National Oil and Hazardous Substances Pollution Contingency Plan; National Priorities List: Partial Deletion of the El Toro Marine Corps Air Station Superfund Site, 69302-69310 [2013-27724]
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Federal Register / Vol. 78, No. 223 / Tuesday, November 19, 2013 / Rules and Regulations
emission limits.’’, 3745–18–61 ‘‘Miami
County emission limits.’’, 3745–18–62
‘‘Monroe County emission limits.’’,
3745–18–63 ‘‘Montgomery County
emission limits.’’, 3745–18–64 ‘‘Morgan
County emission limits.’’, 3745–18–65
‘‘Morrow County emission limits.’’,
3745–18–66 ‘‘Muskingum County
emission limits.’’, 3745–18–67 ‘‘Noble
County emission limits.’’, 3745–18–68
‘‘Ottawa County emission limits.’’,
3745–18–69 ‘‘Paulding County emission
limits.’’, 3745–18–70 ‘‘Perry County
emission limits.’’, 3745–18–71
‘‘Pickaway County emission limits.’’,
3745–18–72 ‘‘Pike County emission
limits.’’, 3745–18–73 ‘‘Portage County
emission limits.’’, 3745–18–74 ‘‘Preble
County emission limits.’’, 3745–18–75
‘‘Putnam County emission limits.’’,
3745–18–76 ‘‘Richland County emission
limits.’’, 3745–18–77 ‘‘Ross County
emission limits.’’, 3745–18–79 ‘‘Scioto
County emission limits.’’, 3745–18–81
‘‘Shelby County emission limits.’’,
3745–18–83 ‘‘Summit County emission
limits.’’, 3745–18–84 ‘‘Trumbull County
emission limits.’’, 3745–18–85
‘‘Tuscarawas County emission limits.’’,
3745–18–86 ‘‘Union County emission
limits.’’, 3745–18–87 ‘‘Van Wert County
emission limits.’’, 3745–18–88 ‘‘Vinton
County emission limits.’’, 3745–18–89
‘‘Warren County emission limits.’’,
3745–18–91 ‘‘Wayne County emission
limits.’’, 3745–18–92 ‘‘Williams County
emission limits.’’, 3745–18–93 ‘‘Wood
County emission limits.’’, 3745–18–94
‘‘Wyandot County emission limits.’’,
adopted on February 7, 2011, effective
February 17, 2011.
(B) February 7, 2011, ‘‘Director’s Final
Findings and Orders’’, signed by Scott J.
Nally, Director, Ohio Environmental
Protection Agency, adopting the rules
identified in paragraph (160)(i)(A) of
this section.
(C) Ohio Administrative Code Rules
3745–18–01 ‘‘Definitions and
incorporation by reference.’’, 3745–18–
54 ‘‘Lucas County emission limits.’’,
3745–18–82 ‘‘Stark County emission
limits.’’, adopted on March 24, 2011,
effective April 3, 2011.
(D) March 24, 2011, ‘‘Director’s Final
Findings and Orders’’, signed by Scott J.
Nally, Director, Ohio Environmental
Protection Agency, adopting the rules
identified in paragraph (160)(i)(C) of
this section.
■ 3. Section 52.1881 is amended by
revising paragraph (a)(4) to read as
follows:
§ 52.1881 Control strategy: Sulfur oxides
(sulfur dioxide).
(a) * * *
(4) Notwithstanding the portions of
this section that EPA has either
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disapproved or taken no action on, EPA
has approved a complete plan
addressing all counties in the State of
Ohio. In addition, specific approved
rules are listed in § 52.1870.
*
*
*
*
*
[FR Doc. 2013–27561 Filed 11–18–13; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 300
[EPA–HQ–SFUND–1910–0010; FRL 9902–
79–Region 9]
National Oil and Hazardous
Substances Pollution Contingency
Plan; National Priorities List: Partial
Deletion of the El Toro Marine Corps
Air Station Superfund Site
Environmental Protection
Agency.
ACTION: Direct final rule.
AGENCY:
The Environmental Protection
Agency (EPA) Region IX is publishing a
direct final Notice of Deletion of
portions of the El Toro Marine Corp Air
Station Superfund Site (Site), located in
Irvine, California, from the National
Priorities List (NPL). The NPL,
promulgated pursuant to section 105 of
the Comprehensive Environmental
Response, Compensation, and Liability
Act (CERCLA) of 1980, as amended, is
an appendix of the National Oil and
Hazardous Substances Pollution
Contingency Plan (NCP). This direct
final partial deletion is being published
by EPA with the concurrence of the
State of California through the
Department of Toxic Substances Control
(DTSC), because EPA has determined
that all appropriate response actions at
these identified parcels under CERCLA
have been completed. However, this
partial deletion does not preclude future
actions under Superfund.
This partial deletion pertains to all
Site media, including soil and
groundwater, of parcels I–A, II–A, III–A,
II–J, II–Q, II–S, II–T, III–C, I–C, II–U, I–
B, I–E, I–G, I–H, I–I, I–J, I–L, I–M, I–P,
II–G, II–I, II–P, III–D, I–K, I–N, I–O, I–
S, II–E, II–L, II–M, II–R, I–Q, I–R, II–B,
II–K, and II–O of the Site. The current
remaining areas of the Site will remain
on the NPL and are not being
considered for deletion as part of this
action.
DATES: This direct final partial deletion
is effective January 21, 2014 unless EPA
receives adverse comments by
December 19, 2013. If adverse
comments are received, EPA will
publish a timely withdrawal of the
SUMMARY:
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direct final partial deletion in the
Federal Register informing the public
that the partial deletion will not take
effect.
Submit your comments,
identified by Docket ID no. EPA–HQ–
SFUND–1910–0010, by one of the
following methods:
• https://www.regulations.gov. Follow
on-line instructions for submitting
comments.
• Email: Aycock.Mary@epa.gov.
• Fax: (415) 947–3528.
• Mail: Mary Aycock, U.S. EPA
Remedial Project Manager, U.S.
Environmental Protection Agency,
Region IX, Mail Code SFD–8–1, 75
Hawthorne Street, San Francisco, CA
94105.
• Hand delivery: Mary Aycock, U.S.
EPA Remedial Project Manager, U.S.
Environmental Protection Agency,
Region IX, Mail Code SFD81, 75
Hawthorne Street, San Francisco, CA
94105. Such deliveries are only
accepted during the Docket’s normal
hours of operation, and special
arrangements should be made for
deliveries of boxed information.
Instructions: Direct your comments to
Docket ID no. EPA–HQ–SFUND–1910–
0010. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through https://
www.regulations.gov or email. The
https://www.regulations.gov Web site is
an ‘‘anonymous access’’ system, which
means EPA will not know your identity
or contact information unless you
provide it in the body of your comment.
If you send an email comment directly
to EPA without going through https://
www.regulations.gov, your email
address will be automatically captured
and included as part of the comment
that is placed in the public docket and
made available on the Internet. If you
submit an electronic comment, EPA
recommends that you include your
name and other contact information in
the body of your comment and with any
disk or CD–ROM you submit. If EPA
cannot read your comment due to
technical difficulties and cannot contact
you for clarification, EPA may not be
able to consider your comment.
Electronic files should avoid the use of
special characters, any form of
ADDRESSES:
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encryption, and be free of any defects or
viruses.
Docket: All documents in the docket
are listed in the https://
www.regulations.gov index. Although
listed in the index, some information is
not publicly available, e.g., CBI or other
information whose disclosure is
restricted by statue. Certain other
material, such as copyrighted material,
will be publicly available only in hard
copy. Publicly available docket
materials are available either
electronically in https://
www.regulations.gov or in hard copy at:
Superfund Records Center, Mail Stop
SFD–7C, 95 Hawthorne Street, Room
403, San Francisco, CA 94105. Phone:
(415) 820–4700. Hours: Mon. thru
Fri.—8 a.m. to 5 p.m.
Heritage Park Regional Library,
Reference Section, 14361 Yale Street,
Irvine, CA 92714. Phone: (949) 936–
4040. Hours: Mon. thru Thu.—10 a.m.
to 9 p.m.; Sat.—10 a.m. to 5 p.m.;
Sun.—12 p.m. to 5 p.m.
FOR FURTHER INFORMATION CONTACT:
Mary Aycock, Remedial Project
Manager, U.S. Environmental Protection
Agency, Region IX, Mail Code SFD81 75
Hawthorne Street, San Francisco, CA
94105, (415) 972–2389, email:
Aycock.Mary@epamail.epa.gov.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Introduction
II. NPL Deletion Criteria
III. Partial Deletion Procedures
IV. Basis for Site Partial Deletion
V. Partial Deletion Action
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I. Introduction
EPA Region IX is publishing this
direct final Notice of Partial Deletion for
the El Toro Marine Corp Air Station
(Site), from the National Priorities List
(NPL). This partial deletion pertains to
all Site media, including soil and
groundwater, of parcels I–A, II–A, III–A,
II–J, II–Q, II–S, II–T, III–C, I–C, II–U,
I–B, I–E, I–G, I–H, I–I, I–J, I–L, I–M, I–
P, II–G, II–I, II–P, III–D, I–K, I–N, I–O,
I–S, II–E, II–L, II–M, II–R, I–Q, I–R, II–
B, II–K, and II–O of the Site. The
properties proposed for deletion are
shown in the map available in the
partial deletion docket and will be
referred to hereafter as ‘‘the properties
proposed for deletion.’’ The NPL
constitutes Appendix B of 40 CFR part
300 which is the Oil and Hazardous
Substances Pollution Contingency Plan
(NCP), which EPA promulgated
pursuant to Section 105 of the
Comprehensive Environmental
Response, Compensation and Liability
Act (CERCLA) of 1980, as amended.
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EPA maintains the NPL as the list of
sites that appear to present a significant
risk to public health, welfare, or the
environment. Sites on the NPL may be
the subject of remedial actions financed
by the Hazardous Substance Superfund
(Fund). This partial deletion of the El
Toro Marine Corp Air Station is
proposed in accordance with 40 CFR
300.425(e) and is consistent with the
Notice of Policy Change: Partial
Deletion of Sites Listed on the National
Priorities List. 60 FR 55466 (Nov. 1,
1995). As described in 300.425(e)(3) of
the NCP, a portion of a site deleted from
the NPL remains eligible for Fundfinanced remedial action if future
conditions warrant such actions.
Because EPA considers this action to
be noncontroversial and routine, this
action will be effective January 21, 2014
unless EPA receives adverse comments
by December 19, 2013. Along with this
direct final Notice of Partial Deletion,
EPA is co-publishing a Notice of Intent
for Partial Deletion in the ‘‘Proposed
Rules’’ section of the Federal Register.
If adverse comments are received within
the 30-day public comment period on
this partial deletion action, EPA will
publish a timely withdrawal of this
direct final Notice of Partial Deletion
before the effective date of the partial
deletion and the partial deletion will
not take effect. EPA will, as appropriate,
prepare a response to comments and
continue with the deletion process on
the basis of the Notice of Intent for
Partial Deletion and the comments
already received. There will be no
additional opportunity to comment.
Section II of this document explains
the criteria for deleting sites from the
NPL. Section III discusses procedures
that EPA is using for this action. Section
IV discusses the properties proposed for
deletion of El Toro Marine Corp Air
Station and demonstrates how they
meet the deletion criteria. Section V
discusses EPA’s action to partially
delete the Site parcels from the NPL
unless adverse comments are received
during the public comment period.
II. NPL Deletion Criteria
The NCP establishes the criteria that
EPA uses to delete sites from the NPL.
In accordance with 40 CFR 300.425(e),
sites may be deleted from the NPL
where no further response is
appropriate. In making such a
determination pursuant to 40 CFR
300.425(e), EPA will consider, in
consultation with the State, whether any
of the following criteria have been met:
i. Responsible parties or other persons
have implemented all appropriate
response actions required;
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ii. all appropriate Fund-financed
response under CERCLA has been
implemented, and no further response
action by responsible parties is
appropriate; or
iii. the remedial investigation has
shown that the release poses no
significant threat to public health or the
environment and, therefore, the taking
of remedial measures is not appropriate.
Pursuant to CERCLA section 121(c)
and the NCP, EPA conducts five-year
reviews to ensure the continued
protectiveness of remedial actions
where hazardous substances, pollutants,
or contaminants remain at a site above
levels that allow for unlimited use and
unrestricted exposure. EPA conducts
such five-year reviews even if a site is
deleted from the NPL. EPA may initiate
further action to ensure continued
protectiveness at a deleted site if new
information becomes available that
indicates it is appropriate. Whenever
there is a significant release from a site
deleted from the NPL, the deleted site
may be restored to the NPL without
application of the hazard ranking
system.
