National Oil and Hazardous Substances Pollution Contingency Plan; National Priorities List: Partial Deletion of the South Valley Superfund Site, 36838-36844 [2018-16257]
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36838
Federal Register / Vol. 83, No. 147 / Tuesday, July 31, 2018 / Proposed Rules
Regulatory Impact Analysis (RIA). Page
33 of the RIA discusses the availability
of annual accident data for 2014–2016,
and includes a footnote (footnote 32)
indicating the source of the accident
data. The footnote states: ‘‘EPA. April
2018. Risk Management Plan (RMP)
Facility Accident Data, 2014–2016.
USEPA, Office of Emergency
Management.’’ This footnote should
read ‘‘EPA. March 2018. Risk
Management Plan (RMP) Facility
Accident Data, 2014–2016. USEPA,
Office of Emergency Management.’’
The other location is on page 34968
of ‘‘Accidental Release Prevention
Requirements: Risk Management
Programs Under the Clean Air Act;
Notification of Data Availability and
Extension of Comment Period,’’ 83 FR
34967, 34968 (July 24, 2018), in the
SUPPLEMENTARY INFORMATION section.
Column two of this page also discusses
the 2014–2016 accident data, but
incorrectly indicates that EPA
developed the docketed spreadsheet
containing these data from the
November 2017 version of the RMP
database. The last sentence of the
carryover paragraph at the top of
column two should read: ‘‘EPA
developed the latter spreadsheet from
the March 2018 version of the
database.’’
While the facility count information
discussed in the Notification of Data
Availability was based on the November
2017 version of the RMP database, EPA
extracted the 2014–2016 accident data
from the March 2018 version of the RMP
database, as indicated above. EPA notes
that the previously docketed 2014–2016
accident spreadsheet contains an
additional 25 accident records for the
2014–2016 period that were not
available when the November 2017
version of the database was created. By
using a later version of the database to
extract accident records, EPA provided
more up-to-date accident information to
support the regulatory record. However,
users who attempt to replicate EPA’s
2014–2016 accident spreadsheet by
extracting accident data from the
November 2017 version of the RMP
database (which was recently added to
the rulemaking docket as EPA–HQ–
OEM–2015–0725–0989) would not see
the additional 25 accident records.
EPA has added a memo to the
rulemaking docket dated July 25, 2018,
with the subject line: Corrections to
References to Risk Management Plan
Accident Information for 2014–2016.
This memo explains the corrections
discussed above and includes a list of
the 25 accidents that are included in the
2014–2016 spreadsheet but not in the
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November 2017 version of the RMP
database.
Dated: July 25, 2018.
Reggie Cheatham,
Director, Office of Emergency Management.
[FR Doc. 2018–16372 Filed 7–30–18; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 300
[EPA–HQ–SFUND–1983–0002; FRL–9981–
39—Region 6]
National Oil and Hazardous
Substances Pollution Contingency
Plan; National Priorities List: Partial
Deletion of the South Valley Superfund
Site
Environmental Protection
Agency (EPA).
ACTION: Proposed rule; notice of intent.
AGENCY:
The Environmental Protection
Agency (EPA) Region 6 is issuing a
Notice of Intent to Delete Operable
Units 1, 2, and 5 of the South Valley
Superfund Site (Site) located in
Albuquerque, New Mexico, from the
National Priorities List (NPL) and
requests public comments on this
proposed action. 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). The EPA and
the State of New Mexico, through the
New Mexico Environment Department,
have determined that all appropriate
response actions at these identified
parcels under CERCLA have been
completed, other than five-year reviews
and operation and maintenance
activities. However, this deletion does
not preclude future actions under
Superfund. This partial deletion
pertains to Operable Units 1, 2, and 5.
The remaining Operable Units 3, 4, and
6 will remain on the NPL and are not
being considered for deletion as part of
this action.
DATES: Comments must be received by
August 30, 2018.
