E-
99-01 (pertaining to the Belmont Island decommissioning) at it's February 15, 2000 meeting in San
Diego.
Staff has reviewed the Coastal Commission staff report and is in general agreement with the
conditions recommended by Coastal Commission staff. It is the recommendation of staff that the
City request imposition by the Coastal Commission of a "continuing responsibility" clause relative
to any unanticipated soil or groundwater contamination discovered in the future along the length of
the abandoned-in-place, on-shore, electrical power cable and pipelines that served Belmont Island
from the oil separation facility at 101 Marina Drive.
Agenda Item ri
C:\My Documents\Coastal Commission\Belmont Island Deconunissioning.CC SR.doc\LW\02-10-00
Belmont Island Decommissioning Project-Permit No. E-99-01
Comment Letter re: Coastal Commission Consideration
City Council Staff Report
February 14, 2000
Overview of Proposed Project:
The proposed project consists of decommissioning and removing Belmont Island, located
approximately 8,100 feet offshore of the City. Belmont Island is a non-operating oil and gas
production facility, and the requested decommissioning includes abandoning in place the following
facilities that Are on-shore in the City of Seal Beach:
❑ one 2-inch diameter submarine electrical power cable;
o two 3-inch diameter steel pipelines formerly used to ship produced gas to the onshore
terminal;
O one 8-inch diameter steel pipeline formerly used to ship produced oil to the onshore
terminal; and
o one 3-inch diameter steel pipeline formerly used to ship fresh water from the onshore
terminal to Belmont Island.
The proposed project is to dismantle Belmont Island and remove the following components:
❑ all existing above and below-surface structures, including:
o approximately 392 cubic yards of hydrocarbon-impacted sand and rock fill in the
caisson core;
o 70 well conductors;
o 106 untreated wood piles; and
o 15,724 cubic yards of rock rip-rap surrounding the caisson.
The quarried rock rip-rap around the caisson is proposed to be taken by barge to the Bolsa Chica
Artificial Reef (BCAR). These materials are estimated to weigh between 15,000-30,000 tons.
Augmentation of BCAR, to a limit of 120,000 tons of clean material, was approved by the Coastal
Commission in October, 1995.
Subsurface Power Cable and Pipelines
The electrical power cable will be disconnected from the onshore facility at 101 Marina Drive by
Southern California Edison. Offshore, the cable will be cut at the seafloor near the south tower of
Belmont Island, and trenched into the seafloor to a depth of approximately 5 feet below the natural
bottom. The oil pipeline and two gas pipelines will then be flushed with seawater to remove
hydrocarbon contamination; flushing will continue until tests show the level of hydrocarbons is 15
ppm or less. All wastewater generated during flushing will be disposed of at an appropriate
onshore facility. The 8-inch pipeline will then be filled with grout from the onshore property to a
point offshore where the line is approximately 15 feet below mean low lower water (MLLW);
wastewater generated during the grouting procedure will also be disposed of at an appropriate
Belmont Island Decommissioning.CC SR 2
Belmont Island Decommissioning Project -Permit No. E-99-01
Comment Letter re: Coastal Commission Consideration
City Council Staff Report
February 14, 2000
onshore facility. The final proposed disposition of the 4 pipeline terminations onshore is: the 8-
inch line will be plugged with cement, the three 3-inch lines will be welded closed, and all lines
will be buried beneath the surface.
Project Alternative - Conversion of Part of Island to an On-Site Artificial Reef
Prior to submitting a Belmont Island Decommissioning Plan to the California State Lands
Commission ("SLC"), the applicant participated in a number of pre-application meetings with staff
of the SLC, Coastal Commission, U.S. Army Corps of Engineers ("ACOE"), and the California
Department of Fish and Game ("CDFG") to discuss, among other issues, the option of converting
the rock rip-rap at the island to an on-site artificial reef. The applicant concluded, after consultation
with the staff of CDFG, U.S. Coast Guard and SLC, that an on-site reef option is not feasible or
the least environmentally damaging project alternative. The staff of CDFG, U.S. Coast Guard and
SLC agreed that the site is not a feasible site for an artificial reef.
On December 3, 1999, the SLC approved the Belmont Island Decommissioning Project that
includes transporting the rock rip-rap to the Bolsa Chica Artificial Reef. On December 6, 1999,
after the SLC had already approved the Decommissioning Plan, a group called Heal the Harbor,
Inc. sent letters to ExxonMobil, the SLC and Coastal Commission offering to assume the legal
ownership of, and the financial responsibility for, a Belmont Island artificial reef. It is opinion of
the Coastal Commission that Heal the Harbor, Inc. has not demonstrated control over the area
(e.g., a lease from the SLC) or adequate financial resources to assume legal liability for such a reef
structure. The Coastal Commission believes that an on-site Belmont Island reef is not a feasible
option or the environmentally preferable alternative.
Other Agency Approvals
The following agency approvals have been obtained or will be obtained prior to any
decommissioning activity taking place:
❑ the SLC adopted a Mitigated Negative Declaration ("MND") and approved the
Decommissioning Project on December 3, 1999
❑ On May 27, 1999, the ACOE determined that a permit would not be required under Section
404 of the Clean Water Act because the project does not involve fill of the waters of the
United States.
❑ On May 6, 1999, the Regional Water Quality Control Board, Santa Ana Regional office
("RWQCB") issued a conditional clearance letter for the project. On June 23, 1999, the
RWQCB stated they had no objection to a proposal to allow to fall to the ocean bottom
marine growth removed from the caisson walls and other below-water island structures.
❑ The South Coast Air Quality Management District ("SCAQMD") will review the proposed
project to determine if air quality permits are required, and if mitigation measures beyond
Belmont Island Decommissioning.CC SR 3
Belmont Island Decommissioning Project-Permit No. E-99-01
Comment Letter re: Coastal Commission Consideration
City Council Staff Report
February 14, 2000
those contained in the Mitigated Negative Declaration ("MND") are necessary to offset
project-related air quality impacts.
❑ The Coastal Commission's action on this application comprises the required federal
consistency agency review in accordance with the provisions of the Coastal Zone
Management Act and the California Coastal Management Program.
Again, staff has prepared a comment letter for City Council approval requesting imposition by the
Coastal Commission of a "continuing responsibility" clause relative to any unanticipated soil or
groundwater contamination discovered in the future along the length of the abandoned-in-place, on-
shore, electrical power cable and pipelines that served Belmont Island from the oil separation
facility at 101 Marina Drive (See Attachment 1).
A copy of the Coastal Commission Staff Report is provided as Attachment 2 for the information of
the City Council.
RECOMMENDATION
Authorize Mayor to sign comment letter with any amendments determined appropriate. Receive
and File Staff Report. Instruct staff to forward to Planning Commission and Environmental Quality
Control Board for information purposes.
NOTED AND APPROVED
,f) _
./2"2"--°
Whittenberg, Director Keith R. Till
Development Services Department City Manager
Attachments: (3)
Attachment 1: Draft City of Seal Beach Comment Letter re: "Application No. E-99-1 -
Belmont island Decommissioning Project"
Attachment 2: "Application No. E-99-1 - Belmont Island Decommissioning Project"
Coastal Commission Staff Report, dated January 27, 2000
Attachment 3: List of Acronyms
Belmont Island Decommissioning.CC SR 4
Belmont Island Decommissioning Project - Permit No. E-99-01
Comment Letter re: Coastal Commission Consideration
City Council Staff Report
February 14, 2000
ATTACHMENT 1
DRAFT CITY OF SEAL BEACH COMMENT
LETTER RE: "APPLICATION NO. E-99-1 -
BELMONT ISLAND DECOMMISSIONING
PROJECT'
Belmont Island Decommissioning.CC SR 5
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February 14, '2000
Sara Wan, Chairperson
California Coastal Commission
45 Fremont Street, Suite 2000
San Francisco, CA 94105-2219
Dear Chairperson Wan and Commissioners:
SUBJECT: Application No. E-99-01
Belmont Island, approximately 8,100 feet off-shore of Seal
Beach
The City Council of the City of Seal Beach has reviewed the Coastal Commission staff
report on the above referenced application and, provided one additional special
condition is imposed as requested below, supports the recommendations of the
Commission's staff regarding this project. As an initial comment, the City of Seal
Beach approves the decommissioning of Belmont Island provided it is undertaken in an
environmentally sensitive manner. In reviewing the report, the City finds no evidence
that all reasonable and appropriate measures will not be imposed by the various
reviewing and permitting agencies to ensure the decommissioning proceeds in the
manner most protective of ocean resources and of the on-shore environment of the City
of Seal Beach.
The City concurs with the recommendations of your staff as set forth in the "Special
Conditions", particularly conditions 3, 4, 5, and 7. However, the City requests
imposition of an additional special condition by the Coastal Commission of a "continuing
responsibility" clause relative to any unanticipated soil or groundwater contamination
discovered in the future along the length of the abandoned-in-place, on-shore, electrical
power cable and pipelines that served Belmont Island from the oil separation facility at 101
Marina Drive. Specifically, the City desires the imposition of a condition to make it very.
clear on the record that, if a soil or groundwater contamination problem attributable to the
subject facilities is encountered during any future excavation activities, then ExxonMobil
shall be responsible for completing proper remediation. With this addition, the City
supports the position of the Commission staff that leaving the existing power cable and
C:Vrly Documents1Coastal Commiaaim\Belmnni Island Decommissioning CC Comment Ituer.doc\L,M02-11-00
99%
City of Seal Beach Comment Letter re:
Coastal Development Permit No. E-99-01 (Belmont Island)
February 14, 20100
pipelines in place as part of the abandonme•,; process is the least environmentally
damaging alternative.
To expedite this matter for the Commission and ExxonMobil, the City requests the
following additional "Special Condition" be imposed by the Commission in approving
Permit Number E-99-01:
"9. On-Shore Abandoned In-Place Facilities. Continuing
Responsibility. If any of the facilities (i.e., four pipelines and one
electrical power cable) that have been allowed to be abandoned in
place under this permit are determined to be the source of any soil
or groundwater contamination in violation of federal or state law,
the executive director will schedule for the Commission's
consideration a remediation plan prepared by ExxonMobil, or its
successors or assigns, prepared in accordance with applicable
federal, state and local laws in effect at the time of the
.determination of contamination. Said remediation plan shall
affirmatively show how and indicate under what methods the
contamination levels shall be remediated to comply with the
appropriate provisions of law. Upon approval of the remediation
plan by the Commission, ExxonMobil (or its successor and assigns)
shall diligently remediate the contamination in accordance with the
plan"
Again, with the imposition of the above additional "Special Condition", the City
supports the approval of Permit Number E-99-01 as recommended by the
Commission's Staff.
If you have any questions regarding this letter and the information provided, Mr. Lee
Whittenberg, Director of Development Services, will be in attendance at the time this
matter is considered by the Commission, and will be most willing to provide additional
information or respond to questions from the Commission.
Sincerely,
Paul Yost, Mayor
City of Sea] Beach
Distribution:
Members of the Coastal Commission
Coastal Commission Staff
Belmont Island Decommiuioning.CC Comment Letter 2
99%
City of Seal Bearh Comment Letter re:
Coastal Development Permit No. E-99-01 (Belmont Island)
February 14, 2000
Seal Beach City Council Seal Beach Planning Commission
Seal Beach Environmental Quality Control Board
Director of Development Services
Belmont Wend Docomntiuionine.CC Comment Letter 3
99%
Belmont Island Decommissioning Project -Permit No. E-99-01
Comment Letter re: Coastal Commission Consideration
City Council Staff Report
February 14, 2000
February 14, 2000
Sara Wan, Chairperson
California Coastal Commission
45 Fremont Street, Suite 2000
San Francisco, CA 94105-2219
Dear Chairperson Wan and Commissioners:
oR
SUBJECT: Application No. E-99-01
Belmont Island, approximately 8,100 feet off-shore of Seal Beach
The City Council of the City of Seal Beach has reviewed the Coastal Commission staff report
on the above referenced application and, provided one additional special condition is imposed
as requested below, supports the recommendations of the Commission's staff regarding this
project. As an initial comment, the City of Seal Beach approves the decommissioning of
Belmont Island provided it is undertaken in an environmentally sensitive manner. In reviewing
the report, the City finds no evidence that all reasonable and appropriate measures will not be
imposed by the various reviewing and permitting agencies to ensure the decommissioning
proceeds in the manner most protective of ocean resources and of the on-shore environment of
the City of Seal Beach.
The City concurs with the recommendations of your staff as set forth in the "Special
Conditions", particularly conditions 3, 4, 5, and 7. However, the City requests imposition of
an additional special condition by the Coastal Commission of a "continuing responsibility" clause
relative to any unanticipated soil or groundwater contamination discovered in the future along the
length of the abandoned-in-place, on-shore, electrical power cable and pipelines that served
Belmont Island from the oil separation facility at 101 Marina Drive. Specifically, the City desires
the imposition of a condition to make it very clear on the record that, if a soil or groundwater
contamination problem attributable to the subject facilities is encountered during any future
excavation activities, then ExxonMobil shall be responsible for completing proper remediation.