III. Partial Deletion Procedures
The following procedures apply to the
properties proposed for deletion:
(1) EPA has consulted with the state
of California prior to developing this
direct final Notice of Partial Deletion
and the Notice of Intent for Partial
Deletion co-published in the ‘‘Proposed
Rules’’ section of the Federal Register.
(2) EPA has provided the state 30
working days for review of this notice
and the parallel Notice of Intent for
Partial Deletion prior to their
publication today, and the state, through
the Department of Toxic Substances
Control, has concurred on the partial
deletion of the Site from the NPL.
(3) Concurrently with the publication
of this direct final Notice of Partial
Deletion, a notice of the availability of
the parallel Notice of Intent for Partial
Deletion is being published in a major
local newspaper, the Orange County
Register. The newspaper notice
announces the 30-day public comment
period concerning the Notice of Intent
for Partial Deletion of the Site from the
NPL.
(4) The EPA placed copies of
documents supporting the partial
deletion in the deletion docket and
made these items available for public
inspection and copying at the Site
information repositories identified
above.
(5) If adverse comments are received
within the 30-day public comment
period on this partial deletion action,
EPA will publish a timely notice of
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withdrawal of this direct final Notice of
Partial Deletion before its effective date
and will prepare a response to
comments and continue with the
deletion process on the basis of the
Notice of Intent for Partial Deletion and
the comments already received.
Deletion of a portion of a site from the
NPL does not itself create, alter, or
revoke any individual’s rights or
obligations. Deletion of a portion of a
site from the NPL does not in any way
alter EPA’s right to take enforcement
actions, as appropriate. The NPL is
designed primarily for informational
purposes and to assist EPA
management. Section 300.425(e)(3) of
the NCP states that the deletion of a site
from the NPL does not preclude
eligibility for further response actions,
should future conditions warrant such
actions.
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IV. Basis for Site Partial Deletion
The following information provides
EPA’s rationale for deleting the
properties proposed for deletion from
the NPL:
Site Background and History
The former El Toro Marine Corps Air
Station (EPA ID: CA6170023208), (El
Toro MCAS) covering approximately
4,712 acres in the City of Irvine, County
of Orange, California is located at 33
degrees (°) 38 minutes (′) to 33°41′ north
latitude,117°41′ to 117°45′ west
longitude, Township 6 South, Range 6
West (T6S/R6W) (Sections 2–5, 7–11,
16–17, 20–21) and T5S/R8W (Sections
32–33, 35).
Development of former El Toro MCAS
began in July 1942, when construction
of a United States Marine Corps pilot’s
fleet operational training facility began
on approximately 2,319 acres of land in
Orange County, California. The Site was
commissioned as El Toro Marine Corps
Air Station on March 17, 1943. In 1950,
the Station was selected for
development as a master jet air station
and permanent center for marine
aviation of the west coast to support the
operations and combat readiness of
Fleet Marine Forces, Pacific. Between
1944 and 1986, additional land was
acquired to bring the size of the onstation portion of the installation to
4,712 acres.
Major activities at the Site
contributing to the generation of
hazardous wastes included vehicle
maintenance, ground support
maintenance, aircraft maintenance, and
aircraft corrosion control. Other waste
generating activities included munitions
disposal, pest control, fire protection
training, and laboratory operations
including photo development, non-
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destructive inspection, and fuel
analysis. Wastes generated by the
maintenance operations included spent
solvents and waste oils (including TCE,
TCA, MEK, toluene, and PD–680), fuels,
greases removed from the spent
solvents, and spent strippers. Aircraft
washrack activities resulted in discharge
of alkaline soaps, detergents, and small
amounts of PD–680. Vehicle and aircraft
waste discharge produced the greatest
volume of industrial waste of any of the
base activities.
A number of potentially contaminated
areas were identified on the Site,
including four landfills suspected of
containing both hazardous and solid
waste, and other areas where
polychlorinated biphenyls (PCBs),
battery acids, leaded fuels, and other
hazardous substances were suspected of
being dumped or spilled. A Remedial
Investigation (RI) conducted by El Toro
MCAS identified volatile organic
compounds (VOCs), primarily
trichloroethene (TCE), in groundwater
that migrated more than three miles off
base. The primary source of the
groundwater contamination was two
large aircraft hangars. Land irrigated by
wells is located within three miles of
the site; however, none of these wells
are drinking water sources. Surface
water flows into the Upper Newport Bay
Ecological Reserve, located
approximately eight miles from the
base.
In recent years, portions of the Site
were transferred to different
governmental agencies. In 1998, the
Bake Parkway/Interstate 5 public
highway expansion project was
completed resulting in the transfer of
approximately 23 acres to the California
Department of Transportation. In 2001,
896.7 acres in the northeast portion of
the station were transferred to the
Federal Aviation Administration.
The Site was decommissioned as an
active base in July 1999. The parcels to
be deleted from the NPL have all been
transferred from the Department of the
Navy (DON) to Heritage Fields LLC
(Heritage Fields) under the Base
Realignment and Closure Act of 1995.
Heritage Fields plans to build a
combination of residential, commercial,
retail and educational facilities on Site.
In addition, Heritage Fields has
transferred 1,387 acres to the City of
Irvine to create the Orange County Great
Park. The Orange County Great Park
will be home to a world-class Olympicstyle sports village and entertainment
center, a new high school and
neighborhood elementary schools, and
infrastructure and support for a
substantially expanded Irvine
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transportation center. Redevelopment
efforts are on-going.
The Site was proposed to be placed
on the NPL on June 24, 1988 (53 FR
23988); and was placed on the NPL on
February 21, 1990 (55 FR 6154). In
October 1990, the U.S. EPA (EPA),
California Department of Health
Services (CDPH) (the CDPH was the
predecessor program to the California
Department of Health Toxic Substances
Control (DTSC)), California Regional
Water Quality Control Board (RWQCB)
and the DON signed a Federal Facility
Agreement (FFA) which formalized the
process for environmental response
actions and the relative roles of the EPA,
state agencies, and the DON under
CERCLA and the Installation
Restoration Program (IRP). The FFA was
signed by the EPA, the State of
California, and the DON in October
1990.
Environmental Baseline Surveys
(EBSs), which identify parcels of land
for sale, lease, or needing further
investigation, were completed in 1995
and 2003. The EBSs identified
environmental factors and locations of
concern (LOCs) where further
evaluation and/or actions were ongoing
or required. Once identified, these LOCs
were reviewed by the DON, state
regulatory agencies and EPA. Based
upon this review, sites were either
recommended for no further action
(NFA) or for further sampling. Based
upon the subsequent sampling, those
sites either became NFA sites or
proceeded to the more extensive
Comprehensive Environmental
Response, Compensation, and Liability
Act (CERCLA) cleanup process.
The portions of the Site to be deleted
from the NPL include 1,900.4 acres of
contiguous property. All of these parcels
have been transferred from the DON to
Heritage Fields. Prior to transferring
property at El Toro MCAS, the DON was
required, pursuant to Section 102(h) of
CERCLA, to document that all
environmental impacts associated with
the DON’s activities on the Site had
been thoroughly investigated and
appropriate remedial actions have been
taken to protect the public health,
welfare, and the environment. DON
presented this documentation in a series
of successive Finding of Suitability to
Transfer (FOST) documents. In each
case, the FOST described the LOCs on
the property to be transferred and the
investigation and remedial actions taken
at those properties to obtain
concurrence from the EPA, CDPH/DTSC
and RWQCB. A total of 7 FOSTs were
finalized for all parcels to be deleted
between July 2005 and September 2012.
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LOC site narratives where release,
disposal, and/or migration of hazardous
substances occurred, but at
concentrations that did not require a
removal or remedial action because site
conditions were found to be protective
of both human health and the
environment may be found in a tables
appendix in the Deletion Docket. This
appendix does not include LOCs that
were only contaminated with
petroleum, as these sites are not subject
to CERCLA based on the petroleum
exemption. In total, 112 such LOCs were
thoroughly evaluated and recommended
for no further action.
This partial deletion covers the
following Site parcels: I–A, II–A, III–A,
II–J, II–Q, II–S, II–T, III–C, I–C, II–U,
I–B, I–E, I–G, I–H, I–I, I–J, I–L, I–M, I–
P, II–G, II–I, II–P, III–D, I–K, I–N, I–O,
I–S, II–E, II–L, II–M, II–R, I–Q, I–R, II–
B, II–K, and II–O. A map identifying the
areas to be deleted, as well as the areas
to remain on the NPL, is available in the
partial deletion docket.
1. Property Covered by FOST #1
Approximately 2,798 acres of the Site
were covered by FOST #1, including
1,070.2 acres that EPA determined had
not been impacted by hazardous waste
and that therefore were not part of the
NPL. These two areas of the Site were
removed from the NPL through two
clarification letters issued by EPA.
Clarification Areas A, B, C, and D,
consisting of 978.6 acres, were removed
from the NPL through an EPA
clarification letter dated October 27,
2005. Clarification Area E, consisting of
91.6 acres, was removed from the NPL
through an EPA clarification letter dated
March 21, 2006.
The unclarified portions of the FOST
#1 area consisted of three Transfer
Parcels: Transfer Parcels I–A, II–A, and
III–A.
1.1 Transfer Parcel I–A
Transfer Parcel I–A was
approximately 809.5 acres. This parcel
contained 225 non-demolished
buildings/structures/facilities including
the units located in the Saddleback
Terrace housing area. In addition, Parcel
I–A contained IRP Site 20—Hobby Shop
and a portion of IRP Site 25—Major
Drainages.
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1.1.1
IRP Site 20—Hobby Shop
Site Location and History
IRP Site 20—Hobby Shop
encompassed approximately 0.5 acre
immediately northwest of the
intersection of North 9th Street and
West Marine Way and included
Building 626. Beginning in 1967, the
site was used as an auto shop for
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military personnel to service and repair
privately owned vehicles. Kerosene was
reportedly used to wash down the
paved area at the site until
approximately 1976. The wash runoff
drained into a catch basin situated in
the entry driveway and finally drained
into an oil/water separator (OWS). From
1976 until closure of the Hobby Shop in
1999, a biodegradable soap was used in
place of kerosene.
Site 20 originally consisted of four
units:
• Unit 1—Shallow Drainage Swale
(1–2 feet below grade), adjacent to the
east side of Building 626.
• Unit 2—South Drainage Ditch, ran
along North 9th Street
• Unit 3—Stained Area, small area
adjacent to the northwest side of
Building 626
• Unit 4—Inner Courtyard of Building
626, an entry driveway, and a frontsloping area adjacent to the drainage
ditch along North 9th Street. The inner
portion was paved with asphalt. The
entry driveway was concrete and
crossed over the drainage ditch. The
front area was covered with grass with
some bare spots and various trees.
Operation and Maintenance
No operation and maintenance is
required for this site.
Remedial Investigations
Investigations at the IRP Site 20
included a RCRA Facility Assessment
(RFA), a Phase I RI, aerial photograph
surveys in 1993, and a Phase II RI in
1996. In 1997, Units 2 and 3 were
excluded from the site based on the
CERCLA petroleum exemption, 42
U.S.C. 9601(14)(F). Sites containing
only petroleum contamination were,
and continue to be remediated under
the oversight of the RWQCB).
Soil sampling identified VOCs, semivolatile organic compounds (SVOCs),
PCBs, and pesticides at the site, all
below residential PRGs. Arsenic was
detected at concentrations above the
former El Toro MCAS background
value. The RI of the site indicated that
the site-related contamination was
limited to the shallow soil interval.
Remedial Investigations
IRP Site 25 was constituted before the
source of the regional VOC groundwater
contamination had been identified as
IRP Site 24 (which is not part of this
deletion). IRP Site 25 was identified for
a Phase II RI, but the drainages were
investigated as part of the Phase I RI for
IRP Sites 18 and 24 to evaluate the
source of the off-site VOC groundwater
plume. Potential contamination within
the major drainages and San Diego
Creek was assessed by analyzing surface
water, sediment, soil, and soil gas
samples. Except for the Borrego Canyon
Wash, metals and pesticides were
detected above former El Toro MCAS
background concentrations in all
drainages. Significant petroleum
hydrocarbon contamination was
detected at depths of 15 to 20 feet below
ground surface (bgs) at the southern end
of Agua Chinon Wash, near the former
El Toro MCAS boundary.
Within the Agua Chinon Wash, total
petroleum hydrocarbons (TPH) were
detected at depths up to 57 feet bgs. The
RI of the site indicated that the siterelated contamination was limited to
sediment and surface water.
Selected Remedy
The human health and ecological risk
assessments showed that the
contaminants present in the soil did not
present an unacceptable risk to human
health or the environment. Therefore,
no remedial action was required. A
Record of Decision (ROD) for NFA was
signed on September 30, 1997. No risks
are present at IRP Site 20 and no
institutional controls are present.