ADDRESSES: Submit your comments,
identified by Docket ID no. EPA–HQ–
SFUND–1983–0002, by one of the
following methods:
• https://www.regulations.gov . Follow
the online instructions for submitting
comments. Once submitted, comments
cannot be edited or removed from
Regulations.gov. The EPA may publish
SUMMARY:
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any comment received to its public
docket. Do not submit electronically any
information you consider to be
Confidential Business Information (CBI)
or other information whose disclosure is
restricted by statute. Multimedia
submissions (audio, video, etc.) must be
accompanied by a written comment.
The written comment is considered the
official comment and should include
discussion of all points you wish to
make. The EPA will generally not
consider comments or comment
contents located outside of the primary
submission (i.e. on the web, cloud, or
other file sharing system). For
additional submission methods, the full
EPA public comment policy,
information about CBI or multimedia
submissions, and general guidance on
making effective comments, please visit
https://www2.epa.gov/dockets/
commenting-epa-dockets.
• Email: hebert.michael@epa.gov.
• Mail: Michael A. Hebert, Remedial
Project Manager, EPA Region 6, Mail
Code—6SF–RL, 1445 Ross Avenue,
Dallas, Texas 75202–2733.
• Hand delivery:
Æ Michael A. Hebert, Remedial Project
Manager, EPA Region 6, Mail Code—
6SF–RL, 7th Floor Reception Area,
1445 Ross Avenue, Dallas, Texas
75202–2733.
Æ Such deliveries are only accepted
during the Docket’s normal hours of
operation (Monday through Friday, 7
a.m. to 4 p.m.) and special
arrangements should be made for
deliveries of boxed information.
Instructions: Direct your comments to
Docket ID no. EPA–HQ–SFUND–1983–
0002. The https://www.regulations.gov
website 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
encryption, and be free of any defects or
viruses.
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Federal Register / Vol. 83, No. 147 / Tuesday, July 31, 2018 / Proposed Rules
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 statute. Certain other
material, such as copyrighted material,
will be publicly available only in the
hard copy. Publicly available docket
materials are available either
electronically in https://
www.regulations.gov or in hard copy at:
Zimmerman Library, Government
Information Department, University of
New Mexico, Albuquerque NM 87131,
505.277.9100, Monday–Thursday—7
a.m.–2 a.m., Friday—7 a.m.–9 p.m.,
Saturday—10 a.m.–6 p.m., Sunday—
12 p.m.–2 a.m.
New Mexico Environment Department,
Harold Runnels Building, 1190 St.
Francis Drive, Santa Fe, NM 87505,
505.827.2855, Monday–Friday—8
a.m.–5 p.m.
FOR FURTHER INFORMATION CONTACT:
Michael A. Hebert, Remedial Project
Manager, U.S. Environmental Protection
Agency, Region 6, Mail Code—6SF–RL,
1445 Ross Avenue, Dallas, Texas,
75202–2733, (214) 665–8315, email:
hebert.michael@epa.gov.
SUPPLEMENTARY INFORMATION:
Table of Contents
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I. Introduction
II. NPL Deletion Criteria
III. Deletion Procedures
IV. Basis for Intended Partial Site Deletion
I. Introduction
EPA Region 6 announces its intent to
delete Operable Units 1, 2, and 5 of the
South Valley Superfund Site (Site), from
the National Priorities List (NPL) and
requests public comment on this
proposed action. The NPL constitutes
Appendix B of 40 CFR part 300 which
is the National 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 those 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
South Valley Superfund Site 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
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the NCP, a portion of a site deleted from
the NPL remains eligible for Fundfinanced remedial action if future
conditions warrant such actions.
EPA will accept comments on the
proposal to partially delete this site for
30 days after publication of this
document in the Federal Register.
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 Operable Units 1, 2, and 5
of the South Valley Superfund Site and
demonstrates how the operable units
meet the deletion criteria.
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. Deletion Procedures
The following procedures apply to
deletion of Operable Units 1, 2, and 5
of the Site:
(1) EPA consulted with the State of
New Mexico before developing this
Notice of Intent for Partial Deletion.
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(2) EPA has provided the State of New
Mexico 30 working days for review of
this notice prior to publication of it
today.
(3) In accordance with the criteria
discussed above, EPA has determined
that no further response is appropriate.