With this addition, the City supports the position of the Commission staff that leaving the existing
Belmont Island Decommissioning.CC SR 6
Belmont Island Decommissioning Project -Permit No. E-99-01
Comment Letter re: Coastal Commission Consideration
City Council Staff Report
February 14, 2000
power cable and pipelines in place as part of the abandonment process is the least environmentally
damaging alternative.
To expedite this matter for the Commission and ExxonMobil, the City requests the following
additional "Special Condition" be imposed by the Commission in approving Permit Number E-99-
01:
"9. On-Shore Abandoned In-Place Facilities. Continuing Responsibility. If
any of the facilities (i.e., four pipelines and one electrical power cable) that
have been allowed to be abandoned in place under this permit are
determined to be the source of any soil or groundwater contamination in
violation of federal or state law, the executive director will schedule for the
Commission's consideration a remediation plan prepared by ExxonMobil, or
its successors or assigns, prepared in accordance with applicable federal,
state and local laws in effect at the time of the determination of
contamination. Said remediation plan shall affirmatively show how and
indicate under what methods the contamination levels shall be remediated to
comply with the appropriate provisions of law. Upon approval of the
remediation plan by the Commission, ExxonMobil (or its successor and
assigns) shall diligently remediate the contamination in accordance with the
plan"
Again, with the imposition of the above additional "Special Condition", the City supports the
approval of Permit Number E-99-01 as recommended by the Commission's Staff.
If you have any questions regarding this letter and the information provided, Mr. Lee
Whittenberg, Director of Development Services, will be in attendance at the time this matter is
considered by the Commission, and will be most willing to provide additional information or
respond to questions from the Commission.
Sincerely,
ç$9
Paul Yost, Mayor
City of Seal Beach
Distribution:
Members of the Coastal Commission
Coastal Commission Staff
Belmont Island Decommissioning.CC SR 7
Belmont Island Decommissioning Project -Permit No. E-99-01
1omment Letter re: Coastal Commission Consideration
PF City Council Staff Report
O� February 14, 2000
Seal Beach City Council Seal Beach Planning Commission
Seal Beach Environmental Quality Control Board
Director of Development Services
Belmont Island Decommissioning.CC SR 8
Belmont Island Decommissioning Project-Permit No. E-99-01
Comment Letter re: Coastal Commission Consideration
City Council Staff Report
February 14, 2000
ATTACHMENT 2
"APPLICATION NO. E-99-1 - BELMONT ISLAND
DECOMNIISSIONING PROJECT" COASTAL
COMIVIISSION STAFF REPORT, DATED
JANUARY 27, 2000
Belmont wand Decommi..ioning.CC SR 9
STATE OF CALIFORNIA-THE RESOURCES AGENCY GRAY DAVIS,GOVERNOR
CALIFORNIA COASTAL COMMISSION
45 FREMONT,SUITE 2000
SAN FRANCISCO,CA 94105.2219 '5
VOICE AND TDD(4I5)904-5200 rV
FAX(415)904-5400
ru t)
rtA
car; ` - Date Filed: January 25, 2000
- ' O�,j0� 49th Day: March 13, 200
�(� \ Staff: LSF/AD-SF
ti r Staff Report: January 27,2000
`'" Hearing Date: February 15, 2U00
Item Number: Tu 1 lb
0- Commission Action:
STAFF RECOMMENDATION
REGULAR CALENDAR
Permit Number: E-99-01
Applicant: ExxonMobil Production Company
Agent: Simon Poulter, Padre Associates, Inc.
Project Location: About 8,100 feet offshore of the City of Seal Beach, Orange
County, State Lease PRC 186.5 (Exhibit 1).
Project Description: Removal of Belmont Island, including well conductors,caisson
core, decks, tower,pilings, wharves,boat landing and rock rip-rap;
and abandonment in place of one electrical power cable and four
pipelines (Exhibit 2).
Substantive File
Documents: See Appendix B
SYNOPSIS
ExxonMobil is applying for a coastal development permit to decommission and remove Belmont
Island, a non-operating offshore oil and gas production facility, and to abandon in place a
submarine power cable and four pipelines. Belmont Island is located approximately 8,100 feet
offshore from Seal Beach in Orange County on State Lease PRC 186.5.
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 2
The facility components to be removed include: the south span and south tower, the concrete
caisson deck and wall structures, approxi*-Lately 9,735 cubic yards of sand and quarried rock fill
in the caisson core, 70 well conductors, 106 untreated wooden piles, the east wharf decking and
piles, the steel strut support system on the west face, the north wharf decking and piles, the boat
landing jacket a d piles, the steel sheet pile caisson the clean rock and sand fill inside the
caisson, and the 15,724 cubic yards of rock rip-rap surrounding the caisson. The applicant
proposes to cut off all island structures even with or below the natural seafloor. The quarried
rock rip-rap around the caisson core is proposed to be taken by barge to the Bolsa Chica
Artificial Reef(BCAR'). The applicant proposes to take other island components by barge to
temporary storage areas in the Long Beach or Los Angeles Harbor or directly to approved
facilities onshore for disposal.
The project is projected to take approximately seven and one-half months to complete.
Consideration of On-Site Artificial Reef
The applicant considered the alternative of converting a portion of the rock rip-rap found at
Belmont Island to an on-site artificial reef. In consultation with the California Department of
Fish and Game ("CDFG"), several options were considered. However, CDFG and applicant
surveys of the marine resources present at the island and discussions between the applicant and
the U.S. Coast Guard and the California State Lands Commission ("SLC") led to the conclusion
that there are physical drawbacks and liability concerns regarding using the site for an artificial
reef. Drawbacks include turbid water conditions at the site which prevent kelp from growing,
and the potential for vessel groundings. Staff agree with the assessments of the other state and
federal agencies that this alternative is neither a feasible option nor the environmentally
preferable alternative. On December 3, 1999, the SLC approved ExxonMobil's proposal to
decommission and remove Belmont Island, including utilization of the rock rip-rap at the BCAR.
(For more details, see section 4.4 of this report).
Coastal Act Issues
Marine Resources
The proposed project is designed to restore the marine environment to a condition similar to the
natural conditions present at the project site prior to island construction. However, in order to
achieve this objective, project activities will result in some incidental impacts to marine
resources. The potential impacts and mitigation measures include:
• Incidental displacement of Garibaldis (Hypsypops rubicundus), a nongame fish species
protected under state law. The applicant has a no-fishing policy in place at the island, and
will instruct project personnel of the policy and the protected status of the fish.
Augmentation of BCAR, to a limit of 120,000 tons of clean material, was approved by the Coastal Commission in
October 1995, under Consistency Certification CC-81-95.
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 3
• Potential impacts to benthic marine invertebrates from decommissioning activities and
anchoring. The marine invertebrates in the project area are not unique, are adapted to turbid
conditions, and are generally short-lived. The applicant proposes to use anchoring
techniques that minimize impacts to benthic organisms.
• Incidental displacement of marine birds that utilize the island for foraging or resting. The
impact is considered insignificant because their use of the island is : ght, and they will be
able to utilize similar areas nearby.
• Potential for interactions with marine mammals. The applicant will train all project
personnel to follow the procedures contained in its Marine Wildlife Contingency Ilan.
• Project-related discharges. The potential exists for minor amounts of lead-based paint,
concrete, steel cuttings, wastewater, marine growth, island components and other project-
related debris to be discharged. The applicant proposes to use best management practices,
including using special containment tanks to remove hazardous debris, using cooling water
on the concrete saws, installing a system under the decks to minimize discharges, and
removing any project-related debris on the seafloor at the conclusion of the project. Special
Condition 2 requires the applicant to take precautions to contain floatable material generated
as a result of the project and dispose of all such materials at an approved landfill. Special
Condition 1 requires the applicant to submit a report to the executive director regarding the
results of the debris removal survey to verify that all debris have been removed.
• Temporary, short-term and localized turbidity. The applicant proposes to funnel wastewater
from concrete cutting activities to the caisson core then remove the water with a vacuum,
placing it into special containment tanks for removal.
Oil and Gas Spill Prevention and Response
The proposed project has the potential to result in a release of hydrocarbons to the coastal
environment. Special Condition 3 requires that the oil and gas pipelines be cleaned to a level
that maximizes spill prevention, less than 15 ppm Total Petroleum Hydrocarbons ("TPH").
Special Condition 4 requires the applicant to document the level of TPH remaining after the
cleaning by sending test samples to a state-certified laboratory.
Regarding oil spill response, Special Condition 6 requires that a seep tent and support vessels be
used during the cutting of the oil and gas lines. Special Condition 5 requires the applicant to
submit written evidence to the executive director that it has contracted with Clean Coastal
Waters (an oil spill cooperative) for the duration of the proposed project. Even with these
Special Conditions, Commission staff find that the proposed project is inconsistent with the
second test contained in section 30232 of the Coastal Act, which requires that "Effective
containment and cleanup facilities and procedures shall be provided for accidental spills that do
occur", because state-of-the-art oil spill response is such that no equipment is currently available
that can effectively keep spilled oil off of the coastline. Notwithstanding this inconsistency,
Commission staff believe that the proposed development can be approved under section 30260
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 4
of the Coastal Act, which provides for special approval of coastal-dependent industrial facilities
that are otherwise found inconsistent with the resource protection and use policies contained in
section 3 of the Coastal Act. The decommissioning of an offshore and gas production island
is considered "coastal dependent" under section 30101 of the Coastal Act.
Public Access and Recreation
Island demolition and removal activities will not adversely impact recreational users or interfere
with the public's access to the beach. In addition to island decommissioning, the applicant
proposes to abandon in place four pipelines and one electrical power cable that are currently
buried 4 to 9 feet below the seafloor and the surface. The pipelines and cable are unlikely ever to
be uncovered because they are located in a high depositional offshore environment and have
never been exposed. However, in the event that they are exposed in the future, Special
Condition 7 requires that if any of the pipelines or the power cable become exposed, the
executive director will schedule for the Commission's consideration the question of whether
removal of the facilities may be necessary to mitigate individual or cumulative adverse impacts
to coastal resources. If the Commission finds in the future that the facilities should be removed,
ExxonMobil shall submit a plan for removal of the facilities in the form of an application to
amend this permit.
Staff Recommendation
The Commission staff recommends that the Commission approve the proposed project, as
conditioned.
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 5
1.0 STAFF RECOMMENDATION
Motion:
I move that the Commission approve Coastal Development Permit Application No. E-99-01
subject to conditions set forth in the staff recommendation.
Staff Recommendation of Approval:
Staff recommends a YES vote. Passage of this motion will result in approval of the permit
subject to conditions set forth in the staff recommendation and adoption of the following
resolution and findings. The motion passes only by affirmative vote of a majority of the
Commissioners present.
Resolution to Approve the Permit:
The Commission hereby approves a coastal development permit for the proposed development
and adopts the findings set forth below on grounds that the development as conditioned will be in
conformity with the policies of Chapter 3 of the Coastal Act and will not prejudice the ability of
the local government having jurisdiction over the area to prepare a Local Coastal Program
conforming to the provisions of Chapter 3. Approval of the permit complies with the California
Environmental Quality Act because either (1) feasible mitigation measures and/or alternatives
have been incorporated to substantially lessen any significant adverse effects of the development
on the environment, or (2) there are no further feasible mitigation measures or alternatives that
would substantially lessen any significant adverse impacts of the development on the
environment.
2.0 STANDARD CONDITIONS See Appendix A.
3.0 SPECIAL CONDITIONS
This permit is granted subject to the following special conditions:
1. Report on Removal of Project-Related Debris. Within 90 days of project completion,
the applicant shall submit to the executive director a report containing 1) a description of the
debris items removed from the vicinity of the project area at the conclusion of the project,
and 2) the results of the side scan sonar survey to verify that all project-related debris has
been removed.
2. Containment and Removal of Floatable Materials. The applicant shall (1) take
precautions to ensure that floatable materials of all types generated as a result of the project
do not leave the project site; and (2) collect any floatable materials generated and dispose of
them at an approved landfill.
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 6
3. Cleaning Oil and Gas Pipelines. The applicant shall clean the interior of the oil and gas
pipelines to a level of less than 15 ppm Total Petroleum Hydrocarbons (TPH).
4. Test Results from Cleaning Oil and Gas Pipelines. The applicant shall document the level
of TPH at the conclusion of flushing operations using a state-certified laboratory and a test
method acceptable to the executive director. Within 30 days of cor ipletion of pipeline
flushing, ExxonMobil will provide the test results to the executive director.
5. Contract with Clean Coastal Waters. Prior to issuance of this permit, the applicant shall
submit to the executive director written evidence that, for the duration of the Be: nont Island
decommissioning project, it has contracted with Clean Coastal Waters (CCW) fc.-oil spill
response and clean up services.
6. Seep Tent and Support Vessel. Prior to cutting the oil and gas pipelines offshore, the
applicant shall deploy a seep tent over each of the cut points and provide a support vessel to
capture and remove from the marine environment any residual hydrocarbons that may be
released from the lines when they are cut.
7. Exposure of Abandoned Facilities. If any of the facilities (i.e., four pipelines and one
electrical power cable) that have been allowed to be abandoned in place under this permit
become exposed to the natural (i.e., air or aquatic) environment, the executive director will
schedule for the Commission's consideration the question of whether removal of the
facilities may be necessary to mitigate individual or cumulative adverse impacts to coastal
resources (e.g., hazards to recreational users). In the event of an affirmative determination
by the Commission on the foregoing question, ExxonMobil shall, within 60 days after such
determination, submit a plan for the removal of such facilities in the form of an application to
amend this permit.