Response Actions and Cleanup
Standards
No response actions have been taken
and no cleanup standards have been set.
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1.1.2 IRP Site 25—Major Drainages
IRP Site 25 encompassed
approximately 22 acres and comprised
the four major washes that flowed
through former El Toro MCAS. These
included Agua Chinon Wash, Bee
Canyon Wash, Borrego Canyon Wash,
and Marshburn Channel. Three of these
drainages (Agua Chinon Wash, Bee
Canyon Wash, and Borrego Canyon
Wash) were continuations of natural
washes that originated in the Santa Ana
Mountains. Surface drainage from the
hills and upgradient irrigated farmland
combined with runoff generated from
extensive paved surfaces at former El
Toro MCAS. The on-station storm sewer
system discharged to the drainage
channels, which then flowed into San
Diego Creek. San Diego Creek
discharged into upper Newport Bay,
about 7 miles downstream from its
intersection with Marshburn Channel.
These washes traversed Transfer Parcels
I–A, II–A, and III–A, and also traversed
property that was not part of FOST #1.
Selected Remedy
The human health and ecological risk
assessments showed that the
contaminants present in these media
did not present an unacceptable risk to
human health or the environment.
Therefore, no remedial action was
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required. The Draft Final RI Report was
completed in 1997, and a ROD for NFA
was signed on September 30, 1997. No
risks are present at IRP Site 25 and no
institutional controls are present.
Response Actions and Cleanup
Standards
No response actions have been taken
and no cleanup standards have been set.
Operation and Maintenance
No operation and maintenance is
required for this site.
1.2 Transfer Parcel II–A
Transfer Parcel II–A was
approximately 1,439.6 acres. This parcel
contained a golf course and 1,078 nondemolished buildings/structures/
facilities which included the units
located in San Joaquin, Vista Terrace,
Navy/Marine (NAMAR), and Wherry
housing areas. Transfer Parcel II–A
included IRP Sites 6 and 19, and a
portion of IRP Site 25 (described above).
TKELLEY on DSK3SPTVN1PROD with RULES
1.2.1 IRP Site 6—Drop Tank Drainage
Area No. 1
Site Location and History
IRP Site 6 encompassed
approximately 3 acres bounded by
taxiways to the north and west, a
concrete aircraft parking apron to the
east, and East Marine Way to the south.
The site consisted of three units:
• Unit 1 was an area along the edge
of a concrete parking apron where
aircraft drop tanks were formerly
drained of residual jet fuel and then
cleaned prior to reuse.
• Unit 2 was a shallow drainage
swale that extends from the north side
of Building 727, west to a catch basin
that eventually discharged into the Agua
Chinon Wash. The catch basin received
surface runoff and sediment from the
site.
• Unit 3 was a flat, grass-covered area
south of the drainage swale where drop
tanks were stored.
From 1969 to 1983, aircraft drop tanks
were transported to the site where the
fuel remaining in the tanks was drained.
Residual jet propulsion fuel, grade 5
(JP 5) in the tanks was drained to the
concrete apron, and the combined fuel/
rinse water ran onto the adjacent grassy
area. In addition to fuel, waste lubricant
oils from maintenance operations were
also reportedly stored in drums and
staged in the area.
Approximately 1,400 gallons of JP 5
fuel were reportedly drained from the
drop tanks onto the concrete apron and
washed onto the adjacent area. Portions
of the unpaved areas at the site were
also reportedly used for storing oil
drums. It was estimated that
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16:31 Nov 18, 2013
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approximately 300 gallons of waste oil
leaked from these storage drums at the
site.
Remedial Investigations
Investigations conducted at IRP Site 6
included a Phase I remedial
investigation (RI) and aerial photograph
surveys in 1993, employee interviews in
1994, and a Phase II RI in 1996. During
the investigations, VOCs, SVOCs, and
polynuclear aromatic hydrocarbons
were detected at concentrations below
residential PRGs. The maximum arsenic
concentration was detected at a depth of
Property of 8–10 feet bgs and was above
the former El Toro MCAS background
concentration for arsenic. The RI of the
site indicated that the site-related
contamination was limited to the
shallow soil interval.
Selected Remedy
The human health and ecological risk
assessments indicated that the
contaminants present in the soil did not
present an unacceptable risk to human
health or the environment. Therefore,
no remedial action was required. A ROD
for NFA was signed on September 30,
1997.
Response Actions and Cleanup
Standards
No response actions have been taken
and no cleanup standards have been set.
Operation and Maintenance
No operation and maintenance is
required for this site.
1.2.2 IRP Site 19—Aircraft
Expeditionary Refueling Site
Site Location and History
IRP Site 19 was within Transfer Parcel
II–A and encompassed approximately 4
acres southwest of Buildings 404 and
414. Between 1964 and 1986, the site
operated as a fuel-storage and fueldispensing area. The site consisted of
six 20,000-gallon JP 5 fuel bladders in
4-foot-high earthen revetments and
associated piping and fuel-dispensing
equipment. The site originally consisted
of four units:
• Unit 1, Northeast Stained Area
• Unit 2, Excavated Areas;
• Unit 3, Stained Area Around
Excavations; and
• Unit 4, Pump Station (this area was
added for the Phase II RI and then was
removed under the CERCLA petroleum
exclusion).
Initial Response
Various spills and leaks reportedly
occurred during operation of the site. In
one instance, an estimated 20,000
gallons of JP 5 were reportedly released
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after a bladder rupture. Petroleum
hydrocarbons were detected in the soil
beneath the ruptured bladder.
The fuel bladders were removed in
1986, and the soil was excavated to a
maximum depth of 15 feet bgs in a 30foot-square area beneath the location of
the bladder rupture (Unit 2). The
excavation was partially backfilled to a
depth of approximately 11 feet in 1994.
Prior to backfill, soil samples were
collected within the excavated area, i.e.,
IRP Site 19. No chemicals of potential
concern were detected at concentrations
greater than EPA industrial PRGs. In
1996, the remaining excavation was
backfilled to grade the surrounding area
with clean fill material. An additional
19,000-square-foot area beneath the
locations of the other bladders was also
excavated in 1986 to a depth of
approximately 2.5 feet. All of the
buildings/structures/facilities at the site
were removed following site closure and
were replaced by a pump station and
UST complex situated adjacent to the
east side of the site.
Remedial Investigations
Investigations conducted at the site
included a Phase I RI and aerial
photograph surveys in 1993, employee
interviews in 1994, and a Phase II RI in
1996. The investigations indicated
SVOCs at concentrations below
residential PRGs, with the exception of
benzo(a)pyrene, which was above the
industrial PRG value. VOCs were
detected at concentrations below
residential PRGs. Arsenic was detected
at concentrations above the industrial
PRG value, and the maximum arsenic
value was above the former El Toro
MCAS background concentration.
Selected Remedy
The human health and ecological risk
assessments showed that the
contaminants present in the soil did not
present an unacceptable risk to human
health or the environment. A ROD for
NFA for Units 2 and 3 was signed on
September 30, 1997. Unit 1 was
excluded from the IRP under the
CERCLA petroleum exclusion in 1995
(closed by RWQCB in a letter dated May
14, 1997), and Unit 4 was excluded from
the IRP under the CERCLA petroleum
exclusion in 1997 (Unit 4 was being
addressed with a number of USTs and
the associated area was therefore
unsuitable for transfer and was not part
of FOST #1).
Response Actions and Cleanup
Standards
No further response actions have been
taken.
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Operation and Maintenance
No operation and maintenance is
required for this site.
1.2.3 PCB T56, concrete pad of
transformer 56
Site Location and History
A minor release of transformer oil
containing PCBs
Selected Remedy
No risks are present at PCB T56 and
no institutional controls are present.
Response Actions and Cleanup
Standards
The transformer was replaced and the
concrete pad was removed. No further
action was required.
Operation and Maintenance
No operation and maintenance is
required for this site.
1.3
Transfer Parcel III–A
hydrocarbons, and pesticides were
detected at concentrations below
residential PRGs. Arsenic was detected
at concentrations above the industrial
PRG from the surface to a depth of 80
feet bgs. The maximum arsenic
concentration was below the former El
Toro MCAS background concentration.
Total recoverable petroleum
hydrocarbons (TRPH) were detected at
the soil surface and at a depth of 5 feet
bgs. Based on the results of the Phase I
RI investigation, a Phase II RI was not
recommended. The RI of the site
indicated that the site-related
contamination was limited to the
shallow soil interval.
Selected Remedy
The human health and ecological risk
assessments showed that the
contaminants present in the soil did not
present an unacceptable risk to human
health or the environment. A ROD for
NFA was signed on September 30, 1997.
Transfer Parcel III–A was
approximately 329.0 acres. This parcel
contained 10 non-demolished
buildings/structures/facilities, as well as
a portion of IRP Site 13.
Response Actions and Cleanup
Standards
No response actions have been taken
and no cleanup standards have been set.
1.3.1
Operation and Maintenance
No operation and maintenance is
required for this site. No deed
restrictions were recommended for Site
13 due to chemicals present in the soil.
However since the groundwater beneath
Site 13 was contaminated by
trichloroethylene (TCE) and
tetrachloroethylene (PCE; also
perchloroethylene) due to Site 24—VOC
source area, when the NFA ROD was
signed on September 30, 1997, the use
restrictions prohibiting drilling of wells
and/or extraction of groundwater and
allowing access for groundwater
monitoring and maintenance of
equipment associated with groundwater
remediation were to be addressed in the
ROD for Site 18 and Site 24. When the
Final ROD for Site 18 and Site 24 was
completed in 2002, the updated VOC
plume and 500 foot buffer zone were no
longer located beneath Site 13.
Consequently, groundwater restrictions
due to the Site 24 VOC plume were no
longer applicable for Site 13.
IRP Site 13—Oil Change Area
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Site Location and History
IRP Site 13 encompassed
approximately 34,000 square feet and
was bounded on the north by Former
Tank Farm No. 2 and on the south by
the storage yard for Building 242. The
site was situated within Transfer Parcel
III–A and Carve-Out (CO) III–B. The site
was relatively flat, unpaved, and
generally unvegetated. Site 13 consisted
of two units: Unit 1 comprised the area
southeast of Tank Farm No. 2 and Unit
2 comprised the area southwest of Tank
Farm No. 2. Trucks were driven to the
area southeast of the tank farm (Unit 1)
for oil changes, and crank case oil was
frequently drained onto the ground.
From 1977 to 1983, approximately 7,000
gallons of waste oil were drained onto
the ground. The oily soil was
subsequently removed, and no visible
evidence of the oily soil remained. A
review of aerial photographs indicated
heavy staining throughout the area
between the tank farm and Building 242
(Unit 2), which persisted over the years
of photographic record. It is likely that
oil changes were also conducted in that
area.
Remedial Investigations
Investigations conducted at the site
included an RFA, a Phase I RI and aerial
photographic surveys in 1993, and
employee interviews in 1994. VOCs,
SVOCs, polynuclear aromatic
VerDate Mar<15>2010
16:31 Nov 18, 2013
Jkt 232001
2. Property Covered by FOST #2
Approximately 8 acres of El Toro
MCAS were covered by FOST #2. This
area consisted of four Transfer Parcels
(II–J, II–S, II–T, and III–C), and a portion
of one Transfer Parcel (II–Q). Transfer
parcels II–J and II–Q did not contain any
CERCLA LOCs. Transfer Parcel II–T was
approximately 0.5 acres in size and
contained one building/structure/
facility (Building 761). Transfer Parcel
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69307
III–C was approximately 1 acre in size
and contained one building/structure/
facility (Building 240). NFA
determinations were made for all LOCs
within Transfer Parcels II–T and III–C.
2.1
Transfer Parcel II–S
Transfer Parcel II–S was
approximately 1.3 acres in size and
included six buildings/structures/
facilities (Buildings 374, 377, 447, 448,
566, and 726) and former Building 603
(demolished).
2.1.1
RFA 131
Site Location and History
RFA 131, an engine test cell, was
located within Transfer Parcel II–S near
Building 447.
Initial Response
Near surface soils were removed in
1997.
Selected Remedy
DTSC concurred with NFA in a letter
from July 1999. RWQCB concurred with
NFA in June 2000.
Response Actions and Cleanup
Standards
No further response actions have been
taken.
Operation and Maintenance
No operation and maintenance is
required for this site.
3. Property Covered by FOST #3
Approximately 3.9 acres of El Toro
MCAS were covered by FOST #3.
Site Location and History
This area consisted of two Transfer
Parcels referred to in FOST #3 as
‘‘Carve-Outs’’ (COs):
• CO I–C consisted of approximately
0.1 acre in the northeastern portion of
the former base. This CO was created
during preparation of the 2004 Finding
of Suitability to Lease when a portion of
an underground pipeline (Norwalk-El
Toro Pipeline) was believed to exist
within this area. However, based on a
detailed review of the pipeline physical
alignment, it was determined that no
portion of the pipeline was within
Transfer Parcel I–C. No buildings or
utilities were located on the Transfer
Parcel.