(4) The State of New Mexico, through
the New Mexico Environment
Department, has concurred with the
deletion of Operable Units 1, 2, and 5
of the South Valley Superfund Site,
from the NPL.
(5) Concurrently, with the publication
of this Notice of Intent for Partial
Deletion in the Federal Register, a
notice is being published in a major
local newspaper, the Albuquerque
Journal, https://www.abqjournal.com.
The newspaper announces the 30-day
public comment period concerning the
Notice of Intent for Partial Deletion of
the Site from the NPL.
(6) The EPA placed copies of
documents supporting the proposed
partial deletion in the deletion docket,
made these items available for public
inspection, and copying at the Site
information repositories identified
above.
If comments are received within the
30-day comment period on this
document, EPA will evaluate and
respond accordingly to the comments
before making a final decision to delete
Operable Units 1, 2, and 5. If necessary,
EPA will prepare a Responsiveness
Summary to address any significant
public comments received. After the
public comment period, if EPA
determines it is still appropriate to
delete Operable Units 1, 2, and 5 of the
South Valley Superfund Site, the
Regional Administrator will publish a
final Notice of Partial Deletion in the
Federal Register. Public notices, public
submissions and copies of the
Responsiveness Summary, if prepared,
will be made available to interested
parties and included in the site
information repositories listed above.
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 future response actions,
should future conditions warrant such
actions.
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IV. Basis for Partial Site Deletion
The following information provides
EPA’s rationale for deleting Operable
Units 1, 2, and 5 of the South Valley
Superfund Site from the NPL:
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Site Background and History
The EPA ID for the South Valley
Superfund Site is NMD980745558. The
South Valley Superfund Site is in the
southern portion of Albuquerque, in
Bernillo County, New Mexico, directly
across Interstate 25 from the
Albuquerque International Airport and
the University of New Mexico Golf
Course. The South Valley Superfund
Site consists of an area of approximately
one square mile proximate to the
intersection of South Broadway
Boulevard and Woodward Road and is
divided into two properties: the former
Air Force Plant 83 site and the Univar
site. The Air Force Plant 83 site is
further divided into two parcels located
north and south of Woodward Road
known as North Plant 83 and South
Plant 83, respectively. Various
manufacturing operations occurred at
the Air Force Plant 83 site from the
1940s until 1967, when the United
States Air Force took ownership of the
property and its contractor, General
Electric Aircraft Engines (GEA), began
manufacturing aircraft engine
components at the property. GEA
purchased the Air Force Plant 83 in
1983 and continued operations until
October 1997, when North Plant 83 was
closed, and until October 2010, when
South Plant 83 was closed. Groundwater
beneath the Site is in the Santa Fe
Group which is comprised of several
layers within the formation. The
shallow zone aquifer (approximately
175–225 below ground surface [bgs])
beneath the North Plant 83 area has a
continuous silty clay layer underneath it
and is therefore primarily perched and
does not have a uniform flow direction.
The shallow groundwater in the South
Plant 83 area flows east to west. Unlike
North Plant 83, the silty clay layer
beneath the South Plant 83 area is
discontinuous and therefore is in
hydraulic connection with the deeper
aquifer zones. The deeper aquifer sand
zones (approximately 225–355 bgs, 255–
415 bgs, and 415–515 bgs) have
discontinuous silts and clays
interbedded within them which are not
laterally extensive but may limit
downward movement through the
formation. Groundwater flows generally
east to west in all the deeper aquifer
zones.
Groundwater contamination was first
suspected in the late 1970s in two
municipal wells—San Jose No. 6 and
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San Jose No. 3. The wells were taken out
of service after subsequent sampling
indicated contamination. Groundwater
monitoring results in the vicinity of the
wells indicated the potential for a
number of sources, including several
industrial operations located in close
proximity to the contaminated wells.
When the Site was proposed to the NPL
on December 30, 1982, (47 FR 58476),
it was the number one priority of the
State of New Mexico. EPA finalized the
NPL listing on September 8, 1983, (48
FR 40658).