8. Approval or Waiver from the South Coast Air Quality Management District. Prior to
issuance of this permit, the applicant shall submit to the executive director(a)(1) a copy of
the permit(s) issued by the South Coast Air Quality Management District ("SCAQMD") for
the decommissioning project and project equipment, and (a)(2) written evidence of the
mitigation measures, if any, the SCAQMD is imposing to offset project-related air quality
impacts; or (b) written evidence of a waiver from the SCAQMD indicating that no permit(s)
or mitigations are required for the project.
4.0 FINDINGS AND DECLARATIONS
The Commission finds and declares as follows:
4.1 Project Location
Belmont Island is located on State Lease PRC 186.5, 8,100 feet offshore from Seal Beach,
Orange County, in a water depth of approximately 42 feet. Four subsea pipelines, used to carry
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APPL CANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 7
gas, oil, and fresh water and one submarine power cable are also located on State Lease PRC
186.5 and connect Belmont Island to 101 Marina Dr., Seal Beach, the former site of ExxonMobil
r'roduction Company's ("ExxonMobil") Seal Beach Oil Separation Facility and Tank Farm. The
majority of the project work is proposed to take place on State Lease PRC 186.5; some work to
flush and abandon the pipelines will take place at 101 Marina Drive.
4.2 Project Background
Monterey Oil Company began construction of Belmont Island in 1953, building the island's
caisson core, concrete deck, the north wharf, and submerged pipelines by 1954. The caisson
core consists of ferrous steel sheet piles, and is filled with quarry rock, native sand, and 106
wooden bearing piles; seventy well conductor pipes were installed within the core to produce oil
and gas. Between 1955 and 1958, more features were added to the island: a concrete wall
around the caisson core, quarried rock rip-rap around the exterior of the core, internal walls, a
reinforced concrete drill deck, a steel catwalk, a steel tower, a bridge to the caisson core,
stairways, the east wharf, a shop, a mud tank, a crane pedestal, and a mezzanine deck. In 1960,
the submarine electrical power cable was installed, converting the island to shore power. In
1962 and in 1983, steel bracing and supports were installed on the north wharf to stabilize it.
Also in 1983, a steel boat landing jacket, new deck sections, a crew change room, and electrical
equipment were added to the island.
Fifty-six of the seventy wells at Belmont Island were used to produce oil and gas; the remainder
were never used. Oil and gas production ceased at Belmont Island in 1995. In June 1997, the
Coastal Commission approved a de minimis waiver (E-99-03-W) for Exxon Company U.S.A.,
for flushing and cutting the wellhead conductors on Belmont Island, so the work could occur
prior to the onset of the winter storm season.
Exxon Company formerly operated an oil separation facility and tank farm to handle the oil and
gas produced from the Belmont Island wells at 101 Marina Drive in Seal Beach. In April 1997,
the Coastal Commission approved a de minimis waiver (E-97-08-W) for A.C. Pipe and
Equipment Company to disassemble and remove five oil storage tanks and associated production
equipment and piping from Exxon's former oil separation facility and tank farm. All of the
structures were above ground, and had been disused since the facility was shut in and taken out
of service in January 1994. In December 1999, the Coastal Commission approved a de minimis
waiver(E-99-12-W) for Exxon Company for demolition and removal of a 250-sq. ft. building
located at the same site. Any further decommissioning of facilities or other development at the
onshore property will require a coastal development permit.
4.3 Project Description
The applicant proposes to decommission and remove Belmont Island, a non-operating oil and
gas production facility, and abandon in place one two-inch diameter submarine electrical power
cable, two three-inch diameter steel pipelines formerly used to ship produced gas to the onshore
terminal, one eight-inch diameter steel pipeline formerly used to ship produced oil to the onshore
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
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terminal, and one three-inch diameter steel pipeline formerly used to ship fresh water from the
onshore terminal to Belmont Island (Exhibit 2).
ExxonMobil proposes to dismantle Belmont Island and remove its components in the following
sequence: south span and south tower, concrete caisson deck and wall structures, approximately
392 cubic yards of hydrocarbon-impacted sand and quarried rock fill in the caisson core, which
contains approximately 9,735 cubic yards of fill; 70 well conductors; 106 untreated wooden
piles; east wharf decking and piles; steel strut support system on the west face; north wharf
decking and piles; boat landing jacket and piles; steel sheet pile caisson the clean rock and sand
fill inside the caisson; and the 15,724 cubic yards of rock rip-rap surrounding the caisson. The
total project is projected to take approximately seven and one-half months (30 weeks2).
Concrete structures will be saw cut or broken into pieces; wood and concrete piles will be
extracted, saw cut, or severed with a pile buck; and steel components will be extracted, torch cut
or mechanically cut; a derrick barge will be used for lifting and removal of structures. All island
structures will be cut off even with or below the natural seafloor.
The quarried rock rip-rap around the caisson core is proposed to be taken by barge to the Bolsa
Chica Artificial Reef(BCAR). These materials are estimated to weigh between 15,000-30,000
tons. Augmentation of BCAR, to a limit of 120,000 tons of clean material, was approved by the
Coastal Commission in October 1995, under Consistency Certification CC-81-95. Other
uncontaminated island components will either be taken to temporary storage areas in the Long
Beach or Los Angeles Harbor, then recycled3 or disposed of in approved facilities onshore.
The electrical power cable will be disconnected from the junction box onshore by Southern
California Edison. Offshore, the cable will be cut at the seafloor near the south tower, and
trenched into the seafloor to a depth of approximately five feet below the natural bottom. The oil
pipeline and the two gas pipelines will then be flushed with seawater to remove hydrocarbon
contamination; flushing will continue until tests show that the level of hydrocarbons is 15 ppm or
less. All wastewater generated during flushing will be disposed of at an appropriate onshore
facility. The eight-inch pipeline will then be filled with grout from the onshore property to the
point offshore where the line is approximately 15 feet below mean lower low water(MLLW);
wastewater generated during the grouting procedure will also be disposed of at an appropriate
onshore facility. The final proposed disposition of the four pipeline terminations onshore is: the
8-inch l:ne will be plugged with cement, the three 3-inch lines will be welded closed, and all
lines w111 be buried beneath the surface. Offshore, the four pipelines are proposed to be
disconnected from the caisson, plugged, and re-buried via jetting to approximately 4-6 feet
below the seafloor, the approximate depth of the straight section of the lines at this location.
Once island decommissioning and pipeline abandonment is complete, ExxonMobil proposes to
remove from the seafloor debris items identified though surveys conducted in 1997 and any
debris generated during decommissioning procedures, to 1000 feet from the former center of
2 This estimate includes cutting and preparation of the well conductors, which was previously approved by the
oastal Commission under coastal development permit de minimis waiver E-99-03-W.
3 Materials that will be evaluated for recycling include steel,concrete,grout, and the well conductors.
CDP APPLICAT )N E- 9-01
APPLICANT: EXXON `BIL PRODUCTION COMPANY
PAGE 9
Belmon' 'star .. Buried objects will be excavated by divers using airlifts or handjets, then the
objects will bt, hoisted to the surface with slings or other rigging and transported to shore for
disposal. Pro;.;ct pc.-sonnei will conduct a side scan sonar survey to ensure the area has been
cleared of debris.
The final project activity ExxonMobil proposes is to smooth the mound of sand that surrounds
the caisson core. Currently 15 feet high, it will be disturbed and partially reduced during
decommissioning and removal activities. A clam bucket will be used to flatten the remaining
mound of sand in a circle to a depth of 2-3 feet; it is expected that wave and current action will
further disperse the sand mound.
4 4 Project Alternative - Conversion of Part of Island to an On-Site Artificial Reef
Prior to submitting a Belmont Island Decommissioning Plan to the California State Lands
Commission ("SLC"), the applicant participated in a number of pre-application meetings with
staff of the SLC, Coastal Commission, U.S. Army Corps of Engineers, and the California
Department of Fish and Game ("CDFG") to discuss, among other issues, the option of
converting the rock rip-rap at the island to an on-site artificial reef.
In consultation with staff of CDFG's Artificial Reef Program, the applicant initiated an artificial
reef design process that included conducting site-specific bathymetry, bottom sediment
characterization, seafloor feature, and biological surveys. CDFG divers also conducted dive
surveys at the island to evaluate the existing biological community at the site. The applicant's
biological survey showed that the majority of fish aggregate at the pier pilings4, not the rock rip-
rap. Nevertheless, the applicant developed three potential on-site reef designs, a High Relief
Onsite Reef, a Reconstructed High Relief Reef, and a Low Relief Onsite Reef, to be considered
by the appropriate regulatory agencies.
High Relief Onsite Reef
All piling would be cut at a height below the existing rip-rap or mudline. Existing rip-rap and
armor rock would be moved only to the extent required to safely remove the structures. Portions
of steel, concrete and wood structures located below the rock line would be abandoned in place.
The intent of this alternative is to decommission the island with the least amount of disturbance
to rip-rap.
Reconstructed High Relief Reef
The intent of this alternative is to remove all island structural components down to and below
natural mudline, while reconstructing a high profile rocky mound onsite using the existing rip-
rap. The rock would be mounded at the site to create a crescent shaped mound standing
approximately 10-15 feet below the water surface.
1 The pier pilings must be removed as part the applicant's lease clearance obligations.
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APPLICANT: EXXONMOBIL PRODUCTION COMPANY
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Low Relief Onsite Reef
Under this option all island components would be removed down to and below natural mudline,
while constructing a low profile rocky mound onsite using the existing rock rip-rap. Removal of
the steel towers, concrete wharves and caisson core would require that the rock rip-rap be
removed away from the caisson core and repositioned around the island site. The rock would be
used to create an oval-shaped reef structure standing about 39 to 33 feet below the water surface.
The applicant concluded, after consultation with the staff of the CDFG, U.S. Coast Guard and
SLC, that an on-site reef option is not feasible or the least environmentally damaging project
alternative. The physical site-specific drawbacks to an on-site reef include:
• All on-site reef alternatives raise significant vessel grounding hazard concerns and would
require that aids to navigation be installed. The U.S. Coast Guard requires a minimum
navigation clearance of 30 feet at this location;
• Poor water quality will severely limit species diversity below the 25 foot depth relative to
other existing reef sites including the CDFG reef at Bolsa Chica; and
• Kelp is unlikely to grow naturally at this site due to the relatively turbid water conditions and
the lack of a nearby kelp bed to provide spores for recruitment. The turbid water conditions
would probably also prevent transplanted kelp from surviving. Also, the marine species at
Belmont Island are not unique to the area and are similar to those found at the neighboring
Long Beach Breakwater, Los Alamitos and Seal Beach jetties and other offshore oil
platforms.
There are also concerns about ownership and liability and the proximity of the site to local
harbors and marinas. In short, the staff of the U.S. Coast Guard, SLC and CDFG agreed that the
ExxonMobil's Belmont Island site is not a feasible site for an artificial reef.
The applicant also developed an off-site reef alternative that involves loading the rock rip-rap
onto barges and depositing the rock at the existing Bolsa Chica Artificial Reef site, an approved
CDFG artificial reef located in about 80 to 120 feet of water approximately three miles offshore
of Huntington Beach State Park. The benefits of this alternative are that (a) CDFG has agreed to
acquire the rock rip-rap to enhance the Bolsa Chica Artificial Reef(and therefore assume
ownership and liability); (b) water clarity is superior as compared to the site of ExxonMobil
Belmont Island; and (c) the Bolsa Chica site eliminates potential vessel grounding concerns since
the water depth is greater than at Belmont Island.s
On December 3, 1999, the SLC approved the Belmont Island Decommissioning Project that
includes transporting the rock rip-rap to the Bolsa Chica Artificial Reef.
s The applicant n9tes that all on-site and off-site artificial reef options will require significant movement of the rip-
rap and potential “iortality of species that have colonized on the rock.
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On December 6, 1999 after the SLC had lready approved the Belmont Island Decommissioning
Project, a group called Heal the Harbor, c. sent letters to ExxonMobil, the SLC and Coastal
Commission (Exhibit 3) offering to assume the legal ownership of, and financial liability for, a
Belmont Island artificial reef. Heal the Harbo-nas not demonstrated control over the area (e.g., a
lease from the SLC) or adequate financial resources to assume legal liability for such a reef
structure. For these reasons, combined with the site-specific concerns discussed above, the
Cuastal Commission believes that an on-site Belmont Island reef is not a feasible option or the
environmentally pref arable alternative.
4.5 Other Agency Approvals
43.1 St:.ie Lands Commission
As "lead agency" under the California Environmental Quality Act ("CEQA"), the SLC prepared
a Mitigated Negative Declaration for the decommissioning of facilities on Belmont Island,
removal of the island, and abandonment in place of the electrical power cable, water pipeline, oil
pipeline, and gas pipelines. On December 3, 1999, the SLC certified Negative Declaration 694
(State Clearinghouse No. 99031117) and approved the decommissioning of Belmont Island
facilities, removal of the island, and abandonment in place of the power cable and pipelines.