• CO II–U consisted of approximately
3.8 acres in the northeastern portion of
the former base. No buildings or utilities
were located on the CO.
Initial Response
A portion of the Norwalk-El Toro
Pipeline was removed from CO II–U in
the fall of 2006, with the exception of
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approximately 100 feet of pipeline that
remains under Agua Chinon Wash.
Remedial Investigations
The COs were evaluated during the
initial phase of environmental
assessment and the results were
documented in the Final 2003 EBS. The
EBS concluded that no hazardous
substances were stored or released on
the COs.
Selected Remedy
No further action was necessary in
these areas.
Response Actions and Cleanup
Standards
No response actions have been taken
and no cleanup standards have been set.
Operation and Maintenance
No operation and maintenance is
required for this site.
Site Location and History
This area consisted of thirteen COs:
COs I–B, I–E, I–G, I–H, I–I, I–J, I–L, I–
M, I–P, II–G, II–I, II–P, III–D. COs I–L,
I–M, I–P, II–G, II–I, and II–P did not
contain CERCLA LOCs.
Selected Remedy
No Further Action determinations
were issued for all LOCs within COs I–
B, I–E, I–G, I–H, I–I, I–J, and II–G. CO
III–D contained a portion of IRP Site 13.
All other LOCs in CO III–D received
NFA determinations and no cleanup
was required.
Response Actions and Cleanup
Standards
No response actions have been taken
and no cleanup standards have been set.
Operation and Maintenance
No operation and maintenance is
required for these sites.
TKELLEY on DSK3SPTVN1PROD with RULES
5. Property Covered by FOST #5
Approximately 119.3 acres of El Toro
MCAS were covered by FOST #5.
Site Location and History
This area included nine COs: COs I–
F, I–K, I–N, I–O, I–S, II–E, II–L, II–M, II–
R, and CO Building 746. CO I–F is not
part of this deletion request and will
remain on the NPL. CO Building 746 is
located within CO II–D and is not part
Jkt 232001
Remedial Investigations
Operation and Maintenance
As these COs did not contain CERCLA
LOCs, no remedial investigations were
conducted.
No operation and maintenance is
required for this site.
Selected Remedy
Approximately 356.81 acres of El
Toro MCAS were covered by FOST #6.
No Further Action determinations
were issued for all LOCs within CO II–
E and II–M. CO II–L contained a portion
of IRP Site 25. All other LOCs in CO II–
L received NFA determinations and no
cleanup was required.
Response Actions and Cleanup
Standards
Operation and Maintenance
No operation and maintenance is
required for these sites.
5.1
CO II–R
CO II–R consisted of approximately
1.2 acres and was located in the
southeast portion of the former base.
Remedial Investigations
As these COs did not contain CERCLA
LOCs, no remedial investigations were
conducted.
16:31 Nov 18, 2013
1998. No evidence of a release was
observed during the visual site
inspections conducted for the 2003 EBS.
Building 457 was subsequently
demolished to its foundation.
No response actions have been taken
and no cleanup standards have been set.
4. Property Covered by FOST #4
Approximately 42.9 acres of El Toro
MCAS were covered by FOST #4.
VerDate Mar<15>2010
of this partial deletion request and will
also remain on the NPL. COs I–K, I–N,
I–O, I–S contained only petroleum LOCs
or no release, disposal, and/or migration
of hazardous substances occurred there.
5.1.1 Resource Conservation and
Recovery Act (RCRA) Facility
Assessment (RFA) Site 244/PCB T74
Site Location and History
There was one pad-mounted
transformer (PCB T74) at Building 457.
Historically, disposal activities were
conducted at this site, though the dates
of these operations are unknown. A
response action was required for
releases of transformer oil containing
PCBs at Building 457 (RCRA Facility
Assessment (RFA) Site 244).
6. Property Covered by FOST #6
Site Location and History
This area included eleven COs: COs
I–D, I–Q, I–R, II–B, II–K, II–N, II–O, III–
B–1, III–B–2, III–E, and III–F. COs I–Q
and I–R contained only petroleum LOCs
and were therefore subject to the
CERCLA petroleum exclusion, or no
release, disposal, and/or migration of
hazardous substances occurred there. As
a result, these COs are not discussed in
this document. Additionally, COs I–D,
II–N, III–B–1, III–B–2, III–E, and III–F
are not part of this partial deletion
request and will remain on the NPL.
Remedial Investigations
As these COs did not contain CERCLA
LOCs, no remedial investigations were
conducted.
Selected Remedy
COs II–K contained a portion of IRP
Site 25. All other LOCs in CO II–K
received NFA determinations and no
cleanup was required. All LOCs in CO
II–O received NFA determinations and
no cleanup was required.
Response Actions and Cleanup
Standards
No response actions have been taken
and no cleanup standards have been set.
Remedial Investigations
Operation and Maintenance
While no remedial investigations
were conducted under CERCLA, RFA
Site 244/PCB T74 was evaluated under
a RCRA Facility Assessment.
No operation and maintenance is
required for these sites.
6.1
CO II–B
Selected Remedy
DTSC concurred with NFA for RFA
244 in a letter dated December 1998.
EPA and DTSC concurred with NFA for
PCB T74 in September 2003.
CO II–B consisted of approximately
6.73 acres located in the northeast
portion of the former base.
6.1.1 Temporary Accumulation Area
(TAA) Site 130C
Response Actions and Cleanup
Standards
Shallow soil samples that were
collected in the area affected by the PCB
release identified PCBs in one of the
seven samples collected. The
transformer was replaced and removal
of impacted soils was completed in
1997. The response action was
completed and closed in December
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Site Location and History
TAA 130C was located northing of
Building 130.
Remedial Investigations
While no remedial investigations
were conducted under CERCLA, TAA
130C was evaluated under a RCRA
Facility Assessment. Sampling
indicated low levels of arsenic and
chlorinated pesticides.
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Selected Remedy
TAA 130C received site closure
concurrence from DTSC in March 2009.
No further action was required.
Remedial Investigations
Response Actions and Cleanup
Standards
Contaminated soil was excavated and
confirmation soil samples were
collected at TAA 130C in 2008.
Operation and Maintenance
Property Covered by FOST #7
Approximately 151.06 acres of El
Toro MCAS were covered by FOST #7.
This area included three COs: COs
II–F–1, II–Q, and II–V–1. There were no
CERCLA LOCs within CO II–F–1 or CO
II–V–1. As a result, COs II–F–1 and II–
V–1 are not discussed in this document.
Any contamination on these COs was,
and continues to be remediated under
the oversight of the RWQCB.
7.1
IRP Site 4
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Site Location and History
IRP Site 4 is located immediately
southeast of Building 658, a former jetengine testing facility. The site is
bounded by 9th Street to the south,
Building 658 to the north and west, and
Tank Farm No. 5 to the east. The IRP
Site 4 consists of two units: Unit 1 is an
oil-stained area southeast of Building
658 which overlaps a concrete
transformer pad, and Unit 2 is a
drainage ditch which received runoff
from a ferrocene spill.
The staining at Unit 1 was the result
of oily discharges from Building 658,
which were observed over an
approximate 2-year period. The
contamination at Unit 2 originated from
an August 1983 spill, when the contents
of a 500-gallon tank (wash water and
residual jet fuel) reportedly overflowed
during washing and spilled onto the
ground, draining into a ditch adjacent to
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16:31 Nov 18, 2013
The human health and ecological risk
assessments showed that the
contaminants present in the soil did not
present an unacceptable risk to human
health or the environment. Therefore,
no remedial action was required. The
NFA ROD was signed on September 30,
1997.
Response Actions and Cleanup
Standards
No response actions have been taken
and no cleanup standards have been set.
Operation and Maintenance
CO II–Q
CO II–Q consisted of approximately
84.49 acres located in the central
portion of the former base and
contained buildings 114, 124, 125, 126,
127, 230, 231, 363, 372, 642, 658, 677,
698, 716, 747, 752, 763, 779, 903, 923,
938, 952, and 1804. CO II–Q also
contained structures 396, 558, 559, 560,
561, 659, 904, 905, 906, 907, 908, 909,
910, and 911. The DON leased this CO
to Heritage Fields, LLC, who
subsequently assigned the lease for the
majority of this CO to the City of Irvine.
CO II–Q includes portions of IRP 4 and
25.
7.1.1
Investigations conducted at IRP Site 4
included a Phase I RI and aerial
photograph surveys in 1993. VOCs and
SVOCs were below residential PRGs in
both units.
Selected Remedy
No operation and maintenance is
required for this site.
7.
9th Street. The spilled liquid reportedly
contained approximately 5 gallons of
ferrocene and a hydrocarbon carrier
solution.
Jkt 232001
No operation and maintenance is
required for this site.
Five Year Reviews
Cleanup activities at El Toro MCAS
have resulted in the remediation of all
Site-related contamination such that
restrictions on use and/or institutional
controls were unnecessary. Accordingly,
no Five-Year Reviews were required
under CERCLA.
Community Involvement
Public participation activities have
been satisfied as required in CERCLA
Section 113(k), 42 U.S.C. 9613(k) and
CERCLA Section 117, 42 U.S.C. 9617.
Community input has been sought by
the DON throughout the cleanup
process. The El Toro MCAS Restoration
Advisory Board (RAB) serves as a focal
point for the exchange of information
about environmental restoration
activities between the DON, regulatory
agencies, and the local community. RAB
members review technical reports and
plans pertaining to the El Toro MCAS
cleanup and provide input to the DON
and the regulatory agencies. RAB
members serve as volunteers and act as
a liaison to the specific community they
represent including various cities and
homeowner associations in the vicinity
of El Toro MCAS. All RAB meetings are
open to the public and anyone
interested may attend. They are held
semi-annually on a Wednesday evening
in April and November at the Irvine City
Hall, One Civic Center Plaza.
Community involvement for the areas
that are the subject of this document has
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69309
occurred by soliciting public comment
on various documents depending on the
site’s investigation and cleanup (if
needed) process. All NFA decision
documents were issued for 30-day
public comment periods with
comments, if any, addressed in the
Responsiveness Summary of the Record
of Decision. In addition, sites where
non-time critical removal actions
occurred provided public involvement
with the issuance of the engineering
evaluation/cost analysis for public
comment.
Since there are a number of ongoing
investigations and cleanup at El Toro
MCAS, community involvement
activities such as the biannual RAB
meetings will continue to occur.
Determination That the Criteria for
Deletion Have Been Met
The NCP (40 CFR 300.425(e)) states
that a site may be deleted from the NPL
when no further response action is
necessary. EPA, in consultation with the
State of California, has determined that
all appropriate response actions under
CERCLA have been completed on the
properties proposed for deletion.
Therefore, these portions of the former
El Toro Marine Corps Air Station meet
the criteria of 40 CFR 300.425(e) and
may be deleted from the NPL. The State
of California, through the DTSC,
concurred on this proposed deletion by
letter dated February 1, 2013.
V. Partial Deletion Action
The EPA, with concurrence of the
State of California through the
Department of Toxic Substances
Control, has determined that all
appropriate response actions under
CERCLA have been completed.
Therefore, EPA is deleting parcels I–A,
II–A, III–A, II–J, II–Q, II–S, II–T, III–C,
I–C, II–U, I–B, I–E, I–G, I–H, I–I, I–J,
I–L, I–M, I–P, II–G, II–I, II–P, III–D,
I–K, I–N, I–O, I–S, II–E, II–L, II–M, II–
R, I–R, II–B, II–K, and II–O of the El
Toro Marine Corp Air Station Site from
the NPL.
Because EPA considers this action to
be noncontroversial and routine, EPA is
taking it without prior publication. This
action will be effective January 21, 2014
unless EPA receives adverse comments
by December 19, 2013. If adverse
comments are received within the 30day public comment period, EPA will
publish a timely withdrawal of this
direct final notice of partial deletion
before the effective date of the partial
deletion and it will not take effect. EPA
will prepare a response to comments
and continue with the deletion process
on the basis of the notice of intent to
partially delete and the comments
E:\FR\FM\19NOR1.SGM
19NOR1
69310
Federal Register / Vol. 78, No. 223 / Tuesday, November 19, 2013 / Rules and Regulations
1991 Comp., p. 351; E.O. 12580, 52 FR 2923,
3 CFR 1987 Comp., p. 193.
Dated: October 22, 2013.
Jared Blumenfeld,
Regional Administrator Region IX.
already received. There will be no
additional opportunity to comment.
List of Subjects in 40 CFR Part 300
Environmental protection, Air
pollution control, Chemicals, Hazardous
waste, Hazardous substances,
Intergovernmental relations, Penalties,
Reporting and recordkeeping
requirements, Superfund, Water
pollution control, Water supply.