The Operable Units at the South
Valley Superfund Site are as follows:
Operable Unit 1 (OU1) (included in
partial deletion)—OU1 consists of the
City of Albuquerque San Jose 6 (SJ–6)
and San Jose 3 (SJ–3) wells, which were
contaminated with volatile organic
compounds (VOCs). EPA signed the
Record of Decision (ROD) for OU1 on
March 22, 1985 but did not identify a
Potentially Responsible Party (PRP). The
remedial goal was to eliminate the
threat to human health posed by
introducing water from the San Jose 6
and San Jose 3 wells into the City of
Albuquerque drinking water supply.
The objective was achieved by EPA
replacing wells SJ–6 and SJ–3 with the
Burton No. 4 well, which was
completed in April 1987.
Operable Unit 2 (OU2) (included in
partial deletion)—The remedial goals of
OU2 were to eliminate the conduit(s) for
contaminant migration from the shallow
to the deeper aquifers and to restrict
groundwater use under the Site. EPA
signed the OU2 ROD on September 30,
1988 and identified GEA as a PRP. GEA
implemented the remedial action by
plugging SJ–6 and SJ–3 and any shallow
wells that could act as conduits for
contaminant transport from the shallow
to the deeper aquifers, restricting
groundwater use, and implementing
groundwater monitoring. GEA
integrated the OU2 groundwater
monitoring program into Operable Unit
6 and continues the monitoring program
today.
Operable Unit 3 (OU3)—The remedial
goal of OU3 included reducing the
concentrations of site-related VOCs in
groundwater to acceptable levels
(aquifer restoration) via a pump-treatinjection system. EPA signed the ROD
on June 28, 1988 and identified Univar
as the Potentially Responsible Party.
Univar initiated groundwater recovery
system in April 1992 and a vapor
recovery system in November 1999.
Univar shut off both systems in
November 2006. Subsequent monitoring
has shown that the groundwater and
vapor recovery systems reduced the
dissolved chlorinated VOC
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concentrations to levels below and
compliant with applicable or relevant
and appropriate requirements as defined
in the ROD. On June 10, 2014, the EPA
acknowledged that Univar completed all
requirements of the Consent Decree
dated March 27, 1990, as they relate to
the constituents of concern in
groundwater identified in the ROD and
the subsequent Explanation of
Significant Differences dated September
26, 2006, except for addressing 1,4dioxane contamination. The EPA
acknowledged that Univar is addressing
1,4-dioxane in groundwater at OU3
pursuant to Section XVI(D) of the above
Consent Decree.
Operable Unit 4 (OU4)—OU4 consists
of the vadose zone at the Univar site. As
the PRP, Univar was required to
investigate the soil around a pit on its
property to establish the source of the
solvents under their plant. The
investigation found no evidence in the
vadose zone that a release occurred at
this location. EPA signed the ROD on
June 28, 1988 and specified No Further
Action.
Operable Unit 5 (OU5) (included in
partial deletion)—OU5 consists of the
unsaturated and saturated portion of the
shallow zone aquifer at North Plant 83
and South Plant 83. EPA signed the
ROD on September 30, 1988, and
identified GEA as the PRP. The remedial
goals for this operable unit were
remediating shallow zone groundwater
and eliminating source materials via
enhanced dewatering, soil flushing, and
soil vapor extraction (SVE) to result in
aquifer restoration. GEA conducted soil
vapor surveys and collected soil borings
in the South Plant 83 area and the North
Plant 83 area to identify VOC
contamination. The result of these
investigations indicated that the
concentrations of VOCs would best be
remediated using SVE. GEA operated
SVE systems at the North Plant 83 and
South Plant 83 areas in 1992 and 1993.
Prior to remediation, the groundwater
contamination encompassed
approximately twelve acres at North
Plant 83 and approximately seven acres
at South Plant 83. GEA initiated shallow
groundwater recovery systems at the
North Plant 83 and South Plant 83 areas
in May 1994 and completely shut down
the groundwater recovery systems in
July 2010. GEA completed compliance
groundwater monitoring and on
September 22, 2014 requested closure of
OU5 stating that GEA had satisfactorily
completed all requirements of the
Administrative Order dated July 3,
1989. All wells and infrastructure
associated with the OU5 groundwater
treatment system have been plugged and
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abandoned or removed as approved by
EPA.