4.5.2 U.S. Army Corps of Engineers
On April 27, 1999, the Los Angeles District of the U.S. Army Corps of Engineers ("ACOE")
conditionally approved Provisional Permit 1999-15473-RLK for the proposed project, pursuant
to Section 10 of the Rivers and Harbors Act of 1899 (33 U.S.C. 1344). Section 10 of the Rivers
and Harbors Act regulates the diking, filling and placement of structures in navigable waterways.
Because the project is located within the navigable waters of the United States and will result in
the excavation of 37 cubic yards of native seafloor materials, Padre Associates, Inc., in a letter
dated May 25, 1999 requested that the ACOE issue a permit for the project pursuant to Section
404 of the Clean Water Act ("CWA") (33 U.S.C. 1344). Section 404 of the CWA regulates
disposal of dredge and fill materials into waters of the United States, including all streams to
their headwaters, lakes of 10 acres and contiguous wetlands"). On May 27, 1999, the ACOE
determined that a permit would not be required under Section 404 of the CWA because the
project involves incidental fall back of materials, rather than fill.
Pursuant to section 307(c)(3)(A) of the Coastal Zone Management Act, any applicant for a
required federal permit to conduct an activity affecting any land or water use or natural resource
in the coastal zone must obtain the Coastal Commission's concurrence in a certification to the
federal permitting agency that the project will be conducted consistent with the California
Coastal Management Program. The Commission's action on this permit application shall
comprise its federal consistency agency review for ExxonMobil's proposed project.
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APPLICANT: EXXONMOBIL r)RODUCTION COMPANY
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4.5.3 Santa Ana Region Regional Water Quality Control Board
The California Regional Water Quality Control Board, Santa Ana Region ("Santa Ma Region")
regulates marine water quality in the Belmont Island project area. The Santa Ma Region issued
a conditional clearance for the proposed project in a letter dated May 6, 1999 (Exhibit 4). The
letter stated that the proposed project entails demolition and dredging within navigable waters,
which will result in a temporary, short-term plume that will have a minimal and temporary
impact on water quality; it also stated that a 401 Certification will not be required since the U.S.
Arm l'orps of Engineers intends to issue a Letter of Permission for the project. In a letter dated
June 71, 1999 (Stewart 1999a) (Exhibit 5) the Santa Ma Region staff stated that they had no
objection to ExxonMobil's proposal to allow to fall to the ocean bottom marine growth removed
from the caisson walls and other below-water island structures.
4.5.4 South Coast Air Quality Management District
The South Coast Air Quality Management District ("SCAQMD") is the local air district
responsible for implementing federal and state air quality standards in the Belmont Island project
area. SCAQMD staff will review the proposed project to determine if air quality permits will be
required for decommissioning activities and project equipment, and if mitigation measures
beyond those contained in the MND are necessary to offset project-related air quality impacts.
See section 4.6.6 of this report for project-related air quality information.
4.6 COASTAL ACT ISSUES
4.6.1 Marine Resources and Water Quality
Coastal Act § 30230 states:
Marine resources shall be maintained, enhanced, and where feasible, restored. Special
protection shall be given to areas and species of special biological or economic significance.
Uses of the marine environment shall be carried out in a manner that will sustain the
biological productivity of coastal waters and that will maintain healthy populations of all
species of marine organisms adequate for long-term commercial, recreational, scientific, and
educational purposes.
Coastal Act § 30231 states:
The biological productivity and the quality of coastal waters, streams, wetlands, estuaries,
and lakes appropriate to maintain optimum populations of marine organisms and for the
protection of human health shall be maintained and, where feasible, restored through,
among other means, minimizing adverse effects of waste water discharges and entrainment,
controlling runoff preventing depletion of ground water supplies and substantial
interference with surface water flow, encouraging waste water reclamation, maintaining
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APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 13
natural vegetation buffer area, that protect riparian habitats, . di minimizing alteration of
natural streams.
The proposed decommissioning and removal of Belmont Island is desigr,.,d to restore the marine
environment to a condition similar to the natural conditions present at the project site prior to
island construct;on. Some impacts to marine resources, projected to be short term and
temporary, will occur during project activities, h)wever.
Potential impacts to marine resources include sone incidental loss of marine invertebrates and
fish; incidental disturbance of marine birds; accidental injury to or death of marine mammals;
disruption of marine biological resources from artificial nigh' 'ighting; and localized alterations
in marine water and sediment, including discharge of minor a-nounts of wastewater and materials
into marine waters, temporary and localized turbidity of marine waters, and introduction of small
amounts of copper into marine sediments.
No Impacts to Wetlands, Kelp, Eelgrass or Surfgrass
The proposed project will not result in any impacts to wetlands, kelp, eelgrass or surfgrass. No
wetlands are found within the lease area or on the applicant's onshore property, and a marine
biological survey conducted for this project in 1999 (de Wit 1999) found no evidence of kelp,
eelgrass or surfgrass on Belmont Island. In addition, none grows on the seafloor in the vicinity
of the pipelines and power cable, or in the area that will be utilized by project vessels during
decommissioning activities.
Marine Invertebrates and Fish
The construction of Belmont Island in the early 1950s resulted in the incidental creation of
human-made substrates, consisting of concrete caisson core walls; wooden pilings; concrete and
steel H-beam piles; a tubular steel jacket boat landing structure with struts; strut supports; and
native sand and quarried rock rip-rap which encircles the base of the structure and extends from
the seafloor to approximately 15-18 feet MLLW. Consistent with state requirements for
decommissioning oil production facilities, ExxonMobil proposes to remove all development
associated with the island or to cut structures off even with or below the seafloor. The rock rip-
rap surrounding the island is proposed to be used for augmentation of the Bolsa Chica Artificial
Reef("BCAR"), and all of the other island components will be recycled or disposed of onshore,
in approved facilities. The Coastal Commission approved augmentation of the Bolsa Chica
Artificial Reef in October 1995 (Consistency Certification CC-81-95).
A marine biological survey conducted for this project in 1999 documented the marine resources
associated with Belmont Island and the surrounding seafloor, the eastern Long Beach
Breakwater, and Platform Esther(de Wit 1999). The report summarizing the survey also
included results of a 1992 study of BCAR. Fifty taxa of marine species were documented during
the survey at Belmont Island. The survey found that the rip-rap and sedimentary substrates at the
four sites were similar, and, except for algae and fish, the rip-rap at Belmont Island had led to the
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 14
incidental support of a relatively diverse marine biological community that is similar to those
found within the same water depths at the Lord Beach Breakwater and Platform Esther. The
algal community at Belmont Island was characterized as depauperate, while the fish present at
the island were more diverse; this difference appeared to be related to the dock and pier pilings
present at the island The marine waters surrounding Belmont Island were described as
relatively turbid.
There is one protected marine fish species that occurs at the project site, the Garibaldi (Hysypops
rubicundus). Garibaldis are the state fish and are protected under state law from sport and
commercial take. Before decom.liissioning operations begin, the applicant will inform all project
personnel of the policy and the G.,-ibaldi's protected status. Though the project will displace
Garibaldis, it is likely that they will recolonize similar areas nearby.
Marine benthic organisms in the project area are generally short-lived and are adapted to turbid
conditions that result from a variety of local factors, including currents, the San Gabriel River
and storms. They include sand dollars, tube worms, sea pens, sea pansies, annelid worms, tube
worms and crustaceans (Dugas 1999 and California State Lands Commission 1999a). Though
the benthic marine organisms found in the vicinity of Belmont Island are not unique and do not
have any special status, ExxonMobil proposes to use an anchoring technique called "fly-over
anchoring" to place the anchors in predetermined locations on the seafloor, thus reducing
potential crushing and smothering impacts to benthic marine organisms.
Marine Birds
Approximately 105 species of marine birds are found in the project area, including two
endangered species, the California brown pelican and the California least tern. As a human-
made structure, Belmont Island provides an incidental benefit as a resting and foraging site for
marine birds. The noise and demolition activities will discourage marine birds from using the
site, and the removal of Belmont Island will incidentally displace the marine birds that
occasionally utilize it. However, marine birds have not significantly utilized the island. In
addition, the Long Beach breakwaters are nearby, providing similar resting and foraging areas as
the island for California brown pelicans, least terns and other birds (Dugas 1999). The MND
found that impacts to marine birds as a result of the proposed project are adverse, but not
significant.
Marine Mammals
In order to decommission and remove Belmont Island, the project will require the use of vessels
and barges, and will result in a temporary, localized increase it: vessel traffic in the project area.
Though unlikely, the possibility exists that a marine mammal could be struck and injured or
killed by a vessel or barge during project activities. Marine mammals do not haul out on
Belmont Island, and the demolition o`t the island is not expected to result in any impacts to
marine mammals.
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Marine mammals are protected under the Marine :v,ammal Protection Act of 1972, and under th
Endangered Species Act of 1973, it is unlawful to harass, harm, or kill endangered and
threatened marine mammal species. In the Southern C difornia Bight area, five endangered
marine mammal species (Blue whale, Fin whale, Sperm whale, Right whale, and Sei whale) and
two threatened marine mammal species (Sea otter and Guadalupe fur seal) are known to occur;
other, non-listed species in th.t project area include, but are not limited to, the Gray whale,
common dolphin, California white-sided dolphin, sea lion, and harbor seal. ExxonMobil has
prepared a Marine Wildlife Contingency Plan for use by project personnel, so that they can avoid
harming marine mammals, and personnel will be trained prior to the start of the project. The
plan includes a requirement for marine mammal observers on vessels, avoidance procedures, and
instructions for what to do if an accidental collision with a marine mammal occurs. Spe''fically:
• support vessel operators will make every effort to maintain a distance of 1,000 feet from
whales to minimize the possibilities of collision and disturbance;
• support vessels will not cross directly in front of migrating whales;
• when paralleling whales, support vessels will not operate at a speed faster than the whales,
and will operate at a constant speed;
• female whales will not be separated from their calves;
• support vessels will not be used to herd or drive whales;
• if a whale engages in evasive or defensive actions, support vessels will drop back until the
animal calms down or moves out of the area;
• if dolphins ride the boat waves or frolic near a vessel, the vessel operator should slow the
vessel down and keep a steady course until they lose interest;
• project personnel should make every effort to avoid approaching and disturbing pinnipeds
and other marine mammals in the water or at rest;
• project personnel should encourage any pinnipeds that hauled out in the project area and are
at risk of injury from project activities to move from the hazard area by making a noise such
as clapping;
• if a vessel collides with a marine mammal, the vessel operator should stop, if it is safe to do
so, then proceed if proceeding will not further damage the animal; and
• after a vessel collision with a marine mammal, the vessel operator must document the
conditions of the accident, and the operator or other project personnel must contact the
National Marine Fisheries Service Stranding Coordinator to report the accident.
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 16
Artificial Night Lighting
Most of the project activities are expected to occur during daylight hours, but some work may
take place at night. For nighttime activities, artificial lighting will be used. Since the light is
artificial, there is the potential that fish, inverte rates, and marine mammals could change some
of behaviors in response to the light. However, the light sources will be similar to those used for
other offshore oil and gas structures and in nearby port operations, their use will be temporary,
and if work must be done after dark, their use will be necessary for practical and safety reasons.
While there is the possibility that artificial lights at night could have affect marine resources, the
potential impact is not likely to be significant.
Coastal Water and Sediment Quality
Discharges to Coastal Waters
Due to Belmont Island's location in the marine environment, some discharges to coastal waters
are projected to occur as the applicant demolishes the island and removes its components. Minor
amounts of lead-based paint, concrete, steel cuttings, wastewater, marine growth, and island
components and other project debris and could be discharged as a result of the project. Project
activities could also cause some localized turbidity in the marine environment.
Lead Paint, Wastewater and Cuttings
The MND found that the paint used on Belmont Island steel structures and concrete is lead-
based, and stated that tests show the lead content ranges from 1,000 ppm to 87,000 ppm.
Subsequently, in April 1999 Padre Associates (Zukor and Emslie 1999) tested concrete samples
from the surfaces around the island, and the results showed that the concrete at the sample
locations would not be considered a hazardous waste under state and federal regulations due to
their lead content. The assessment did not include tests of other painted surfaces at the island.
To minimize potential discharges of cement dust and paint to the marine environment during
concrete cutting activities, concrete saws are proposed to be used to cut the upper and lower
concrete decks on Belmont Island as they are prepared for removal, and water will be used to
cool the saws to minimize the release of fugitive dust. The upper deck drains to the lower deck,
which in turn drains into the caisson core. The project schedule is designed such that the caisson
core will be one of the last features to be demolished and removed, and thus the majority of the
cooling water expected to be generated by the project will drain into, and be contained by, the
caisson core. All water in the core will be removed later in the project schedule when all core
materials are removed. The wastewater will be transported to shore in steel containment boxes
for treatment (see section 4.6.2 of this report, Oil and Gas Spills for a discussion of the proposed
procedures). Though the majority of the cooling water will drain into the core, a maximum of
four barrels of wastewater could be incidentally discharged to the marine environment (Weber
2000).
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
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Prior to beginning the project, ExxonMobil plans to develop a site safety plan, which will
include procedures to handle lead-based paint. The company plans to recycle steel and concrete
coated with lead based paint at an onshore facility permitted to handle such materials. The SLC
has required in its Mitigation Monitoring Program that ExxonMobil prepare the plan for SLC
review, prior to final project approval.