Appendix B—[Amended]
For the reasons set out in this
document, 40 CFR part 300 is amended
as follows:
PART 300—[AMENDED]
2. Table 2 of Appendix B to part 300
is amended by revising the entry under
‘‘El Toro Marine Corps Air Station’’,
California to read as follows:
■
1. The authority citation for part 300
continues to read as follows:
Appendix B to Part 300—National
Priorities List
Authority: 33 U.S.C. 1321(c)(2); 42 U.S.C.
9601–9657; E.O. 12777, 56 FR 54757, 3 CFR
*
■
*
*
*
*
TABLE 2—FEDERAL FACILITIES SECTION
Notes (a)
State
Site name
City/county
*
CA .....................
*
*
*
El Toro Marine Corps Air Station ............................................................
*
*
El Toro ............................................
*
*
*
*
*
*
*
*
P
(a) *
* *
*P = Sites with partial deletion(s).
DEPARTMENT OF COMMERCE
[FR Doc. 2013–27724 Filed 11–18–13; 8:45 am]
BILLING CODE 6560–50–P
National Oceanic and Atmospheric
Administration
DEPARTMENT OF TRANSPORTATION
RIN 0648–AY96
Pipeline and Hazardous Materials
Safety Administration
[Docket No. 100813359–3908–02]
Endangered and Threatened Species;
Protective Regulations for the Gulf of
Maine Distinct Population Segment of
Atlantic Sturgeon
49 CFR Part 172
Hazardous Materials Table, Special
Provisions, Hazardous Materials
Communications, Emergency
Response Information, Training
Requirements, and Security Plans
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Interim final rule.
AGENCY:
CFR Correction
In Title 49 of the Code of Federal
Regulations, Parts 100 to 177, revised as
of October 1, 2012, on page 242, in
§ 172.101, in the Hazardous Materials
Table, in the entry for ‘‘Oxygen,
compressed’’, in column 10A, the letter
‘‘A’’ is added.
[FR Doc. 2013–27733 Filed 11–18–13; 8:45 am]
TKELLEY on DSK3SPTVN1PROD with RULES
BILLING CODE 1505–01–D
VerDate Mar<15>2010
16:31 Nov 18, 2013
Jkt 232001
50 CFR Part 223
We, NMFS, are issuing an
interim final regulation to conserve the
Gulf of Maine Distinct Population
Segment (DPS) of Atlantic sturgeon
(Acipenser oxyrinchus oxyrinchus). On
February 6, 2012, we listed the Gulf of
Maine DPS of Atlantic sturgeon as
threatened under the Endangered
Species Act (ESA). When a species is
listed as threatened under the ESA, we
are required to issue protective
regulations under section 4(d) of the
ESA. Such protective regulations are
ones deemed ‘‘necessary and advisable
for the conservation of the species’’ and
may include any act prohibited for
endangered species under section
9(a)(1) of the ESA. This regulation
extends the prohibitions listed in
section 9 of the ESA to Gulf of Maine
DPS Atlantic sturgeon. The prohibitions
set forth in this rule are considered
SUMMARY:
PO 00000
Frm 00026
Fmt 4700
Sfmt 4700
necessary and advisable for the
conservation of this species. Given that
the changes made to this rule are based
on the new information that was not
submitted as public comment on the
proposed rule, we are publishing this
rule as an interim final rule and are
soliciting additional public comment.
This document also announces the
availability of a final Environmental
Assessment that analyzes the
environmental impacts of promulgating
this interim final regulation.
DATES: This interim final rule is
effective on December 19, 2013.
Comments on this interim final rule
must be received by December 19, 2013.
ADDRESSES: You may submit comments,
identified by RIN No. 0648–AY96, by
any of the following methods:
• Federal eRulemaking Portal: http//
www.regulations.gov. Follow the
instructions for submitting comments.
• Fax: To the attention of Lynn
Lankshear at (978) 281–9394.
• Mail or hand-delivery: Submit
written comments to the Assistant
Regional Administrator, Protected
Resources Division, NMFS, Northeast
Region, 55 Great Republic Drive,
Gloucester, MA 01930.
Instructions: All comments received
are a part of the public record and will
generally be posted to https://
www.regulations.gov without change.
All Personal Identifying Information (for
example, name, address, etc.)
voluntarily submitted by the commenter
may be publicly accessible. Do not
submit Confidential Business
Information or otherwise sensitive or
protected information.
E:\FR\FM\19NOR1.SGM
19NOR1
Agencies
[Federal Register Volume 78, Number 223 (Tuesday, November 19, 2013)]
[Rules and Regulations]
[Pages 69302-69310]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2013-27724]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 300
[EPA-HQ-SFUND-1910-0010; FRL 9902-79-Region 9]
National Oil and Hazardous Substances Pollution Contingency Plan;
National Priorities List: Partial Deletion of the El Toro Marine Corps
Air Station Superfund Site
AGENCY: Environmental Protection Agency.
ACTION: Direct final rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) Region IX is
publishing a direct final Notice of Deletion of portions of the El Toro
Marine Corp Air Station Superfund Site (Site), located in Irvine,
California, from the National Priorities List (NPL). The NPL,
promulgated pursuant to section 105 of the Comprehensive Environmental
Response, Compensation, and Liability Act (CERCLA) of 1980, as amended,
is an appendix of the National Oil and Hazardous Substances Pollution
Contingency Plan (NCP). This direct final partial deletion is being
published by EPA with the concurrence of the State of California
through the Department of Toxic Substances Control (DTSC), because EPA
has determined that all appropriate response actions at these
identified parcels under CERCLA have been completed. However, this
partial deletion does not preclude future actions under Superfund.
This partial deletion pertains to all Site media, including soil
and groundwater, of parcels I-A, II-A, III-A, II-J, II-Q, II-S, II-T,
III-C, I-C, II-U, I-B, I-E, I-G, I-H, I-I, I-J, I-L, I-M, I-P, II-G,
II-I, II-P, III-D, I-K, I-N, I-O, I-S, II-E, II-L, II-M, II-R, I-Q, I-
R, II-B, II-K, and II-O of the Site. The current remaining areas of the
Site will remain on the NPL and are not being considered for deletion
as part of this action.
DATES: This direct final partial deletion is effective January 21, 2014
unless EPA receives adverse comments by December 19, 2013. If adverse
comments are received, EPA will publish a timely withdrawal of the
direct final partial deletion in the Federal Register informing the
public that the partial deletion will not take effect.
ADDRESSES: Submit your comments, identified by Docket ID no. EPA-HQ-
SFUND-1910-0010, by one of the following methods:
https://www.regulations.gov. Follow on-line instructions
for submitting comments.
Email: Aycock.Mary@epa.gov.
Fax: (415) 947-3528.
Mail: Mary Aycock, U.S. EPA Remedial Project Manager, U.S.
Environmental Protection Agency, Region IX, Mail Code SFD-8-1, 75
Hawthorne Street, San Francisco, CA 94105.
Hand delivery: Mary Aycock, U.S. EPA Remedial Project
Manager, U.S. Environmental Protection Agency, Region IX, Mail Code
SFD81, 75 Hawthorne Street, San Francisco, CA 94105. Such deliveries
are only accepted during the Docket's normal hours of operation, and
special arrangements should be made for deliveries of boxed
information.
Instructions: Direct your comments to Docket ID no. EPA-HQ-SFUND-
1910-0010. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through https://www.regulations.gov or email. The https://www.regulations.gov Web site
is an ``anonymous access'' system, which means EPA will not know your
identity or contact information unless you provide it in the body of
your comment. If you send an email comment directly to EPA without
going through https://www.regulations.gov, your email address will be
automatically captured and included as part of the comment that is
placed in the public docket and made available on the Internet. If you
submit an electronic comment, EPA recommends that you include your name
and other contact information in the body of your comment and with any
disk or CD-ROM you submit. If EPA cannot read your comment due to
technical difficulties and cannot contact you for clarification, EPA
may not be able to consider your comment. Electronic files should avoid
the use of special characters, any form of
[[Page 69303]]
encryption, and be free of any defects or viruses.
Docket: All documents in the docket are listed in the https://www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statue. Certain other material, such
as copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in https://www.regulations.gov or in hard copy at:
Superfund Records Center, Mail Stop SFD-7C, 95 Hawthorne Street, Room
403, San Francisco, CA 94105. Phone: (415) 820-4700. Hours: Mon. thru
Fri.--8 a.m. to 5 p.m.
Heritage Park Regional Library, Reference Section, 14361 Yale Street,
Irvine, CA 92714. Phone: (949) 936-4040. Hours: Mon. thru Thu.--10 a.m.
to 9 p.m.; Sat.--10 a.m. to 5 p.m.; Sun.--12 p.m. to 5 p.m.
FOR FURTHER INFORMATION CONTACT: Mary Aycock, Remedial Project Manager,
U.S. Environmental Protection Agency, Region IX, Mail Code SFD81 75
Hawthorne Street, San Francisco, CA 94105, (415) 972-2389, email:
Aycock.Mary@epamail.epa.gov.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Introduction
II. NPL Deletion Criteria
III. Partial Deletion Procedures
IV. Basis for Site Partial Deletion
V. Partial Deletion Action
I. Introduction
EPA Region IX is publishing this direct final Notice of Partial
Deletion for the El Toro Marine Corp Air Station (Site), from the
National Priorities List (NPL). This partial deletion pertains to all
Site media, including soil and groundwater, of parcels I-A, II-A, III-
A, II-J, II-Q, II-S, II-T, III-C, I-C, II-U, I-B, I-E, I-G, I-H, I-I,
I-J, I-L, I-M, I-P, II-G, II-I, II-P, III-D, I-K, I-N, I-O, I-S, II-E,
II-L, II-M, II-R, I-Q, I-R, II-B, II-K, and II-O of the Site. The
properties proposed for deletion are shown in the map available in the
partial deletion docket and will be referred to hereafter as ``the
properties proposed for deletion.'' The NPL constitutes Appendix B of
40 CFR part 300 which is the Oil and Hazardous Substances Pollution
Contingency Plan (NCP), which EPA promulgated pursuant to Section 105
of the Comprehensive Environmental Response, Compensation and Liability
Act (CERCLA) of 1980, as amended. EPA maintains the NPL as the list of
sites that appear to present a significant risk to public health,
welfare, or the environment. Sites on the NPL may be the subject of
remedial actions financed by the Hazardous Substance Superfund (Fund).
This partial deletion of the El Toro Marine Corp Air Station is
proposed in accordance with 40 CFR 300.425(e) and is consistent with
the Notice of Policy Change: Partial Deletion of Sites Listed on the
National Priorities List. 60 FR 55466 (Nov. 1, 1995). As described in
300.425(e)(3) of the NCP, a portion of a site deleted from the NPL
remains eligible for Fund-financed remedial action if future conditions
warrant such actions.
Because EPA considers this action to be noncontroversial and
routine, this action will be effective January 21, 2014 unless EPA
receives adverse comments by December 19, 2013. Along with this direct
final Notice of Partial Deletion, EPA is co-publishing a Notice of
Intent for Partial Deletion in the ``Proposed Rules'' section of the
Federal Register. If adverse comments are received within the 30-day
public comment period on this partial deletion action, EPA will publish
a timely withdrawal of this direct final Notice of Partial Deletion
before the effective date of the partial deletion and the partial
deletion will not take effect. EPA will, as appropriate, prepare a
response to comments and continue with the deletion process on the
basis of the Notice of Intent for Partial Deletion and the comments
already received. There will be no additional opportunity to comment.
Section II of this document explains the criteria for deleting
sites from the NPL. Section III discusses procedures that EPA is using
for this action. Section IV discusses the properties proposed for
deletion of El Toro Marine Corp Air Station and demonstrates how they
meet the deletion criteria. Section V discusses EPA's action to
partially delete the Site parcels from the NPL unless adverse comments
are received during the public comment period.
II. NPL Deletion Criteria
The NCP establishes the criteria that EPA uses to delete sites from
the NPL. In accordance with 40 CFR 300.425(e), sites may be deleted
from the NPL where no further response is appropriate. In making such a
determination pursuant to 40 CFR 300.425(e), EPA will consider, in
consultation with the State, whether any of the following criteria have
been met:
i. Responsible parties or other persons have implemented all
appropriate response actions required;
ii. all appropriate Fund-financed response under CERCLA has been
implemented, and no further response action by responsible parties is
appropriate; or
iii. the remedial investigation has shown that the release poses no
significant threat to public health or the environment and, therefore,
the taking of remedial measures is not appropriate.