After the closure of South Plant 83 in
October 2010, GEA performed
additional remedial activities associated
with OU5 soils. Specifically, GEA
performed investigations within the
North Plant 83 and South Plant 83
building footprints and excavated and
disposed of hexavalent chromium
contaminated soil from the East and
West Tank Line area in South Plant 83.
In addition, GEA filed a deed restriction
in the Bernalillo County records
covering areas where semi-volatile
organic compounds (i.e., polyaromatic
hydrocarbons) or hexavalent chromium
contamination remained above
industrial soil screening levels.
Operable Unit 6 (OU6)—OU6 consists
of the deep aquifer at North Plant 83
and South Plant 83. EPA signed the
ROD on September 30, 1988 and
identified GEA as the PRP. The remedial
goals of OU6 are hydraulically
containing the plume to protect the City
of Albuquerque’s water supply wells
and reducing the concentrations of siterelated VOC compounds in groundwater
to acceptable levels (aquifer restoration).
The original plume was approximately
100 acres in size but as of 2018, only
two wells have constituents above
cleanup levels. The groundwater
remediation system at OU6 began
operation in March 1996. Remedial
action activities have hydraulically
contained the plume and shrunk it
significantly from its former volume and
mass. To date, over 7.5 billion gallons
of contaminated water have been
recovered, treated, and reinjected back
into the deep aquifer.
The South Valley area of Albuquerque
has experienced ongoing development
and redevelopment for decades. The
proposed extension of Sunport
Boulevard from east of Interstate 25 to
west of Interstate 25, if constructed, is
expected to spur local economic growth
and redevelopment.
Remedial Investigation and Feasibility
Study
Operable Unit 1 (OU1)—Other than
the sampling that established that San
Jose No. 6 and San Jose No. 3 municipal
water supply wells had been impacted,
there was no remedial investigation
performed for OU1. Upon detection of
contamination, the City of Albuquerque
discontinued use of the water supply
wells. Subsequently, the EPA, the City
of Albuquerque, and other stakeholders
conducted several meetings to discuss
potential sites for a replacement
municipal well, which culminated in
the final design and ultimate
installation of a replacement municipal
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water supply well, Burton Well No. 4.
In addition, a remedial investigation
was initiated which provided
information utilized to develop
remedial activities for the remaining
operable units at the Site.
Operable Unit 2 (OU2)—GEA
conducted a remedial investigation for
OU2 because of the contamination
identified in OU1. As part of the
remedial investigation, GEA compiled
existing investigative information and
collected additional soil, groundwater,
surface water, and sediment information
associated with the one-square-mile
boundary area of the South Valley
Superfund Site. In addition, GEA
identified contamination associated
with several different sources. Based
upon the remedial investigation data,
GEA determined in the feasibility study
that contaminated groundwater in the
shallow zone was potentially migrating
into the intermediate zone throughout
the Site through improperly constructed
groundwater wells. The contaminants of
concern identified in the remedial
investigation were VOCs, with the main
contaminant being trichloroethylene
(TCE).
Operable Unit 5 (OU5)—GEA
conducted a remedial investigation for
OU5 because of the contamination
identified in OU1. As part of the
remedial investigation GEA, compiled
existing investigative information and
collected additional soil, groundwater,
surface water, and sediment information
associated with the one-square-mile
boundary area of the South Valley
Superfund Site. Further, GEA identified
contamination associated with several
different sources. The contaminants of
concern identified in the remedial
investigation were VOCs, with the main
contaminant being TCE.
Based upon the remedial investigation
data, GEA determined in the feasibility
study that OU5 soil contamination
occurs in areas associated with the two
areas, North Plant 83 and South Plant
83, and groundwater contamination
occurs in the shallow aquifer below
portions of both the North Plant 83 and
South Plant 83 areas. GEA also
identified groundwater contamination
comprising of similar constituents of
concerns as in OU5 in several other
hydrogeological units beneath the Site,
which are addressed in OU6.