Demolition and Other Project-Related Debris
To reduce the possibility of introducing structural components of the island into marine waters,
ExxonMobil proposes to install a containment system underneath the wharf decks. To ensure no
human-made materials associated with the island are unintentionally left in the marine
environment, ExxonMobil proposes to remove any debns generated by demolition activities as
well as debris identified in side scan sonar surveys conducted in 1997. Divers will place debris
items in slings or other rigging; they will then be hoisted to the surface and transported to shore
for disposal. Buried items will be excavated with airlifts or handjets prior to removal. To verify
that all debris has been removed, ExxonMobil personnel will survey the project area at the close
of the project. The Commission is requiring in Special Condition 1 that ExxonMobil submit a
report to the executive director within 90 days of project completion describing the items
removed and providing the results of the side scan sonar survey to verify that all project-related
debris has been removed.
Marine Growth
As the components of the island are being demolished and readied for removal and offsite
disposal, the potential exists for marine biological growth to be introduced into the marine
environment. Divers will remove marine growth from the caisson walls and other underwater
island components proposed for onshore disposal, and will allow the growth to fall to the ocean
bottom. This procedure is preferred by the Santa Ana Region to prevent odor and solid waste
disposal issues, provided the applicant undertakes adequate measures to minimize impacts to the
receiving waters (Stewart 1999b), including preventing floatable materials from leaving the
project site disposing of such floatable materials at a landfill site. The Santa Ana Region has
requested that the ACOE include a condition in its Letter of Permission to prevent release of
floatable materials to marine waters and to properly remove any floatable materials generated
(Schubel 1999). Consistent with this request, the Coastal Commission imposes Special
Condition 2, requiring that ExxonMobil (1) take precautions to ensure that floatable materials of
all types generated as a result of the project do not leave the project site; and (2) collect any
floatable materials generated and dispose of them at an approved landfill.
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 18
Temporary Turbidity
There are various aspects of the project that will result in increased temporary, short-term,
localized turbidity due to suspension of native sediments in the project are. , consisting of sand
and soft, silty clay. The area of potential disturbance will extend approxir lately 50 feet beyond
Belmont Island and will cover an area approximately two acres in size. Project activities that
will result in turbidity include demolition and dredging to remove all island components, burial
of the electrical power cable and pipeline ends, vessel anchoring, debris removal, flattening out
the mound of native sand that will remain after island decommissioning, and incidental
discharges to marine waters (as discussed earlier in this report).
In order to decommission and remove Belmont Island, the applicant must use equipment and
techniques that will cause some turbidity of marine waters in the project area. With the
exception of anchoring techniques, the nature of the project activities is such that turbidity
cannot be avoided. The "fly-over anchoring" technique the applicant proposes to use to place the
anchors in predetermined locations on the seafloor may serve to reduce some of the turbidity
associated with anchoring.
The increased turbidity that will result from the project will decrease light availability and could
smother or otherwise negatively affect some benthic marine organisms. However, as stated, the
marine benthic organisms in the project area are adapted to turbid conditions. Also, the Santa
Ana Region found that the plume of turbid water that will be generated by the project will result
in a minimal and temporary impact on water quality, and thus does not need to be regulated
under waste discharge requirements (Stewart 1999a). The Commission finds that the potential
turbidity impacts of the proposed project are largely unavoidable, will be temporary and short-
term, and will not significantly affect marine organisms or the biological productivity of marine
waters.
Abandonment in Place of Electrical Power Cable and Pipelines
The applicant proposes to abandon in place two three-inch diameter steel pipelines formerly used
to ship produced gas to the onshore terminal, one eight-inch diameter steel pipeline formerly
used to ship produced oil to the onshore terminal, one three-inch diameter steel pipeline formerly
used to ship fresh water from the onshore terminal to Belmont Island, and ohe two-inch diameter
submarine electrical power cable.
Prior to abandonment, the eight-inch line is proposed to be filled with cement grout from the
applicant's onshore property to the point offshore where the line is approximately 15 feet below
MLLW. The pipelines are buried below the seafloor surface, from four to nine feet deep; they
do not have a history of exposure in the surf zone or elsewhere on the seafloor. In addition, the
MND did not identify any impacts to the marine environment as a result of their abandonment in
place.
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 19
The submarine electrical power cable that formerly connected Belmont Islar.J to shore power is
also proposed to be abandoned in place. The major component of the cable is copper wire;
copper is a toxic substance which is known to bioaccumulate in the tissues of marne organisms,
and can cause tissue damage or death in marine organisms (Brown 2000). The power cable is
approximately 11,000 feet long, and is buried approximately six feet below the surface of the
seafloor. It is expected to slowly corrode and remain within the sediment. However, copper that
is contained in sediment in a bound form is less available and less toxic to marine organisms than
the free ion form of copper(Brown 2000). In addition, the seafloor in the project area does not
contain species of special biological or economic significance, and the in-place abandonment of
the power cable is not expected to impede the long-term biological productivity of the marine
environment.
Conclusion—Marine Resources and Water Quality
The Coastal Commission finds that the proposed project will not result in impacts to wetlands,
kelp, eelgrass, or surfgrass, as none are found in the project area. There will be some incidental
impacts to marine invertebrates, fish, and birds as a result of the project, but the biological
productivity of the marine species found in the area will be maintained. The Commission further
finds that there may be some short term, temporary, and localized impacts to coastal water and
sediment quality. However, the proposed project will remove a human-made structure from the
marine environment, resulting in restoration of the marine environment to a condition similar to
the natural conditions present at the project site prior to island construction. Therefore, the
Commission finds the project, as conditioned, consistent with sections 30230 and 30231 of the
Coastal Act.
4.6.2 Oil and Gas Spills
Coastal Act § 30232 states:
Protection against the spillage of crude oil, gas, petroleum products, or hazardous
substances shall be provided in relation to any development or transportation of such
materials. Effective containment and cleanup facilities and procedures shall be provided
for accidental spills that do occur.
4.6.2.1 Potential Project-Related Oil and Gas Spills
The proposed project has the potential to result in a release of hydrocarbons to the coastal
environment due to the following causes: (a) accidental work vessel or derrick barge anchor
damage to the nearby Aera-Beta pipeline, (b) removal of the hydrocarbon-impacted materials
from within the caisson, (c) flushing the pipelines formerly used to transport oil and gas to the •
onshore facility, (d) grouting the 8-inch line, (e) spillage of oil or oily water from a work barge,
(f) leakage or spillage of fuel or lubricants from work vessels or equipment, (g) removal of the
creosote-treated wooden pilings, and (h) cutting the oil and gas pipelines offshore.
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 20
Potential Offshore Spills
The worst-case spill that could arise from project operations is the rupture of the Aera-Beta crude
oil pipeline. The Aera-Beta pipeline brings oil from Platforms Elly, Ellen, and Eureka to
onshore facilities in the Long Beach Harbor; it passes by Belmont Island on the seafloor (where
it is buried), approximately 400 feet to the southwest. If ruptured during the project, a
substantial oil spill could result. The 16-inch pipeline has a capacity of 22,000 barrels. If a work
vessel or the derrick barge could anchor on top of the pipeline and rupture it, the applicant
estimates that a spill of approximately 2,200 barrels of oil to the marine environment could
occur.
While a rupture of the Aera-Beta pipeline is the worst-case spill that has the potential to occur
during the project, there are other aspects of the project that could also result in a spill of
hydrocarbons. For example, environmental assessments conducted for the project by Fugro
West, Inc. in 1996 and Padre Associates in 1997 show that some of the components of Belmont
Island are known to be contaminated with hydrocarbons as a result of the island's use as an oil
and gas production facility: cellar number 2 and its contents, the 70 well conductors, and some
of the sand, rock, and water in the caisson core. The concrete deck covering the core and its
underlying grout may also be contaminated with hydrocarbons; project personnel will be able to
determine if this is the case when they begin to remove the deck. As the components of the
island are demolished and placed onto barges for removal, the possibility exists for hydrocarbon-
impacted water or materials to fall into marine waters.
When the pipelines are being flushed and when the 8-inch line is being grouted, the pressure
needed to conduct the operations could cause one or more of the lines to leak, releasing part of
their contents to the marine environment.
The applicant's Oil Spill Contingency Plan notes that there is the potential that oil or oily water
being transported on a work barge could be discharged to marine waters, and estimates that 5
barrels of oil could be discharged to marine waters in such a spill. The Oil Spill Contingency
Plan also notes that leakage or spillage of fuel or lubricants from work vessels or equipment
could occur during the project. Neither the Oil Spill Contingency Plan nor the environmental
assessment in the MND describe how these accidents might occur, but one possible cause could
be a loss of fuel or hydrocarbon impacted cargo from vessels or barges via a collision witli
another vessel or barge, due to the increased project related vessel traffic in the area.
In addition, some of the wooden pier pilings used as Belmont Island were treated with creosote, a
substance derived from coal tar that is used as a pesticide and wood preservative. Creosote-
treated pier pilings have been known to contribute polycyclic aromatic hydrocarbons (PAHs) to
the marine environment, which can be toxic to biological resources6. When the creosote-treated
pier pilings at Belmont Island are extracted and placed on barges for disposal at an approved
Class I disposal site, it is possible that some creosote may be released into the marine
6 Refer to Coastal Development Permit No. 3-97-078 for a complete discussion and references.
CDP APPLICATION E-99-(
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 21
environment eith . from the sediment or from the pilings themselves. Any piles that canny, be
extracted are proposed to be cut off even with or below the bottom of the seafloor.
Finally, there is the potential for a release of hydrocarbons to the marine environment when the
oil and gas lines are disconnected or cut. They are connected to Belmont Island via risers, which
extend from the seafloor to the main deck. ExxonMobil proposes to e.:cavate the rock and sand
that buries the lines where they connect to the risers, then to disconnect or cut the lines with an
oxy-arc underwater cutting torch. When the pipelines are separated, some of their contents,
including any residual hydrocarbons, will release to the marine environment.
Potential .,nshore Spills
To remove residual hydrocarbons from their interiors, the 8-inch oil pipeline, and the two 3-inch
gas pipelines will be flushed with seawater prior to decommissioning. The lines will be flushed
one at a time. Each line will be flushed from the island to the onshore property, and the flush
water will be emptied into a Baker containment tank, which will be connected to the pipeline via
a hose. If the hose were to become disconnected, it is estimated that a spill of approximately one
barrel of wastewater could occur.
Prior to disconnecting the 8-inch pipeline from Belmont Island, the applicant proposes to fill the
pipeline with approximately 3000 feet (40 cubic yards) of cement grout, from the onshore
facility to a point corresponding to approximately 15 feet MLLW offshore (or about 2000 feet
offshore from the MLLW line). The grout will displace approximately 8,000 gallons of seawater
from the line; ExxonMobil proposes to route the water back through one of the other pipelines
and collect it onshore in the same manner as the water generated by the flushing procedures. As
with the flush water, the potential exists for a spill of water from the pipeline if the hose
connecting the pipeline to the Baker tank becomes disconnected.
4.6.2.2 Oil and Gas Spill Prevention
The first test of Coastal Act section 30232 requires the applicant to provide "protection against
the spillage of crude oil, gas, petroleum products, or hazardous substances..." ExxonMobil plans
to implement a number of measures to minimize the risk of the occurrence of any hydrocarbon
spills.
Offshore Spill Prevention
To avoid anchoring impacts to the Aera-Beta pipeline, ExxonMobil has developed anchoring
plans and locations for its derrick barge and vessels, to eliminate the possibility that anchors
would be dropped on the pipeline, thus possibly damaging it. Divers will buoy the pipeline,
project personnel will not handle anchors while vessels are over the Aera-Beta pipeline, and the
derrick barge will be anchored on the southeast side of the island. In addition, all vessel
navigation systems for project vessels will be programmed to show the location of the pipeline.
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 22
Before beginning decommissioning activities, ExxonMobil personnel will conduct an inventory
of hazardous materials; any such materials identified will be disposed of following applicable
state and federal standards. As a condition of SLC's approval of this project, ExxonMobil will
develop a Materials Handling Plan for the removal, containment, transportation, treatment, and
disposal of impacted core materials. ExxonMobil has already incorporated several measures into
the project to prevent spills of this material from occurring. One is that the caisson core will not
be demolished until after the hydrocarbon-impacted fill and water is removed from it. The water
will be tested with a field screening unit and verified by a certified laboratory, and any
contaminated water will be vacuumed and placed in containers for treatment onshore. The fill
will also be tested, and will be placed in containment bins for proper disposal onshore. The bins
will be on or adjacent to the island during removal activities, to minimize the transfer of
materials over the water and thus the potential for spills from this activity. Another measure
ExxonMobil proposes is to install a containment system under the wharf decks to minimize the
possibility that demolition materials will fall into the marine environment.
There is no known way to prevent a spill from the pipelines if the pressure exerted during
flushing and grouting operations creates a leak; to prevent such a spill from being large,
however, project personnel will patrol the lines, and the operations will be shut down as soon as
any leak is detected.