Pursuant to CERCLA section 121(c) and the NCP, EPA conducts five-
year reviews to ensure the continued protectiveness of remedial actions
where hazardous substances, pollutants, or contaminants remain at a
site above levels that allow for unlimited use and unrestricted
exposure. EPA conducts such five-year reviews even if a site is deleted
from the NPL. EPA may initiate further action to ensure continued
protectiveness at a deleted site if new information becomes available
that indicates it is appropriate. Whenever there is a significant
release from a site deleted from the NPL, the deleted site may be
restored to the NPL without application of the hazard ranking system.
III. Partial Deletion Procedures
The following procedures apply to the properties proposed for
deletion:
(1) EPA has consulted with the state of California prior to
developing this direct final Notice of Partial Deletion and the Notice
of Intent for Partial Deletion co-published in the ``Proposed Rules''
section of the Federal Register.
(2) EPA has provided the state 30 working days for review of this
notice and the parallel Notice of Intent for Partial Deletion prior to
their publication today, and the state, through the Department of Toxic
Substances Control, has concurred on the partial deletion of the Site
from the NPL.
(3) Concurrently with the publication of this direct final Notice
of Partial Deletion, a notice of the availability of the parallel
Notice of Intent for Partial Deletion is being published in a major
local newspaper, the Orange County Register. The newspaper notice
announces the 30-day public comment period concerning the Notice of
Intent for Partial Deletion of the Site from the NPL.
(4) The EPA placed copies of documents supporting the partial
deletion in the deletion docket and made these items available for
public inspection and copying at the Site information repositories
identified above.
(5) If adverse comments are received within the 30-day public
comment period on this partial deletion action, EPA will publish a
timely notice of
[[Page 69304]]
withdrawal of this direct final Notice of Partial Deletion before its
effective date and will prepare a response to comments and continue
with the deletion process on the basis of the Notice of Intent for
Partial Deletion and the comments already received.
Deletion of a portion of a site from the NPL does not itself
create, alter, or revoke any individual's rights or obligations.
Deletion of a portion of a site from the NPL does not in any way alter
EPA's right to take enforcement actions, as appropriate. The NPL is
designed primarily for informational purposes and to assist EPA
management. Section 300.425(e)(3) of the NCP states that the deletion
of a site from the NPL does not preclude eligibility for further
response actions, should future conditions warrant such actions.
IV. Basis for Site Partial Deletion
The following information provides EPA's rationale for deleting the
properties proposed for deletion from the NPL:
Site Background and History
The former El Toro Marine Corps Air Station (EPA ID: CA6170023208),
(El Toro MCAS) covering approximately 4,712 acres in the City of
Irvine, County of Orange, California is located at 33 degrees ([deg])
38 minutes (') to 33[deg]41' north latitude,117[deg]41' to 117[deg]45'
west longitude, Township 6 South, Range 6 West (T6S/R6W) (Sections 2-5,
7-11, 16-17, 20-21) and T5S/R8W (Sections 32-33, 35).
Development of former El Toro MCAS began in July 1942, when
construction of a United States Marine Corps pilot's fleet operational
training facility began on approximately 2,319 acres of land in Orange
County, California. The Site was commissioned as El Toro Marine Corps
Air Station on March 17, 1943. In 1950, the Station was selected for
development as a master jet air station and permanent center for marine
aviation of the west coast to support the operations and combat
readiness of Fleet Marine Forces, Pacific. Between 1944 and 1986,
additional land was acquired to bring the size of the on-station
portion of the installation to 4,712 acres.
Major activities at the Site contributing to the generation of
hazardous wastes included vehicle maintenance, ground support
maintenance, aircraft maintenance, and aircraft corrosion control.
Other waste generating activities included munitions disposal, pest
control, fire protection training, and laboratory operations including
photo development, non-destructive inspection, and fuel analysis.
Wastes generated by the maintenance operations included spent solvents
and waste oils (including TCE, TCA, MEK, toluene, and PD-680), fuels,
greases removed from the spent solvents, and spent strippers. Aircraft
washrack activities resulted in discharge of alkaline soaps,
detergents, and small amounts of PD-680. Vehicle and aircraft waste
discharge produced the greatest volume of industrial waste of any of
the base activities.
A number of potentially contaminated areas were identified on the
Site, including four landfills suspected of containing both hazardous
and solid waste, and other areas where polychlorinated biphenyls
(PCBs), battery acids, leaded fuels, and other hazardous substances
were suspected of being dumped or spilled. A Remedial Investigation
(RI) conducted by El Toro MCAS identified volatile organic compounds
(VOCs), primarily trichloroethene (TCE), in groundwater that migrated
more than three miles off base. The primary source of the groundwater
contamination was two large aircraft hangars. Land irrigated by wells
is located within three miles of the site; however, none of these wells
are drinking water sources. Surface water flows into the Upper Newport
Bay Ecological Reserve, located approximately eight miles from the
base.
In recent years, portions of the Site were transferred to different
governmental agencies. In 1998, the Bake Parkway/Interstate 5 public
highway expansion project was completed resulting in the transfer of
approximately 23 acres to the California Department of Transportation.
In 2001, 896.7 acres in the northeast portion of the station were
transferred to the Federal Aviation Administration.
The Site was decommissioned as an active base in July 1999. The
parcels to be deleted from the NPL have all been transferred from the
Department of the Navy (DON) to Heritage Fields LLC (Heritage Fields)
under the Base Realignment and Closure Act of 1995. Heritage Fields
plans to build a combination of residential, commercial, retail and
educational facilities on Site. In addition, Heritage Fields has
transferred 1,387 acres to the City of Irvine to create the Orange
County Great Park. The Orange County Great Park will be home to a
world-class Olympic-style sports village and entertainment center, a
new high school and neighborhood elementary schools, and infrastructure
and support for a substantially expanded Irvine transportation center.
Redevelopment efforts are on-going.
The Site was proposed to be placed on the NPL on June 24, 1988 (53
FR 23988); and was placed on the NPL on February 21, 1990 (55 FR 6154).
In October 1990, the U.S. EPA (EPA), California Department of Health
Services (CDPH) (the CDPH was the predecessor program to the California
Department of Health Toxic Substances Control (DTSC)), California
Regional Water Quality Control Board (RWQCB) and the DON signed a
Federal Facility Agreement (FFA) which formalized the process for
environmental response actions and the relative roles of the EPA, state
agencies, and the DON under CERCLA and the Installation Restoration
Program (IRP). The FFA was signed by the EPA, the State of California,
and the DON in October 1990.
Environmental Baseline Surveys (EBSs), which identify parcels of
land for sale, lease, or needing further investigation, were completed
in 1995 and 2003. The EBSs identified environmental factors and
locations of concern (LOCs) where further evaluation and/or actions
were ongoing or required. Once identified, these LOCs were reviewed by
the DON, state regulatory agencies and EPA. Based upon this review,
sites were either recommended for no further action (NFA) or for
further sampling. Based upon the subsequent sampling, those sites
either became NFA sites or proceeded to the more extensive
Comprehensive Environmental Response, Compensation, and Liability Act
(CERCLA) cleanup process.
The portions of the Site to be deleted from the NPL include 1,900.4
acres of contiguous property. All of these parcels have been
transferred from the DON to Heritage Fields. Prior to transferring
property at El Toro MCAS, the DON was required, pursuant to Section
102(h) of CERCLA, to document that all environmental impacts associated
with the DON's activities on the Site had been thoroughly investigated
and appropriate remedial actions have been taken to protect the public
health, welfare, and the environment. DON presented this documentation
in a series of successive Finding of Suitability to Transfer (FOST)
documents. In each case, the FOST described the LOCs on the property to
be transferred and the investigation and remedial actions taken at
those properties to obtain concurrence from the EPA, CDPH/DTSC and
RWQCB. A total of 7 FOSTs were finalized for all parcels to be deleted
between July 2005 and September 2012.
[[Page 69305]]
LOC site narratives where release, disposal, and/or migration of
hazardous substances occurred, but at concentrations that did not
require a removal or remedial action because site conditions were found
to be protective of both human health and the environment may be found
in a tables appendix in the Deletion Docket. This appendix does not
include LOCs that were only contaminated with petroleum, as these sites
are not subject to CERCLA based on the petroleum exemption. In total,
112 such LOCs were thoroughly evaluated and recommended for no further
action.
This partial deletion covers the following Site parcels: I-A, II-A,
III-A, II-J, II-Q, II-S, II-T, III-C, I-C, II-U, I-B, I-E, I-G, I-H, I-
I, I-J, I-L, I-M, I-P, II-G, II-I, II-P, III-D, I-K, I-N, I-O, I-S, II-
E, II-L, II-M, II-R, I-Q, I-R, II-B, II-K, and II-O. A map identifying
the areas to be deleted, as well as the areas to remain on the NPL, is
available in the partial deletion docket.
1. Property Covered by FOST 1
Approximately 2,798 acres of the Site were covered by FOST
1, including 1,070.2 acres that EPA determined had not been
impacted by hazardous waste and that therefore were not part of the
NPL. These two areas of the Site were removed from the NPL through two
clarification letters issued by EPA. Clarification Areas A, B, C, and
D, consisting of 978.6 acres, were removed from the NPL through an EPA
clarification letter dated October 27, 2005. Clarification Area E,
consisting of 91.6 acres, was removed from the NPL through an EPA
clarification letter dated March 21, 2006.
The unclarified portions of the FOST 1 area consisted of
three Transfer Parcels: Transfer Parcels I-A, II-A, and III-A.
1.1 Transfer Parcel I-A
Transfer Parcel I-A was approximately 809.5 acres. This parcel
contained 225 non-demolished buildings/structures/facilities including
the units located in the Saddleback Terrace housing area. In addition,
Parcel I-A contained IRP Site 20--Hobby Shop and a portion of IRP Site
25--Major Drainages.
1.1.1 IRP Site 20--Hobby Shop
Site Location and History
IRP Site 20--Hobby Shop encompassed approximately 0.5 acre
immediately northwest of the intersection of North 9th Street and West
Marine Way and included Building 626. Beginning in 1967, the site was
used as an auto shop for military personnel to service and repair
privately owned vehicles. Kerosene was reportedly used to wash down the
paved area at the site until approximately 1976. The wash runoff
drained into a catch basin situated in the entry driveway and finally
drained into an oil/water separator (OWS). From 1976 until closure of
the Hobby Shop in 1999, a biodegradable soap was used in place of
kerosene.
Site 20 originally consisted of four units:
Unit 1--Shallow Drainage Swale (1-2 feet below grade),
adjacent to the east side of Building 626.
Unit 2--South Drainage Ditch, ran along North 9th Street
Unit 3--Stained Area, small area adjacent to the northwest
side of Building 626
Unit 4--Inner Courtyard of Building 626, an entry
driveway, and a front-sloping area adjacent to the drainage ditch along
North 9th Street. The inner portion was paved with asphalt. The entry
driveway was concrete and crossed over the drainage ditch. The front
area was covered with grass with some bare spots and various trees.
Remedial Investigations
Investigations at the IRP Site 20 included a RCRA Facility
Assessment (RFA), a Phase I RI, aerial photograph surveys in 1993, and
a Phase II RI in 1996. In 1997, Units 2 and 3 were excluded from the
site based on the CERCLA petroleum exemption, 42 U.S.C. 9601(14)(F).
Sites containing only petroleum contamination were, and continue to be
remediated under the oversight of the RWQCB).
Soil sampling identified VOCs, semi-volatile organic compounds
(SVOCs), PCBs, and pesticides at the site, all below residential PRGs.
Arsenic was detected at concentrations above the former El Toro MCAS
background value. The RI of the site indicated that the site-related
contamination was limited to the shallow soil interval.
Selected Remedy
The human health and ecological risk assessments showed that the
contaminants present in the soil did not present an unacceptable risk
to human health or the environment. Therefore, no remedial action was
required. A Record of Decision (ROD) for NFA was signed on September
30, 1997. No risks are present at IRP Site 20 and no institutional
controls are present.
Response Actions and Cleanup Standards
No response actions have been taken and no cleanup standards have
been set.
Operation and Maintenance
No operation and maintenance is required for this site.
1.1.2 IRP Site 25--Major Drainages
IRP Site 25 encompassed approximately 22 acres and comprised the
four major washes that flowed through former El Toro MCAS. These
included Agua Chinon Wash, Bee Canyon Wash, Borrego Canyon Wash, and
Marshburn Channel. Three of these drainages (Agua Chinon Wash, Bee
Canyon Wash, and Borrego Canyon Wash) were continuations of natural
washes that originated in the Santa Ana Mountains. Surface drainage
from the hills and upgradient irrigated farmland combined with runoff
generated from extensive paved surfaces at former El Toro MCAS. The on-
station storm sewer system discharged to the drainage channels, which
then flowed into San Diego Creek. San Diego Creek discharged into upper
Newport Bay, about 7 miles downstream from its intersection with
Marshburn Channel. These washes traversed Transfer Parcels I-A, II-A,
and III-A, and also traversed property that was not part of FOST
1.