After the closure of South Plant 83 in
October 2010, GEA performed
additional remedial activities associated
with OU5, including soil investigations
within the North Plant 83 and South
Plant 83 building footprints. GEA
identified 68 separate areas as a
potential concern with 41 of these
locations being identified for
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36841
investigation. In addition, GEA sampled
soil borings for VOCs, semi-volatile
organic compounds, polychlorinated
biphenyls, and selected metals. GEA did
not detect VOCs above industrial soil
screening levels and did not detect any
polychlorinated biphenyls. GEA
detected semi-volatile organic
compounds (i.e., polyaromatic
hydrocarbons) and hexavalent
chromium in a few of the 41 locations
investigated. In addition, GEA
inspected, investigated, and cleaned out
sanitary sewer lines for both North Plant
83 and South Plant 83. While GEA
detected concentrations of metal
contaminants in sediments within the
sewer lines, it did not identify impacts
in the soils adjacent and beneath the
sewer lines.
Selected Remedy
Operable Unit 1 (OU1)—EPA signed
the ROD for OU1 on March 22, 1985.
The selected remedy was installation of
a new water supply well to replace the
capacity of the contaminated well San
Jose No. 6. The remedial goal was to
eliminate the threat to human health
posed by introducing water from this
well into the City of Albuquerque
drinking water supply.
Operable Unit 2 (OU2)—EPA signed
the ROD for OU2 on September 30,
1988. The selected remedy consisted of
cleaning out and sealing abandoned
wells that were acting as conduits for
contaminant migration, groundwater
quality monitoring during and after
implementation of any remedial action,
and the imposition of access restrictions
regarding well construction
specifications and depth of completions
through the State Engineer’s office. The
remedial goals were eliminating
conduit(s) for contaminant migration
from the shallow to intermediate
aquifers and preventing the use of
contaminated groundwater in the site
area.
Operable Unit 5 (OU5)—EPA signed
the ROD for OU5 on September 30,
1988. The selected remedy consisted of
further investigation to define the extent
of soil and groundwater contamination,
soil remediation utilizing SVE on
portions of North Plant 83 and South
Plant 83, groundwater remediation
through extraction, treatment with air
stripping followed by carbon
adsorption, and reinjection into the
aquifer for shallow (OU5) groundwater
contaminated zones located under
portions of North Plant 83 and South
Plant 83 along with intermediate/deep
(OU6) groundwater contaminated zones
on-site and off-site. The remedial goals
for OU5 were remediating shallow zone
groundwater and eliminating source
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materials via enhanced dewatering, soil
flushing, and SVE. Further, as a result
of the investigations performed by GEA
after closure of South Plant 83 in
October 2010, GEA conducted removal
of soil proximate to the East and West
Tank Line area in South Plant 83 in
2011.
Response Actions
Operable Unit 1 (OU1)—The United
State Corps of Engineers completed a
final design for a new municipal water
supply well in late 1986. The remedial
action performed at OU1 was the
replacement of wells SJ–6 and SJ–3 with
the Burton No. 4 well, which was
completed in April 1987.
Operable Unit 2 (OU2)—GEA
completed a final design dated July 20,
1990, that contained plans to install
monitoring wells, clean out and plug
abandoned wells including the SJ–6
well (OU1), and conduct a groundwater
monitoring program. GEA completed
the installation of new monitoring wells
and the plugging and abandonment of
wells that could act as conduits for
contaminant transport to lower
groundwater zones by the end of 1992.
GEA initiated an OU2 groundwater
monitoring program, which in 1996 was
combined with the OU6 groundwater
monitoring program to simplify
groundwater monitoring and reporting
at the Site. The New Mexico State
Engineer’s office issued a restriction
concerning groundwater well
construction within the boundaries of
the South Valley Superfund Site on
December 19, 1988.