To reduce the risk of accidents involving project vessels or other vessels transiting the area
which could result in a spill of oil or other hydrocarbons from the cargo or fuel tanks,
ExxonMobil will install aids to navigation on Belmont Island, establish a safety zone around the
island during decommissioning activities, and work with the U.S. Coast Guard to ensure Notices
to Mariners are issued prior to and during project operations. The aids to navigation will be
battery operated lights and a foghorn, which will be installed on the island pursuant to Coast
Guard regulations. Additional precautionary measure the applicant proposes are that the
hydrocarbon-impacted water and material from the caisson core will be transported in specially
designed containment bins, and all diesel-fired engines will be maintained and tuned to the
manufacturer's specifications.
To prevent a potential spill of hydrocarbons from the oil and gas lines as they are cut, the
applicant will first flush the lines with seawater.
Onshore Spill Prevention
During pipeline flushing, a portable, 900-gallon containment pool will be set up under the
connection point between the hose and the pipeline, and a vacuum truck will be ready to remove
any flush water from the pool. In addition, the pipeline is designed to shut down immediately,
stopping the flow through the line, if pressure is lost within it. The pipelines are proposed to be
flushed one at a time to a level until the level of total petroleum hydrocarbons (TPH) in the
pipeline is 15 ppm or less, to ensure that when the pipelines are abandoned, they will be as lean
of hydrocarbon content as possible. The level will be determined by a field screening device or
by a certified laboratory. The applicant expects that any spill from the pipelines would be
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 23
contained by the pool; however, it is possibl' chat a maximum of one barrel of wastewater could
be released to the environment.
The grouting of the 8-inch line is proposed to occur after the line is flushed; therefore the
applicant expects the TPH in the water in the line to be at or less than 15 ppm. The containment
pool and the vacuum truck are also proposed to be used during the grouting of the 8-inch
pipeline, to capture any •pill of wastewater that might occur.
The California Ocean Plan contains objectives regarding maintenance of water quality; one
objective relevant to this project is the objective that there should be no visible oil or grease. An
oil sheen tends to form on water whe:. the TPH level is approximately 15 ppm. For pipelines
associated with marine terminals prop-,sed for abandonment, it is the working policy of the SLC
(Exhibit 6) that the pipelines be flushed to a standard of less than 15 ppm of TPH. To adhere to
the Ocean Plan objective for oil and grease and to be consistent with the working policy of the
SLC on pipeline flushing, the applicant's oil and gas pipelines should be flushed to a level of less
than 15 ppm. Therefore, the Commission imposes Special Condition 3, which requires the
applicant to clean the interior of the oil and gas pipelines to a level of less than 15 ppm TPH.
The applicant does not specify the method by which the level of TPH will be verified. Field
screening methods may be used for initial determinations, however, the Commission therefore
imposes Special Condition 4, which requires that ExxonMobil document the level of TPH at the
conclusion of flushing operations using a state-certified laboratory and a test method acceptable
to the executive director. Within 30 days of completion of pipeline flushing, ExxonMobil will
provide the test results to the executive director. The Commission finds that with the imposition
of Special Conditions 3 and 4, the proposed project can be conducted in a manner that provides
for protection against the spillage of crude oil, gas, and petroleum products, as required by
section 30232 of the Coastal Act.
The Commission therefore finds the project, as conditioned, consistent with the first test of
Coastal Act section 30232.
4.6.2.3 Spill Response
The second test of section 30232 requires the applicant to provide effective containment and
cleanup equipment and procedures for accidental spills that do occur. Despite the preventive
measures proposed by ExxonMobil, the possibility remains that an oil or gas release could occur
during project operations.
Offshore Spill Response
An on-scene oil spill response team will be available to respond immediately to a spill, and the
following equipment will be maintained at the project site: one seep tent, 3 bails of sorbent pads,
600 feet of sorbent boom, one boom tender vessel, and 1,000 feet of containment boom. The
applicant estimates that this equipment is sufficient to respond to a spill of approximately 5
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PR(OUCTION COMPANY
PAGE 24 •
barrels, which would probably cover any potential offshore spill as a result of the proposed
project with the exception of the reasonable worst-case spill, the rupture of the Aera-Beta line.
To respond to and clean up a spill from the Aera-Beta line or any other spill that could not be
handled by project personnel, ExxonMobil will call upon Clean Coastal Waters ("CCW"), a
cooperative, and if more response capability is needed, will also call the Marine Spill Response
Corporation ("MSRC") to assist. Currently, ExxonMobil's membership with CCW is
suspended, but it will be renewed prior to the start of project activities. ExxonMobil has a
current service agreement with MSRC. To ensure that full oil spill response capabilities are in
place, th; Commission imposes Special Condition 5, requiring ExxonMobil to submit, prior to
permit is.. ;ance, written evidence to the executive director that, for the duration of the Belmont
Island decommissioning project, it has contracted with CCW for oil spill response and clean up
services.
A CCW initial response vessel could be at the project site in approximately 30 minutes, and the
primary response vessel, Clean Waters One, could be at the project site in approximately 45
minutes. Based in the Long Beach Harbor, CCW owns six other primary response vessels, two
recovery vessels, three barges, and four work boats. Depending on which vessel initially
responds, the equipment on board the vessel may include: 1,300 feet of Expandi Model 4300
boom, a boom reel, a power take off, a generator or other power source, a stationary or
advancing skimmer, an oil/water separator and storage tank, an offloading pump, a 2.5 ton
hydraulic crane with 15 feet of boom, sorbent pads, or sorbent booms. The primary response
vessel, Clean Waters One, is equipped with the following: 3,750 feet of Expandi Model 4300
boom, four hydraulic power packs, two LORI LORS skimming systems, two advancing skimmer
jibs with boom, two GT-185 skimmers, four offloading pumps, a 12-ton capacity hydraulic
crane, 50 feet of boom, 20 bales of sorbent pads, and 800 feet of sorbent boom.
MSRC's equipment held by a network of responders; its closest response vessel is based in Port
Hueneme. It would only be called out in the unlikely event of a major spill, and would be able to
be at the project site in approximately 7.5 hours.
When project personnel cut or separate the pipelines offshore in preparation for abandonment,
the pipelines will have been flushed to remove residual hydrocarbons. The Coastal Commission
has required in similar projects, such as in Permit No. E-98-26, that a seep tent be used to reduce
the possibility of an uncontrolled release of residual hydrocarbons. A seep tent is a steel dome-
like structure that can be placed over a flowline opening to capture a small hydrocarbon release.
The contents of the tent are then pumped via a hose onto a holding tank on the support vessel.
As a precautionary measure, the Commission is requiring in Special Condition 6 that, prior to
cutting the oil and gas pipelines offshore, ExxonMobil deploy a seep tent over each of the cut
points and provide a support vessel to capture and remove from the marine environment any
residual hydrocarbons that may be released from the lines when they are cut.
Regarding a potential spill of hydrocarbons due to the existence or removal of the creosote-
treated pilings, the applicant proposes to visually inspect the water for sheen and to collect
sediment samples adjacent to the pilings to determine if it contains creosote. Samples from three
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 25
locations will be collected, at a depth of approximately two feet below I ^ seafloor surface. The
proposal is to collect the samples using a mechanical airlift, which will place them in a pre-
cleaned 5-gallon bucket. Sample jars will be filled using the materials in the l,dckets, and will be
tested in a laboratory for volatile organic compounds and CAM-17 metals. i, contaminants are
found, the applicant proposes to continue testing the sediments to determine the extent of
contamination, and to develop a plan to remove any creosote-contaminated sediments.
Notwithstanding the conditions of this permit and the extensive oil spill containment and cleanup
equipment and services to be provided by ExxonMobil, CCW, and MSRC, the Commission finds
that the second test of Coastal Act section 30232, which requires "effective" containment and
clean-up equipment for spills that do occur, can not be met at thi, time, and thus the project is
inconsistent with the second test of Coastal Act section 30232. T-t., Commission interprets the
word "effective" to mean that spill containment and recovery equipment must have the ability to
keep spilled oil off the coastline. Unfortunately, the state-of-the-art oil spill response is such that
no equipment currently available has the capability to recover all oil from large spills, and often
even small spills, in the open ocean. For example, mechanical skimming devices typically
remove less than 20% of the spilled petroleum in a large spill (National Research Council 1989).
Nevertheless, the project can be found consistent with the Coastal Act under the section 30260
coastal-dependent industrial provision for the reasons discussed in section 4.6.7 of this report.
Onshore Spill Response
ExxonMobil proposes to have a team of personnel onsite to respond to and clean up any spill that
could occur on shore during line flushing or grouting procedures, and estimates that the
maximum spill that could occur onshore is one barrel. The equipment available on site to clean
up a spill will be a vacuum truck, a backhoe and sorbent pads, and is sufficient to effectively
clean up a project-related onshore spill.
The Commission finds that, for accidental spills on shore, the proposed project is consistent with
the second requirement of Coastal Act section 30232.
4.6.3 Commercial and Recreational Fishing
Coastal Act § 30234.5 states:
The economic, commercial, and recreational importance of fishing activities shall be
recognized and protected.
Commercial fishing does not occur at the project area and therefore will not be impacted by
decommissioning activities. Although Belmont Island is surrounded by a U.S. Coast Guard 200-
foot preclusion area, recreational fishing has been known to occur at the island. The
Commission thus recognizes that removal of the island will eliminate this recreational fishing
site. However, the express purpose of the island was exclusively for oil and gas extraction and
not fisheries and/or recreational enhancement. The SLC requires the operator as part of the lease
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 26
termination or quitclaim process to restore the site back to its pre-development condition.
Therefore, sports fishermen that have successful) , fished at the island over the years derived an
incidental economic and/or recreational benefit from the placement of the rip-rap, pilings and
other structures on the seafloor.
The Commission thus t nds the project consistent with Coastal Act section 30234.5.
4.6.4 Public Access and Recreation
Coastal Act § 30210 states:
In carrying out the requirement of Section 4 of Article X of the California Constitution,
maximum access, which shall be conspicuously posted, and recreational opportunities
shall be provided for all people consistent with public safety needs and the need to protect
public rights, rights of private property owners, and natural resources from overuse.
Coastal Act § 30211 states:
Development shall not interfere with the public's right of access to the sea where acquired
through use or legislative authorization, including, but not limited to, the use of dry sand and
rocky coastal beaches to the first line of terrestrial vegetation.
Belmont Island is approximately 8,100 feet offshore of the City of Seal Beach. Recreational uses
of this area of the coast include boating,jet skiing, fishing, diving and snorkeling. General boating
and jet skiing activities may be temporarily affected by the activities associated with island
decommissioning particularly due to increased vessel traffic in the area. However, such impacts
will be minor and short-term. The applicant proposes to issue through the U.S. Coast Guard in
advance of the start of decommissioning activities a Notice to Mariners so that boaters and other
ocean users will be adequately notified of project operations.
Removal of the island will affect those recreational users that currently use the island for fishing.
However, as discussed above in section 4.6.3 of this report, Belmont Island was installed as a
human-made oil and gas production island only and any benefits that may have accrued to
recreational users over the life of the island have been incidental.
ExxonMobil retains a private parking area within the marina and therefore no public parking spaces
will be occupied by project-related vehicles during the decommissioning project. All staging and
stockpiling of materials and equipment will occur at ExxonMobil's onshore facility or at the Long
Beach Harbor. No decommissioning activities will interfere with the public's access to and the
ability to recreate at the beach.
The applicant also proposes to abandon in place four pipelines and one power cable that are
currently buried 4 to 9 feet below the surface of the seafloor and ground. To remove the pipelines
and cable would require extensive onshore and offshore excavation and could cause significant
public access and recreation impacts due to beach closures and near-shore construction activities.
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 27
Any future exposure of the pipelines and cable on the beach or in the near-shore area could,
however, cause a hazard to beach and recreational users. The pipelines and cable are unlikely ever
to be uncovered because they are located in a high depositional offshore environment and have
never been exposed. However, in the event that they are exposed in the future, the Commission is
requiring in Special Condition 7 that if any of the facilities (i.e., four pipelines and the power
cable) become exposed to the natural (i.e., air or aquatic) environment, the executive director will
schedule for the Commission's consideration the question of whether removal ,,f the facilities may
be necessary to mitigate individual or cumulative adverse impacts to coastal resources. If the
Commission agrees that the facilities should be removed, ExxonMobil shall, w,thin 60 days of such
a determination, submit a plan for removal of such facilities in the form of an application to amend
this permit.
The Commission thus finds that the project, as conditioned, will not adversely impact recreational
users or public access to the beach and is therefore consistent with Coastal Act sections 30210 and
30211.
4.6.5 Visual Resources
Coastal Act § 30251 states, in part:
The scenic and visual qualities of coastal areas shall be considered and protected as a
resource of public importance. Permitted development shall be sited and designed to protect
views to and along the ocean and scenic coastal areas, to minimize the alteration of natural
land forms, to be visually compatible with the character of surrounding areas, and, where
feasible, to restore and enhance visual quality in visually degraded areas.
During the eight-month project duration a derrick barge and crew and supply boats will be
operating at the project site and traveling to and from their ports of origin (either Long Beach or
Los Angeles). Operations will be visible; however, since the island is about 8,100 feet offshore,
decommissioning operations will not be a major element of the viewshed as seen from shore. The
project will therefore not result in significant adverse short-term visual impacts and will enhance
the long-term visual quality of this area of the coast when the industrial human-made structure is
removed.