Remedial Investigations
IRP Site 25 was constituted before the source of the regional VOC
groundwater contamination had been identified as IRP Site 24 (which is
not part of this deletion). IRP Site 25 was identified for a Phase II
RI, but the drainages were investigated as part of the Phase I RI for
IRP Sites 18 and 24 to evaluate the source of the off-site VOC
groundwater plume. Potential contamination within the major drainages
and San Diego Creek was assessed by analyzing surface water, sediment,
soil, and soil gas samples. Except for the Borrego Canyon Wash, metals
and pesticides were detected above former El Toro MCAS background
concentrations in all drainages. Significant petroleum hydrocarbon
contamination was detected at depths of 15 to 20 feet below ground
surface (bgs) at the southern end of Agua Chinon Wash, near the former
El Toro MCAS boundary.
Within the Agua Chinon Wash, total petroleum hydrocarbons (TPH)
were detected at depths up to 57 feet bgs. The RI of the site indicated
that the site-related contamination was limited to sediment and surface
water.
Selected Remedy
The human health and ecological risk assessments showed that the
contaminants present in these media did not present an unacceptable
risk to human health or the environment. Therefore, no remedial action
was
[[Page 69306]]
required. The Draft Final RI Report was completed in 1997, and a ROD
for NFA was signed on September 30, 1997. No risks are present at IRP
Site 25 and no institutional controls are present.
Response Actions and Cleanup Standards
No response actions have been taken and no cleanup standards have
been set.
Operation and Maintenance
No operation and maintenance is required for this site.
1.2 Transfer Parcel II-A
Transfer Parcel II-A was approximately 1,439.6 acres. This parcel
contained a golf course and 1,078 non-demolished buildings/structures/
facilities which included the units located in San Joaquin, Vista
Terrace, Navy/Marine (NAMAR), and Wherry housing areas. Transfer Parcel
II-A included IRP Sites 6 and 19, and a portion of IRP Site 25
(described above).
1.2.1 IRP Site 6--Drop Tank Drainage Area No. 1
Site Location and History
IRP Site 6 encompassed approximately 3 acres bounded by taxiways to
the north and west, a concrete aircraft parking apron to the east, and
East Marine Way to the south. The site consisted of three units:
Unit 1 was an area along the edge of a concrete parking
apron where aircraft drop tanks were formerly drained of residual jet
fuel and then cleaned prior to reuse.
Unit 2 was a shallow drainage swale that extends from the
north side of Building 727, west to a catch basin that eventually
discharged into the Agua Chinon Wash. The catch basin received surface
runoff and sediment from the site.
Unit 3 was a flat, grass-covered area south of the
drainage swale where drop tanks were stored.
From 1969 to 1983, aircraft drop tanks were transported to the site
where the fuel remaining in the tanks was drained. Residual jet
propulsion fuel, grade 5 (JP 5) in the tanks was drained to the
concrete apron, and the combined fuel/rinse water ran onto the adjacent
grassy area. In addition to fuel, waste lubricant oils from maintenance
operations were also reportedly stored in drums and staged in the area.
Approximately 1,400 gallons of JP 5 fuel were reportedly drained
from the drop tanks onto the concrete apron and washed onto the
adjacent area. Portions of the unpaved areas at the site were also
reportedly used for storing oil drums. It was estimated that
approximately 300 gallons of waste oil leaked from these storage drums
at the site.
Remedial Investigations
Investigations conducted at IRP Site 6 included a Phase I remedial
investigation (RI) and aerial photograph surveys in 1993, employee
interviews in 1994, and a Phase II RI in 1996. During the
investigations, VOCs, SVOCs, and polynuclear aromatic hydrocarbons were
detected at concentrations below residential PRGs. The maximum arsenic
concentration was detected at a depth of Property of 8-10 feet bgs and
was above the former El Toro MCAS background concentration for arsenic.
The RI of the site indicated that the site-related contamination was
limited to the shallow soil interval.
Selected Remedy
The human health and ecological risk assessments indicated that the
contaminants present in the soil did not present an unacceptable risk
to human health or the environment. Therefore, no remedial action was
required. A ROD for NFA was signed on September 30, 1997.
Response Actions and Cleanup Standards
No response actions have been taken and no cleanup standards have
been set.
Operation and Maintenance
No operation and maintenance is required for this site.
1.2.2 IRP Site 19--Aircraft Expeditionary Refueling Site
Site Location and History
IRP Site 19 was within Transfer Parcel II-A and encompassed
approximately 4 acres southwest of Buildings 404 and 414. Between 1964
and 1986, the site operated as a fuel-storage and fuel-dispensing area.
The site consisted of six 20,000-gallon JP 5 fuel bladders in 4-foot-
high earthen revetments and associated piping and fuel-dispensing
equipment. The site originally consisted of four units:
Unit 1, Northeast Stained Area
Unit 2, Excavated Areas;
Unit 3, Stained Area Around Excavations; and
Unit 4, Pump Station (this area was added for the Phase II
RI and then was removed under the CERCLA petroleum exclusion).
Initial Response
Various spills and leaks reportedly occurred during operation of
the site. In one instance, an estimated 20,000 gallons of JP 5 were
reportedly released after a bladder rupture. Petroleum hydrocarbons
were detected in the soil beneath the ruptured bladder.
The fuel bladders were removed in 1986, and the soil was excavated
to a maximum depth of 15 feet bgs in a 30-foot-square area beneath the
location of the bladder rupture (Unit 2). The excavation was partially
backfilled to a depth of approximately 11 feet in 1994. Prior to
backfill, soil samples were collected within the excavated area, i.e.,
IRP Site 19. No chemicals of potential concern were detected at
concentrations greater than EPA industrial PRGs. In 1996, the remaining
excavation was backfilled to grade the surrounding area with clean fill
material. An additional 19,000-square-foot area beneath the locations
of the other bladders was also excavated in 1986 to a depth of
approximately 2.5 feet. All of the buildings/structures/facilities at
the site were removed following site closure and were replaced by a
pump station and UST complex situated adjacent to the east side of the
site.
Remedial Investigations
Investigations conducted at the site included a Phase I RI and
aerial photograph surveys in 1993, employee interviews in 1994, and a
Phase II RI in 1996. The investigations indicated SVOCs at
concentrations below residential PRGs, with the exception of
benzo(a)pyrene, which was above the industrial PRG value. VOCs were
detected at concentrations below residential PRGs. Arsenic was detected
at concentrations above the industrial PRG value, and the maximum
arsenic value was above the former El Toro MCAS background
concentration.
Selected Remedy
The human health and ecological risk assessments showed that the
contaminants present in the soil did not present an unacceptable risk
to human health or the environment. A ROD for NFA for Units 2 and 3 was
signed on September 30, 1997. Unit 1 was excluded from the IRP under
the CERCLA petroleum exclusion in 1995 (closed by RWQCB in a letter
dated May 14, 1997), and Unit 4 was excluded from the IRP under the
CERCLA petroleum exclusion in 1997 (Unit 4 was being addressed with a
number of USTs and the associated area was therefore unsuitable for
transfer and was not part of FOST 1).
Response Actions and Cleanup Standards
No further response actions have been taken.
[[Page 69307]]
Operation and Maintenance
No operation and maintenance is required for this site.
1.2.3 PCB T56, concrete pad of transformer 56
Site Location and History
A minor release of transformer oil containing PCBs
Selected Remedy
No risks are present at PCB T56 and no institutional controls are
present.
Response Actions and Cleanup Standards
The transformer was replaced and the concrete pad was removed. No
further action was required.
Operation and Maintenance
No operation and maintenance is required for this site.
1.3 Transfer Parcel III-A
Transfer Parcel III-A was approximately 329.0 acres. This parcel
contained 10 non-demolished buildings/structures/facilities, as well as
a portion of IRP Site 13.
1.3.1 IRP Site 13--Oil Change Area
Site Location and History
IRP Site 13 encompassed approximately 34,000 square feet and was
bounded on the north by Former Tank Farm No. 2 and on the south by the
storage yard for Building 242. The site was situated within Transfer
Parcel III-A and Carve-Out (CO) III-B. The site was relatively flat,
unpaved, and generally unvegetated. Site 13 consisted of two units:
Unit 1 comprised the area southeast of Tank Farm No. 2 and Unit 2
comprised the area southwest of Tank Farm No. 2. Trucks were driven to
the area southeast of the tank farm (Unit 1) for oil changes, and crank
case oil was frequently drained onto the ground. From 1977 to 1983,
approximately 7,000 gallons of waste oil were drained onto the ground.
The oily soil was subsequently removed, and no visible evidence of the
oily soil remained. A review of aerial photographs indicated heavy
staining throughout the area between the tank farm and Building 242
(Unit 2), which persisted over the years of photographic record. It is
likely that oil changes were also conducted in that area.
Remedial Investigations
Investigations conducted at the site included an RFA, a Phase I RI
and aerial photographic surveys in 1993, and employee interviews in
1994. VOCs, SVOCs, polynuclear aromatic hydrocarbons, and pesticides
were detected at concentrations below residential PRGs. Arsenic was
detected at concentrations above the industrial PRG from the surface to
a depth of 80 feet bgs. The maximum arsenic concentration was below the
former El Toro MCAS background concentration. Total recoverable
petroleum hydrocarbons (TRPH) were detected at the soil surface and at
a depth of 5 feet bgs. Based on the results of the Phase I RI
investigation, a Phase II RI was not recommended. The RI of the site
indicated that the site-related contamination was limited to the
shallow soil interval.
Selected Remedy
The human health and ecological risk assessments showed that the
contaminants present in the soil did not present an unacceptable risk
to human health or the environment. A ROD for NFA was signed on
September 30, 1997.
Response Actions and Cleanup Standards
No response actions have been taken and no cleanup standards have
been set.
Operation and Maintenance
No operation and maintenance is required for this site. No deed
restrictions were recommended for Site 13 due to chemicals present in
the soil. However since the groundwater beneath Site 13 was
contaminated by trichloroethylene (TCE) and tetrachloroethylene (PCE;
also perchloroethylene) due to Site 24--VOC source area, when the NFA
ROD was signed on September 30, 1997, the use restrictions prohibiting
drilling of wells and/or extraction of groundwater and allowing access
for groundwater monitoring and maintenance of equipment associated with
groundwater remediation were to be addressed in the ROD for Site 18 and
Site 24. When the Final ROD for Site 18 and Site 24 was completed in
2002, the updated VOC plume and 500 foot buffer zone were no longer
located beneath Site 13. Consequently, groundwater restrictions due to
the Site 24 VOC plume were no longer applicable for Site 13.
2. Property Covered by FOST 2
Approximately 8 acres of El Toro MCAS were covered by FOST
2. This area consisted of four Transfer Parcels (II-J, II-S,
II-T, and III-C), and a portion of one Transfer Parcel (II-Q). Transfer
parcels II-J and II-Q did not contain any CERCLA LOCs. Transfer Parcel
II-T was approximately 0.5 acres in size and contained one building/
structure/facility (Building 761). Transfer Parcel III-C was
approximately 1 acre in size and contained one building/structure/
facility (Building 240). NFA determinations were made for all LOCs
within Transfer Parcels II-T and III-C.
2.1 Transfer Parcel II-S
Transfer Parcel II-S was approximately 1.3 acres in size and
included six buildings/structures/facilities (Buildings 374, 377, 447,
448, 566, and 726) and former Building 603 (demolished).
2.1.1 RFA 131
Site Location and History
RFA 131, an engine test cell, was located within Transfer Parcel
II-S near Building 447.
Initial Response
Near surface soils were removed in 1997.
Selected Remedy
DTSC concurred with NFA in a letter from July 1999. RWQCB concurred
with NFA in June 2000.
Response Actions and Cleanup Standards
No further response actions have been taken.
Operation and Maintenance
No operation and maintenance is required for this site.
3. Property Covered by FOST 3
Approximately 3.9 acres of El Toro MCAS were covered by FOST
3.
Site Location and History
This area consisted of two Transfer Parcels referred to in FOST
3 as ``Carve-Outs'' (COs):
CO I-C consisted of approximately 0.1 acre in the
northeastern portion of the former base. This CO was created during
preparation of the 2004 Finding of Suitability to Lease when a portion
of an underground pipeline (Norwalk-El Toro Pipeline) was believed to
exist within this area. However, based on a detailed review of the
pipeline physical alignment, it was determined that no portion of the
pipeline was within Transfer Parcel I-C. No buildings or utilities were
located on the Transfer Parcel.
CO II-U consisted of approximately 3.8 acres in the
northeastern portion of the former base. No buildings or utilities were
located on the CO.
Initial Response
A portion of the Norwalk-El Toro Pipeline was removed from CO II-U
in the fall of 2006, with the exception of
[[Page 69308]]
approximately 100 feet of pipeline that remains under Agua Chinon Wash.