Operable Unit 5 (OU5)—Because the
remedial investigation identified both
soil and groundwater contamination,
the response actions for OU5 were
separated by media into soil and
groundwater actions. For soils, GEA
finalized the remedial design for the
SVE systems in late 1991, which EPA
subsequently approved on January 24,
1992. GEA installed and operated SVE
systems on both the North Plant 83 and
South Plant 83 areas. The North Plant
83 SVE system operated for
approximately four months from June
1992 to June 1993. The South Plant 83
SVE system operated for approximately
five months from October 1992 to March
1993. For groundwater, GEA’s
contractor, Canonie Environmental,
completed a final design dated July 21,
1993, that contained construction
details for the remedial systems for the
shallow zone groundwater remediation
on the North Plant 83 and South Plant
83 areas. The North Plant 83 system
initially was comprised of seven
extraction wells, and the South Plant 83
system was comprised of three wells.
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These systems were augmented through
their operational lifetime to adapt to
changes in groundwater concentrations
and flow patterns.
After the closure of South Plant 83 in
October 2010, GEA performed
additional remedial activities associated
with OU5. GEA conducted removal of
soil proximate to the East and West
Tank Line area in South Plant 83 in
2011. Approximately 3.5 tons of
contaminated soil and concrete were
removed and transported for final
disposal at an off-site hazardous waste
disposal facility. Following removal,
GEA backfilled the area with clean fill
and capped the area with a five-inchthick, 3,000 pounds/square inch layer of
reinforced concrete. GEA filed a deed
restriction in the Bernalillo County
records covering areas where semivolatile organic compounds (i.e.,
polyaromatic hydrocarbons) or
hexavalent chromium contamination
remained present above industrial soil
screening levels. GEA removed
approximately 1,750 feet of primary 4inch to 8-inch diameter cast iron
process sewer lines, 435 feet of similar
smaller branch lines, and seven
manholes and disposed these materials
at a Resource Conservation and
Recovery Act treatment, storage, and
disposal facility. Finally, GEA cleaned
and abandoned in place the South Plant
83 sewer system piping and plugged the
connection to the City of Albuquerque
sewer system.
Cleanup Levels
Operable Unit 1 (OU1)—There were
no cleanup levels established for OU1,
as the remedy was simply replacement
of a municipal water supply well to
replace the capacity lost by the
contaminated SJ–6 well.
Operable Unit 2 (OU2)—There were
no cleanup levels established for OU2,
as the remedy was simply the
installation of additional groundwater
monitoring wells, the plugging and
abandonment of wells that could act as
conduits for contaminant transport to
lower groundwater zones, the
imposition of access restrictions
regarding well construction
specifications and depth of completions
through the State Engineer’s office, and
the establishment of a groundwater
monitoring program to obtain data
concerning groundwater contamination.
Operable Unit 5 (OU5)—The
investigations and remediation work for
OU5 was separated by media into soil
and groundwater work. For soil, the
ROD required the utilization of SVE for
soil remediation but did not specify
cleanup levels. The ROD stated, ‘‘Soils
treatment will continue until the vapor
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extraction system ceases to produce
volatile contaminants and will be
followed by sampling to confirm soil
remediation.’’ GEA obtained post
remediation soil samples after the SVE
systems ceased operations and proposed
cleanup levels for soils in April 1993.
The proposed cleanup levels considered
soil exposure pathways including
dermal contact, inhalation, and
ingestion (i.e., by children ages 2 to 6)
as well as the potential for contaminants
to leach from soil into groundwater that
would exceed drinking water standards.
GEA based the cleanup levels on the
assumption of an operating
manufacturing facility with restricted
access but also on the worst-case
exposure scenario that the site could be
converted to residential use. During a
meeting with GEA on November 2,
1993, EPA verbally agreed to the
proposed cleanup levels. In a letter
dated June 21, 1994, EPA indicated that
the levels of contaminants found in the
soils were below limits that required
removal. In addition, out of an
abundance of caution, as part of the
2017 Remedial Action Report for OU5,
GEA performed a comparison of the
post remediation soil concentrations to
the EPA Industrial and Residential Soil
Screening Levels (November 2015)
which indicated all the post soil
remediation soil concentrations were
below the EPA Industrial and
Residential Soil Screening Levels. For
groundwater, the ROD specified that
cleanup levels would be maximum
contaminant limits from the Safe
Drinking Water Act and levels in the
New Mexico Water Quality Control
Commission regulations, whichever was
more stringent. These levels were
updated in an Explanation of Significant
Differences dated October 16, 2006,
which added a level for
tetrachloroethylene promulgated under
the Safe Drinking Water Act in 1992.