The Commission thus finds the proposed project consistent with the scenic and visual goals of
Coastal Act section 30251.
4.6.6 Air Quality
Coastal Act § 30253(3) states:
New development shall be consistent with requirements imposed by the air pollution
control district or the State Air Resources Control Board as to each particular
development.
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 28
The MND states that the use of equipment, vessels, and vehicles for project operations will result
in criteria pollutant emissions, including nitrogen oxides (NOx,), reactive org-.nic compounds
(ROC), particular matter less than ten microns in size (PMIo),sulfur oxides kSOx), carbon
monoxide (CO), and toxic pollutant emissions, such as formaldehyde, acetaldehyde, 1,3-
butadiene, and benzene. The sources of project air emissions include cranes; winches;
generators; forklifts; pumps; welders; air compress )rs; concrete saws; a vibratory extractor;
diesel-fueled internal combustion engines on the dive vessel; two tug boats; crew boats;
employee transportation vehicles; and heavy-duty iiauling trucks. During removal of
hydrocarbon-contaminated fill material in the caisson core, there is the potential that some
fugitive low-volatility hydrocarbons could be released to the ati ...)sphere. In addition, a minimal
amount of fugitive dust will be generated during concrete sawing and material removal activities
on the island.
The MND states that ten of the proposed project activities are projected to exceed daily and
quarterly NOx emissions, and concludes that the project will thus have a significant air quality
impact. To minimize criteria pollutant emissions, Exxon Mobil will comply with all
requirements of the SCAQMD (Rules 401, 402, 404, 431.2, 1110.2).
The applicant proposes the following mitigation measures (of these, the first four were
incorporated by the SLC into its Mitigation Monitoring Program):
• maintain all diesel engines in good condition and keep them properly tuned to the
manufacturer's specifications;
• retard engine timing four degrees for all internal combustion engines, when feasible, to
reduce NOx emissions 20-30%;
• limit the number of diesel engines operating at any one time;
• suspend project activities when necessary during health advisories or Stage 1 smog alerts;
• cool the concrete saws with water during cutting activities to minimize fugitive dust; and
• use only equipment that has a valid operating permit from the SCAQMD or is registered
under the California Statewide Portable Equipment Registration Program.
Regarding fugitive low-volatility hydrocarbons that could be generated by the project, the
amounts are projected to be minimal and unquantifiable. ExxonMobil proposes to conduct all
waste removal, transportation and disposal activities in compliance with the SCAQMD's Rule
1166, which governs volatile organic compound emissions from decontamination of soil.
SCAQMD staff will review the proposed project to determine if air quality permits will be
required for decommissioning activities and project equipment, and if mitigation measures
beyond those contained in the MND are necessary to offset project-related air quality impacts.
Therefore, the Commission is imposing Special Condition 8, which requires the applicant, prior
to issuance of this permit, to submit to the executive director copies of the permit(s) issued by the
SCAQMD for the decommissioning project and project equipment; and written evidence of
mitigation measures, if any, the SCAQMD is imposing to offset project-related air quality
impacts. If the SCAQMD is not requiring permits or mitigations for this project, the applicant
shall submit to the executive director written evidence of a waiver for this project from the
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 29
SCAQMD. As conditioned, the Coastal Commission finds that the proposed project is consistent
with section 30253(3) of the Coastal Act, which requires that a development project must be
consistent with a local air district's requirements.
4.6.7 Coastal-Dependent "Override" Provision
Section 30101 of the Coastal Act defines a coastal-dependent development or use as that which
"requires a site on or adjacent to the sea to be able to function at all." Ports, commercial fishing
facilities, and offshore oil and gas developments (e.g., the decommissioning of an offshore oil
and gas production island) are examples of development considered "coastal dependent" under
section 30101.
In section 30260, the Coastal Act further provides for special approval of coastal-dependent
industrial facilities that are otherwise found inconsistent with the resource protection and use
policies contained in Chapter 3 of the Coastal Act. The decommissioning of Belmont Island
qualifies as a "coastal-dependent industrial facility." Coastal-dependent industrial facilities must
first be evaluated under all applicable Chapter 3 policies. If the proposed project does not meet
one or more of these policies, the development can then be analyzed under the three
requirements of section 30620 of the Coastal Act. Coastal Act § 30260 specifically states:
Coastal-dependent industrial facilities shall be encouraged to locate or expand within
existing sites and shall be permitted reasonable long-term growth where consistent with
this division. However, where new or expanded coastal-dependent industrial facilities
cannot feasibly be accommodated consistent with other policies of this division, they may
nonetheless be permitted in accordance with this section and section 30261 and 30262 if
(1)alternative locations are infeasible or more environmentally damaging; (2) to do
otherwise would adversely affect the public welfare; and(3)adverse environmental effects
are mitigated to the maximum extent feasible.
As described in section 4.6.2 of this report, ExxonMobil's proposed project does not meet the
standards of section 30232 due to the significant impacts that could be caused by an accidental
offshore oil spill. Since the project qualifies as a "coastal-dependent industrial facility" the
Commission may nevertheless approve the project if the three requirements of section 30260 can
be met.
4.6.7.1 Alternative Locations
The Coastal Commission may approve the proposed development if notwithstanding the
project's inconsistency with one or more policies of Chapter 3 it finds that alternative project
locations are infeasible or more environmentally damaging. The proposed project is to
decommission an existing offshore artificial oil and gas production island. Since this project
involves removal and abandonment-in-place of existing facilities, the issue of whether the
project is sited in the least environmentally damaging location is not applicable. Therefore the
proposed project is consistent with the first test of section 30260.
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 30
4.6.7.2 Public Welfare
The second test of Coastal Act section 30260 states that non-conforming coastal-dependent
industrial development may be permitted "if to do otherwise would adversely affect the public
welfare." The test requires more than a finding that, on balance, a project as p oposed is in the
interest of the public. It requires that the Coastal Commission find that there %,'ould be a
detriment to the public welfare were the Coastal Commission to deny a permit for the project.
The proposed project involves the decommissioning of an existing offshore artificial oil and gas
production island and its associated wells as required by State Lands Commission oil and E,..s
lease provisions. Improperly abandoned wells could potentially cause a h!'drocarbon relea. into
marine waters. To deny the project would also mean that the shut-in industrial facility will be
left in place and cause adverse long-term shoreline visual impacts. Thus, denial of the project
may be detrimental to the public's welfare.
However, in addition to determining whether a refusal to allow the project to be carried at all
would adversely affect the public welfare (which the Commission has answered in the
affirmative), the Commission must also determine whether a refusal to allow the project to be
carried out precisely in the manner proposed by the applicant would adversely affect the public
interest.
In previous sections of these findings, the Commission has identified the valuable public policy
goals that will be furthered by imposing additional mitigation measures. The question thus
becomes whether the conditions of this permit which impose additional mitigation upon the
applicant will have an adverse effect on the public interest. The applicant has made no showing
that such requirements are financially or otherwise infeasible. Therefore, the Commission finds
that the proposed project, as conditioned by this permit, will not have an adverse effect on the
public welfare. The proposed project is therefore consistent with the second test of section
30260.
4.6.7.3 Maximum Feasible Mitigation
The third test in section 30260 requires a finding that the adverse environmental impacts of a
proposed project have been mitigated to the maximum extent feasible. As discussed in section
4.6.2 of this report, the Commission has determined that the project is inconsistent with Coastal
Act section 30232 due to the potential for and resulting impacts of an offshore oil spill.
However, upon the applicant's acceptance of this permit, as conditioned, the Commission can
find that the environmental impacts generated by this project have been mitigated to the
maximum extent feasible.
5.0 California Environmental Quality Act
As "lead agency" under CEQA, the State Lands Commission certified in December 1999 a
mitigated Negative Declaration for ExxonMobil's Belmont Island Decommissioning Project.
CC ' APPLICATION E-99-01
APPLICAI'T: EXXONMOBIL PRODUCTION COMPANY
PACE 31
The Commission's permit process has also been designated by the State Resources Agency as
the finctional equivalent of the CEQA environmental impact review process. Pursuant to section
1P60.5(d)(2)(A) of the CEQA and section 15252(b)(1) of Title 14, California Code of
Regulations, the Commission may not approve a development project "if there are feasible
alternatives or feasible mitigation measures available which would substantially lessen any
significant adverse impact which the activity may have on the environment." The Commission
finds that there are no feasible less environmentally damaging alternatives or additional feasible
mitigation measures that would substantially lessen any significant adverse impact which the
activity may have on the environment, other than those identified herein. Therefore, the
Commission finds that the project is consistent with the provisions of the CEQA.
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 32
APPENDIX A
Standard Conditions
1. Notice of Receipt and Acknowledgment. The permit is not valid and development shall not
commence until a copy of the permit, signed by the permittee or authorized agent,
acknowledging receipt of the permit and acceptance of the terms and conditions, is returned
to the Commission office.
2. Expiration. If development has not commenced, the permit will expire two years from the
date on which the Commission voted on the application. Development shall be pursued in a
diligent manner and completed in a reasonable period of time. Application for extension of
the permit must be made prior to the expiration date.
3. Compliance. All development must occur in strict compliance with the proposal as set forth
in the application for permit, subject to any special conditions set forth below. Any
deviation from the approved plans must be reviewed and approved by the staff and may
require Commission approval.
4. Interpretation. Any questions of intent of interpretation of any condition will be resolved by
the Executive Director or the Commission.
5. Inspections. The Commission staff shall be allowed to inspect the site and the development
during construction, subject to 24-hour advance notice.
6. Assignment. The permit may be assigned to any qualified person, provided assignee files
with the Commission an affidavit accepting all terms and conditions of the permit.
7. Terms and Conditions Run with the Land. These terms and conditions shall be perpetual,
and it is the intention of the Commission and the permittee to bind all future owners and
possessors of the subject property to the terms and conditions.
CDP APPLICATION -99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 33
APPENDIX B
Substantive File Documents
Leck, Tim, M.A., Secretary, Heal the Harbor, Inc. 1999. Letter to the Executive Director,
California Coastal Commission, dated December 6, 1999.
Brow;i, Dave. 2000. Copper in the Environment. Published on the Internet at
http://www.science.mcmaster.ca/Biology/4503/COPPER.HTM.
California Coastal Commission. Coastal Development Permit 3-97-078 (Port San Luis Harbor
District Maintenance Dredging and Disposal and Repair and Maintenance of Harbor
Structures); Consistency Certification CC-81-95 (California Department of Fish and Game
Bolsa Chica Artificial Reef); Coastal Development Permit Waiver—De Minimis E-99-03-W
(Exxon Company U.S.A. Belmont Island Well Flushing and Conductor Cutting); and E-99-
12-W (Exxon Company Seal Beach Onshore Facility Building Demolition and Removal).
California State Lands Commission. 1999a. Initial Study and Negative Declaration for Belmont
Island Decommissioning Project. March 1999.
California State Lands Commission. 1999b. Calendar Item 76. Reconsider Adoption of
Mitigated Negative Declaration and Consider Approval of the Abandonment and Removal of
and Oil and Gas Drilling and Production Man-Made Island, Belmont Field, Orange County.
December 3, 1999.
Dawson, Scott A., Planning Section, California Regional Water Quality Control Board, Santa
Ana Region. 1999. Letter to Goodyear Walker, California State Lands Commission, dated
May 4, 1999.
De Wit, L.A., Consultant. 1999. Belmont Island Decommissioning Marine Biological Survey.
Prepared for Padre Associates. July 1999.
Dugas, Brian G., Project Manager, Padre Associates, Inc. 1999. Letter to Ms. Lilli Ferguson,
Coastal Program Analyst, California Coastal Commission, dated May 7, 1999.
Exxon Company, U.S.A. 1999. Project Execution Plan for Belmont Island Decommissioning
Project. Prepared with the assistance of Padre Associates, Inc. and Longitude 123. March
1999.
Cr)P APPLICATION E-99-01
AF'LICANT: EXXONMOBIL PRODUCTION COMPANY
PA ;E 34
Fugro West, Inc. 1996. Preliminary Environmental Assessment, Belmont Island Facility,
Offshore of Seal Beach, Orange County, California.
Garcia, Linda C., Associate WRC Engineer—Planning, California Regional Water Quality
Control Board, Santa Ana Region. 1999. Letter to Mr. Tim Cagle, Exxon Company, U.S.A.,
dated May 3, 1999.
Gregory, Gary L., Assistant Executive Officer and Chief, Marine Facilities Division, California
State Lands Commission. 1999. Letter to Mr. Joe Gonzalez, Estero Marine Terminal, dated
March 8, 1999.
Hebert, Donna M., Project Manager, Padre Associates. 1999. Letter to Mr. Russ Kaiser, U.S.
Army Corps of Engineers. Dated May 25, 1999.
Kaiser, Russ, Regulatory Branch, Los Angeles District, U.S. Army Corps of Engineers. 1999.
Fax to Ms. Lilli Ferguson, Coastal Program Analyst, California Coastal Commission, dated
August 16, 1999.
National Research Council. 1989. Using Oil Dispersants on the Sea. National Academy Press:
Washington, DC.