Remedial Investigations
The COs were evaluated during the initial phase of environmental
assessment and the results were documented in the Final 2003 EBS. The
EBS concluded that no hazardous substances were stored or released on
the COs.
Selected Remedy
No further action was necessary in these areas.
Response Actions and Cleanup Standards
No response actions have been taken and no cleanup standards have
been set.
Operation and Maintenance
No operation and maintenance is required for this site.
4. Property Covered by FOST 4
Approximately 42.9 acres of El Toro MCAS were covered by FOST
4.
Site Location and History
This area consisted of thirteen COs: COs I-B, I-E, I-G, I-H, I-I,
I-J, I-L, I-M, I-P, II-G, II-I, II-P, III-D. COs I-L, I-M, I-P, II-G,
II-I, and II-P did not contain CERCLA LOCs.
Remedial Investigations
As these COs did not contain CERCLA LOCs, no remedial
investigations were conducted.
Selected Remedy
No Further Action determinations were issued for all LOCs within
COs I-B, I-E, I-G, I-H, I-I, I-J, and II-G. CO III-D contained a
portion of IRP Site 13. All other LOCs in CO III-D received NFA
determinations and no cleanup was required.
Response Actions and Cleanup Standards
No response actions have been taken and no cleanup standards have
been set.
Operation and Maintenance
No operation and maintenance is required for these sites.
5. Property Covered by FOST 5
Approximately 119.3 acres of El Toro MCAS were covered by FOST
5.
Site Location and History
This area included nine COs: COs I-F, I-K, I-N, I-O, I-S, II-E, II-
L, II-M, II-R, and CO Building 746. CO I-F is not part of this deletion
request and will remain on the NPL. CO Building 746 is located within
CO II-D and is not part of this partial deletion request and will also
remain on the NPL. COs I-K, I-N, I-O, I-S contained only petroleum LOCs
or no release, disposal, and/or migration of hazardous substances
occurred there.
Remedial Investigations
As these COs did not contain CERCLA LOCs, no remedial
investigations were conducted.
Selected Remedy
No Further Action determinations were issued for all LOCs within CO
II-E and II-M. CO II-L contained a portion of IRP Site 25. All other
LOCs in CO II-L received NFA determinations and no cleanup was
required.
Response Actions and Cleanup Standards
No response actions have been taken and no cleanup standards have
been set.
Operation and Maintenance
No operation and maintenance is required for these sites.
5.1 CO II-R
CO II-R consisted of approximately 1.2 acres and was located in the
southeast portion of the former base.
5.1.1 Resource Conservation and Recovery Act (RCRA) Facility Assessment
(RFA) Site 244/PCB T74
Site Location and History
There was one pad-mounted transformer (PCB T74) at Building 457.
Historically, disposal activities were conducted at this site, though
the dates of these operations are unknown. A response action was
required for releases of transformer oil containing PCBs at Building
457 (RCRA Facility Assessment (RFA) Site 244).
Remedial Investigations
While no remedial investigations were conducted under CERCLA, RFA
Site 244/PCB T74 was evaluated under a RCRA Facility Assessment.
Selected Remedy
DTSC concurred with NFA for RFA 244 in a letter dated December
1998. EPA and DTSC concurred with NFA for PCB T74 in September 2003.
Response Actions and Cleanup Standards
Shallow soil samples that were collected in the area affected by
the PCB release identified PCBs in one of the seven samples collected.
The transformer was replaced and removal of impacted soils was
completed in 1997. The response action was completed and closed in
December 1998. No evidence of a release was observed during the visual
site inspections conducted for the 2003 EBS. Building 457 was
subsequently demolished to its foundation.
Operation and Maintenance
No operation and maintenance is required for this site.
6. Property Covered by FOST 6
Approximately 356.81 acres of El Toro MCAS were covered by FOST
6.
Site Location and History
This area included eleven COs: COs I-D, I-Q, I-R, II-B, II-K, II-N,
II-O, III-B-1, III-B-2, III-E, and III-F. COs I-Q and I-R contained
only petroleum LOCs and were therefore subject to the CERCLA petroleum
exclusion, or no release, disposal, and/or migration of hazardous
substances occurred there. As a result, these COs are not discussed in
this document. Additionally, COs I-D, II-N, III-B-1, III-B-2, III-E,
and III-F are not part of this partial deletion request and will remain
on the NPL.
Remedial Investigations
As these COs did not contain CERCLA LOCs, no remedial
investigations were conducted.
Selected Remedy
COs II-K contained a portion of IRP Site 25. All other LOCs in CO
II-K received NFA determinations and no cleanup was required. All LOCs
in CO II-O received NFA determinations and no cleanup was required.
Response Actions and Cleanup Standards
No response actions have been taken and no cleanup standards have
been set.
Operation and Maintenance
No operation and maintenance is required for these sites.
6.1 CO II-B
CO II-B consisted of approximately 6.73 acres located in the
northeast portion of the former base.
6.1.1 Temporary Accumulation Area (TAA) Site 130C
Site Location and History
TAA 130C was located northing of Building 130.
Remedial Investigations
While no remedial investigations were conducted under CERCLA, TAA
130C was evaluated under a RCRA Facility Assessment. Sampling indicated
low levels of arsenic and chlorinated pesticides.
[[Page 69309]]
Selected Remedy
TAA 130C received site closure concurrence from DTSC in March 2009.
No further action was required.
Response Actions and Cleanup Standards
Contaminated soil was excavated and confirmation soil samples were
collected at TAA 130C in 2008.
Operation and Maintenance
No operation and maintenance is required for this site.
7. Property Covered by FOST 7
Approximately 151.06 acres of El Toro MCAS were covered by FOST
7. This area included three COs: COs II-F-1, II-Q, and II-V-1.
There were no CERCLA LOCs within CO II-F-1 or CO II-V-1. As a result,
COs II-F-1 and II-V-1 are not discussed in this document. Any
contamination on these COs was, and continues to be remediated under
the oversight of the RWQCB.
7.1 CO II-Q
CO II-Q consisted of approximately 84.49 acres located in the
central portion of the former base and contained buildings 114, 124,
125, 126, 127, 230, 231, 363, 372, 642, 658, 677, 698, 716, 747, 752,
763, 779, 903, 923, 938, 952, and 1804. CO II-Q also contained
structures 396, 558, 559, 560, 561, 659, 904, 905, 906, 907, 908, 909,
910, and 911. The DON leased this CO to Heritage Fields, LLC, who
subsequently assigned the lease for the majority of this CO to the City
of Irvine. CO II-Q includes portions of IRP 4 and 25.
7.1.1 IRP Site 4
Site Location and History
IRP Site 4 is located immediately southeast of Building 658, a
former jet-engine testing facility. The site is bounded by 9th Street
to the south, Building 658 to the north and west, and Tank Farm No. 5
to the east. The IRP Site 4 consists of two units: Unit 1 is an oil-
stained area southeast of Building 658 which overlaps a concrete
transformer pad, and Unit 2 is a drainage ditch which received runoff
from a ferrocene spill.
The staining at Unit 1 was the result of oily discharges from
Building 658, which were observed over an approximate 2-year period.
The contamination at Unit 2 originated from an August 1983 spill, when
the contents of a 500-gallon tank (wash water and residual jet fuel)
reportedly overflowed during washing and spilled onto the ground,
draining into a ditch adjacent to 9th Street. The spilled liquid
reportedly contained approximately 5 gallons of ferrocene and a
hydrocarbon carrier solution.
Remedial Investigations
Investigations conducted at IRP Site 4 included a Phase I RI and
aerial photograph surveys in 1993. VOCs and SVOCs were below
residential PRGs in both units.
Selected Remedy
The human health and ecological risk assessments showed that the
contaminants present in the soil did not present an unacceptable risk
to human health or the environment. Therefore, no remedial action was
required. The NFA ROD was signed on September 30, 1997.
Response Actions and Cleanup Standards
No response actions have been taken and no cleanup standards have
been set.
Operation and Maintenance
No operation and maintenance is required for this site.
Five Year Reviews
Cleanup activities at El Toro MCAS have resulted in the remediation
of all Site-related contamination such that restrictions on use and/or
institutional controls were unnecessary. Accordingly, no Five-Year
Reviews were required under CERCLA.
Community Involvement
Public participation activities have been satisfied as required in
CERCLA Section 113(k), 42 U.S.C. 9613(k) and CERCLA Section 117, 42
U.S.C. 9617. Community input has been sought by the DON throughout the
cleanup process. The El Toro MCAS Restoration Advisory Board (RAB)
serves as a focal point for the exchange of information about
environmental restoration activities between the DON, regulatory
agencies, and the local community. RAB members review technical reports
and plans pertaining to the El Toro MCAS cleanup and provide input to
the DON and the regulatory agencies. RAB members serve as volunteers
and act as a liaison to the specific community they represent including
various cities and homeowner associations in the vicinity of El Toro
MCAS. All RAB meetings are open to the public and anyone interested may
attend. They are held semi-annually on a Wednesday evening in April and
November at the Irvine City Hall, One Civic Center Plaza.
Community involvement for the areas that are the subject of this
document has occurred by soliciting public comment on various documents
depending on the site's investigation and cleanup (if needed) process.
All NFA decision documents were issued for 30-day public comment
periods with comments, if any, addressed in the Responsiveness Summary
of the Record of Decision. In addition, sites where non-time critical
removal actions occurred provided public involvement with the issuance
of the engineering evaluation/cost analysis for public comment.
Since there are a number of ongoing investigations and cleanup at
El Toro MCAS, community involvement activities such as the biannual RAB
meetings will continue to occur.
Determination That the Criteria for Deletion Have Been Met
The NCP (40 CFR 300.425(e)) states that a site may be deleted from
the NPL when no further response action is necessary. EPA, in
consultation with the State of California, has determined that all
appropriate response actions under CERCLA have been completed on the
properties proposed for deletion. Therefore, these portions of the
former El Toro Marine Corps Air Station meet the criteria of 40 CFR
300.425(e) and may be deleted from the NPL. The State of California,
through the DTSC, concurred on this proposed deletion by letter dated
February 1, 2013.
V. Partial Deletion Action
The EPA, with concurrence of the State of California through the
Department of Toxic Substances Control, has determined that all
appropriate response actions under CERCLA have been completed.
Therefore, EPA is deleting parcels I-A, II-A, III-A, II-J, II-Q, II-S,
II-T, III-C, I-C, II-U, I-B, I-E, I-G, I-H, I-I, I-J, I-L, I-M, I-P,
II-G, II-I, II-P, III-D, I-K, I-N, I-O, I-S, II-E, II-L, II-M, II-R, I-
R, II-B, II-K, and II-O of the El Toro Marine Corp Air Station Site
from the NPL.
Because EPA considers this action to be noncontroversial and
routine, EPA is taking it without prior publication. This action will
be effective January 21, 2014 unless EPA receives adverse comments by
December 19, 2013. If adverse comments are received within the 30-day
public comment period, EPA will publish a timely withdrawal of this
direct final notice of partial deletion before the effective date of
the partial deletion and it will not take effect. EPA will prepare a
response to comments and continue with the deletion process on the
basis of the notice of intent to partially delete and the comments
[[Page 69310]]
already received. There will be no additional opportunity to comment.
List of Subjects in 40 CFR Part 300
Environmental protection, Air pollution control, Chemicals,
Hazardous waste, Hazardous substances, Intergovernmental relations,
Penalties, Reporting and recordkeeping requirements, Superfund, Water
pollution control, Water supply.
Dated: October 22, 2013.
Jared Blumenfeld,
Regional Administrator Region IX.
For the reasons set out in this document, 40 CFR part 300 is
amended as follows:
PART 300--[AMENDED]
0
1. The authority citation for part 300 continues to read as follows:
Authority: 33 U.S.C. 1321(c)(2); 42 U.S.C. 9601-9657; E.O.
12777, 56 FR 54757, 3 CFR 1991 Comp., p. 351; E.O. 12580, 52 FR
2923, 3 CFR 1987 Comp., p. 193.
Appendix B--[Amended]
0
2. Table 2 of Appendix B to part 300 is amended by revising the entry
under ``El Toro Marine Corps Air Station'', California to read as
follows:
Appendix B to Part 300--National Priorities List
* * * * *
Table 2--Federal Facilities Section
----------------------------------------------------------------------------------------------------------------
State Site name City/county Notes (a)
----------------------------------------------------------------------------------------------------------------
* * * * * * *
CA............................... El Toro Marine Corps Air Station El Toro.................... P
* * * * * * *
----------------------------------------------------------------------------------------------------------------
(a) * * *
*P = Sites with partial deletion(s).
[FR Doc. 2013-27724 Filed 11-18-13; 8:45 am]
BILLING CODE 6560-50-P