Schubel, Richard J., Chief, Regulatory Branch, Los Angeles District, U.S. Army Corps of
Engineers. 1999. Letter to Mr. Tim Cagle, Exxon Company U.S.A., dated April 27, 1999.
Stewart, Gary, Chief, Regulations Section, California Regional Water Quality Control Board,
Santa Ana Region. 1999a. Letter to Mr. Tim Cagle, Exxon Company U.S.A., dated May 6,
1999.
Stewart, Gary, Chief, Regulations Section, California Regional Water Quality Control Board,
Santa Ana Region. 1999b. Letter to Ms. Donna M. Hebert, Project Manager, Padre
Associates, Inc., dated June 23, 1999.
Weber, Mike, Environmental Specialist, Padre Associates, Inc. 1999a. Letter to Ms. Lilli
Ferguson, Coastal Program Analyst, California Coastal Commission, dated December 17,
1999.
Weber, Mike, Environmental Specialist, Padre Associates, Inc. 1999b. Letter to Ms. Lilli
Ferguson, Coastal Program Analyst, California Coastal Commission, dated December 30,
1999.
CDP APPLICATION E-99-01
APPLICANT: EXXONMOBIL PRODUCTION COMPANY
PAGE 35
Weber, Mike, Environmei. al Specialist, Padre , •sociates, Inc. 2000. Letter to Ms. Lilli
Ferguson, Coastal Program Analyst, California Coastal Commission, dated January 7, 2000.
Zukor, Ryan M. and Alan E. Emslie, P.E., Senior Principal, Padre Associates, Inc. 1999. Letter
and report to Mr. Tim Cagle, ExxonMobil Production Company, documenting concrete
cc ring activities and lab natory analyses, Belmont Island facility, dated December 30, 1999.
•
: _ z
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E,` HIBIT 2
ExxonMobil Prc suction Company
SUBSEA POWER CABLE ,
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BELMONT ISLAND DECOMMISSIONING PROJECT
E)KON
FIGURE 1.2-3 PLAN VIEW & EAST ELEVATION
Healing The Harbr •s, Bettering T • Bays And Optimizing The Ocean:
December 6 , 1999
f
`illy. .�i
seal Ile evreair, 7ptc.
P.O. Box 3182
,s4 Manhattan Beach,CA 90266
www.healtheharbor.org. (310)329-3824
RECEIVED
-4)1
DEC 1 01999
CAUFORMA
4WASTALCZASIISI-.
At
Executive Director EXHIBIT 3
California Coatal Commission
45 Fremont Street E-99-01
San Francisco, CA 94105
ExxonMobil Production Company
Dear Coastal Commission Exectutive Director:
Heal the Harbor, Inc. is a public benefit, non profit, non
stock California Corporation incorporated for educational , charitable
and environmental purposes. While Heal the Harbor is interested in
cleaning up the dirtiest water (the harbors ) first , we recognize that
artificial islands like Belmont Island 1 . 5 miles off the Coast near
Long Beach Harbor acts as a compensation to the benefit of the
environment for the detriment caused by Long Beach Harbor. For this
and other reasons for the benefit of the marine environment , Heal the
Harbor, Inc. will assume legal ownership and legal liabilty for boating
and diving accidents off Belmont Island should the Coastal Commission
approve a plan whereby ExxonMobil would deed the property to Heal the
Harbor, Inc. and donate 50%-75% of the dismantling costs to a Heal the
Harbor, Inc. Trust Fund for the Island' s maintenance, legal liabilities
and adminstration. Interest on the Trust Fund would be used to keep the
fund at its initial sum with any monies over the initial sum being
used for research and other environmental public benefit programs .
The CFO of Heal the Harbor, Inc. is an accountant and is licensed
before the IRS. Dr. Rimmon C. Fay, Ph.D. , noted biologist , diver and
former California Coastal Commissioner would be hired as project
scientist as he is in our opinion the best and most qualified
world renoun scientist to head the project and gain more information
on the "Rigs to Reefs" question, in general.
•
Enclosed along with this letter is a copy of a Los Angeles Times
article of December 4 , 1999 for reference and a copy of a draft
proposal from Heal the Harbor, Inc. to Mr. Lee Raymond, CEO of Exxon.
e
Enclosures : as stated on -
•
im Beck, M.A. Secretary
Heal the Harbor, Inc.
I 1‘..G1111 1& 111%.• I Mui u JI.7, 1.7c-[cc1III UUyJ P11IU I!ILIIIli, 1 IIC VLCQ0
COPY DRAFT PROPOSAL
:: ‘
Dece,,ber 6 , 1999
41111111
't'' eae 74e Vlevretvr,
ler IV. P.O. Box 3182
Manhattan Beach, CA 90266
www.heaftheharbor.org. (310)3?9-3824
Mr. Lee Raymond, President and CEO
The Exxon Corporation
5959 Las Colinas Boulevard
Irving, Texas 75039-2298
Dear Mr. Raymond:
Thank you very much for reading and responding to this letter
and the draft proposal which it represents to the benefit of Exxon
and the environment. Heal the Harbor, Inc. is a non profit , non stock
public benefit corporation incorporated in California in 1997.
According to the Los Angeles Times December 4, 1999 (article
enclosed for reference) ExxonMobil owns Belmont Island 1.5 miles off
Long Beach, California and must pay $25-$30 million to dismantle this
artificial island and move the rocks and concrete to the State owned
reef at Bolsa Chica. According to Dr. Rimmon C. Fay, Ph.D. world
renoun biologist and former California Coastal Commissioner, Bellmont
Island is an environmental productive asset and should be preserved
if possible. Heal the Harbor, Inc. is willing to assume legal liability
for Bellmont Island as is or in a more bioproductive or in such conditio
as to improve navigation or reduce boating or diving accidents.
The majority of the Board of Heal the Harbor, Inc. would be willing
to assume the ownership and legal responsibilty and liability for
boating and diving accidents at Belmont Island, should ExxonMobil deed
the property to Heal the Harbor, Inc. and transfer $15 million in
U.S_ Funds or ExxonMobil stock to Heal the Harbor, Inc . to be held
in a trust account for maintenance, liability and adminstration.
Interest on the Trust Fund could be used for research. and other
public benefit purposes should the Fund exceed $15 million. This
propsal will save ExxonMobil $10 to $15 million in dismanteling costs .
Thank you very much for considering this proposal . With best
wishes that Exxon Mobil and Heal the Harbor, Inc. can work together
to serve the environment as well as the Stock Holde the best
ways possible.
*,'CC: California Coastal Commission imothy A. Beck, M.A.
Dr . Rimmon C. Fay, Ph.D.
Secretary
Michtal Parks , L.A. Times
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C,alliornia Regional water Quality Control tsoarci .e._
Santa Ana Region -
Winston H. Hickox Interne Addrms: hap://www.r•rrtb.ce.sovi-ewqcb8 Gray Davis
Secretary for 3737 Max Stree;Suite 500,Rive^ude,California 92101.3339
Env rcnrnenr.:: P1orc(909)78:-130 • F. 7111.62111Y(909) Governor
Prorecnon
May 6, 1999 EXHIBIT 4
Tim Cake E-99-01
E:oxon Company, USA ExxonMobil Production Company
800 Bell, 14th Floor
Houston, TX 77002
EXXON BELMONT ISLAND DECOMMISIONT G PROJECT- SEAL BEACH, ORANGE COUNTY,
CALIFORNIA
Dear Mr. Cagle:
On April 21, 1999, Padre Associates, Inc. submitted on your behalf an application for a Section 401 Water
Quality Certification for the above-referenced project. The U.S. Army Corps of Fngineers intends to issue
a Letter of Permission to the project thereby negadng the issuance of a 401 Certification.
The proposed project will involve demolition and dredging within navigable waters of the U.S. which will
create a plume of turbid water. The plume will be of short duration and will result to a minimal and
temporary impact on water quality. As such, this project does not need to be regulated under waste
discharge requirements
This Ietter constitutes our conditional clearance for this project. Should any conditions change from those
stated in your submittal, this clearance may be revoked, and you must notify this office irnrnrdiaro5ly to
determine a further course of action. Please be aware that this clearance does not relieve you of the
responsibility to comply with the laws and guidelines of other regulatory agencies involved with this
project.
If you have any questions, please call Jun Marsrez at(909) 782-3258.
ly,
11111111111.
S • �
Regulations S 'on
Cc: U.S. EPA, Wetlands and Sediment M,nagement Section -Jerry Bock (WTR-10)
U.S. Army Corps of Engineers -Russ Kaiser
State Water Resources Control Board-John Youngerman
Padre Associates, Inc. - Donna M. Hebert
California Environmental Protection Agency
j .4ecyeld?::e
99 15:51 NO.096 D63
California R;; 'tonal Water Quality C :ntrol Board _ •
Santa Ana Region
stCt1 (1ICkOn Interna Address: At3p:!/syvew Ikreb,ce.pv!—rwgebi Gray Dr l5
Secretor).At 3737 Main Street,Suits 300,Riverside.California 92501.3339 Gown.
6irv110111urataf Piicnc(909)782.4130•FAX(909)761-6281
Pramul on
June 23, 1999 EXHIBIT 5
Donna M. Hebert E-99-01
Project Manager ExxonMobil Production ';ompany
Padre Associates, Inc.
5450 Telegraph Road, Suite 101
Ventura, CA 93003
EXXON BELMONT ISLAND DECOMMISSIONING PROJECT - MARINE GROWTH
REMOVAL
Dear Ms. Hebert:
This is in response to your June 7, 1999 letter regarding the above-referenced project You are
requesting approval to allow the marine growth to fall into the ocean bottom after being removed
from the caisson walls and other structural members below the water surface. This procedure is
preferred to prevent the occurrence of significant odors and solid waste disposal issues that could
result if removal and disposal of marine growth were done elsewhere.
We have no objection to the proposal of allowing the removed marine growth to fall into the
ocean bottom, provided that adequate measures to minimize any impacts to the receiving water
are undertaken.
If you have additional questions, please call Jun Martirez at (909) 782-3258 or me at (909) 782-
4379.
•
Sincerely,
•
Gary Ste Chief
Regulations Section
RECEIVED
•
cc: Tn. A toyCorpa.afF.rlgiuocra us aisle_ JUN2 8 1999
Exxon Company,USA-Tim Cagle
REG ULATO RY BRANCH
Cal41ornia Environmental Protection.4 r ency
0 R.cyd•d? *
.ar. � yr ..rurVKNIA
GRAY DAVIS. Governor
CALIFOR• :IA STATE LANDS COMMISSION
330 Golden Shire, Suite 210 ROBERT C. HIGHT, Executive Officer
II
Long Beach, Ci 90802-4246 California Relay Servrce from TDD Phc a 1-800-735.2922
from Voice Phon, 1-800-735-2929
Contact Phone: (562)499-6312
�; Contact FAX (562)499-6317
triZ .
.. --L—
EXHIBIT 6
March 8, 1999 E-99-01
ExxonMobil Production Company
Mr. Joe Gonzalez _ File Ref: W 9777.4
Estero Marine Terminal
4000 Highway One
Morro Bay, CA 93442
Dear Mr. Gonzalez:
This letter is in response to recent correspondence regarding your application for
partial abandonment of the Estero Marine Terminal. It appears that there is some
confusion regarding the standards required for pipeline flushing and subsequent
verification that those standards have been met. I would like to clarify the Marine
Facilities Division working policy on this issue.
Under the Lempert-Keene-Seastrand Oil Spill Prevention and Response Act of
1990, amended (the Act), the California State Lands Commission has specific authority
to adopt rules, regulations, guidelines, and leasing policies for existing and proposed
manne terminals with the state, whether or not on lands leased from the commission,
and all other marine facilities on lands under lease from the commission to minimize the
possibilities of a discharge of oil. Further, these rules, regulations, guidelines and
leasing policies shall provide the best achievable protection of the public health and
safety and the environment (Sec. 6755).
In keeping with this mandate, the Marine Facilities Division (MFD) has adopted
the policy that "All pipelines associated with Marine Oil Terminals, located on lands
leased from the commission, shall, upon entering into caretaker status or in preparation
for abandonment, be flushed with water, in order to remove residual oil and grease, to a
standard of less than 15 ppm of Total Petroleum Hydrocarbon (TPH). Furthermore, the
concentration of oil and grease remaining in the pipeline water will be quantitatively
verified by a certified laboratory using approved analytical procedures. Official
laboratory test results and the chain of custody logs will be made available to Marine
Facilities Division personnel upon completion of pipeline flushing operations."
- ;;C";?g.:
Belmont Island Decommissioning Project - Permit No. E-99-01
Comment Letter re: Coastal Commission Consideration
City Council Staff Report
February 14, 2000
ATTACHIVIENT 3
LIST OF ACRONYMS
ACOE U.S. Army Corps of Engineers
BCAR Bolsa Chica Artificial Reef
CDFG California Department of Fish and Game
MLLW mean low lower water
MND Mitigated Negative Declaration
ppm parts per million
RWQCB Regional Water Quality Control Board, Santa Ana Regional
office
SCAQMD South Coast Air Quality Management District
SLC California State Lands Commission
* * * *
Belmont Wand Decommissioning.CC SR 10