GEA implemented and conducted a
groundwater monitoring program
throughout the operation of the shallow
zone groundwater remediation systems.
After six years of monitoring indicating
that none of the off-site wells of the
North Plant 83 system well network
exceeded cleanup levels, EPA approved
closure of the off-site wells and
conveyance system. GEA flushed,
cleaned, and abandoned conveyance
piping in place and plugged and
abandoned wells in 2010. One on-site
well associated with the North Plant 83
system remained slightly above cleanup
levels. In 2010, GEA performed in-situ
chemical oxidation around this well
which subsequent sampling confirmed
that contaminant concentrations fell and
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remained below cleanup levels. The
South Plant 83 system experienced a
similar history to the North Plant 83
system. By 1999, all wells associated
with the South Plant 83 system except
for two wells were below cleanup
levels. By 2006, only one well had
concentrations above cleanup levels.
Like the North Plant 83 system, GEA
performed in-situ chemical oxidation in
2010 around this well, which
subsequent sampling confirmed that
contaminant concentrations fell below
cleanup levels shortly after the in-situ
treatment and remained below cleanup
levels through 2012.
After the closure of South Plant 83 in
October 2010, GEA performed
additional remedial activities associated
with OU5. Utilizing investigations
results, GEA completed an assessment
of the risk for the contaminants
identified in the investigation. This
assessment indicated that hexavalent
chromium contamination in deep soils
would not pose a risk to human health
and the environment assuming that an
impermeable cover remained in place
and institutional controls were
implemented. The assessment also
indicated that the semi-volatile organic
compounds (i.e., polyaromatic
hydrocarbons) identified in soils would
not pose a risk to human health and the
environment if the existing concrete cap
was left in place. GEA removed soil
with concentrations of hexavalent
chromium above 50 milligrams per
kilogram (mg/kg) but did not remove
soil with hexavalent chromium
contamination ranging from 5.6 to 50
mg/kg at depths between 5 to 14 feet
below the existing concrete slab. GEA
filed a deed restriction in the Bernalillo
County records covering areas where
semi-volatile organic compounds or
hexavalent chromium contamination
remained above industrial soil screening
levels.
Operation and Maintenance
Operable Unit 1 (OU1)—The
operation and maintenance concerning
the Burton No. 4 replacement well is
performed by the City of Albuquerque.
Operable Unit 2 (OU2)—There is no
operation and maintenance associated
with OU2. The restriction concerning
groundwater well construction within
the boundaries of the South Valley
Superfund Site issued by the New
Mexico State Engineer’s office on
December 19, 1988, remains in effect
but is now monitored under OU6. This
restriction is not needed and does not
affect the protectiveness of the actions
performed at OU2.
Operable Unit 5 (OU5)—Since the soil
and groundwater remediation systems
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associated with OU5 have met their
associated cleanup levels and have been
dismantled, there are no operation and
maintenance activities required or
ongoing for the OU5 SVE and
groundwater remediation systems. In
addition, while still in effect, the New
Mexico State Engineer’s restriction
concerning groundwater well
construction is no longer required for
the protectiveness of the OU5 remedy
because groundwater concentrations are
below the maximum contaminant limits
from the Safe Drinking Water Act and
levels in the New Mexico Water Quality
Control Commission regulations. After
ceasing operations in September 2010
and completing demolition of the South
Plant 83 buildings in May 2011, GEA
performed investigations of the South
Plant 83 property which included
evaluating soil impacts near any
existing sub-grade foundation features
as well as the North Plant 83 and South
Plant 83 sewer systems. In addition,
GEA cleaned out and abandoned in
place the sewer systems. Because of the
soil investigation, GEA removed
hexavalent chromium contamination
near the location of the East and West
Tank Line on the South Plant 83
property. Some contamination remained
in place and, as a result, GEA filed a
declaration of restrictive covenants on
September 9, 2014 in the Bernalillo
County property records. The
declaration identified five areas where
semi-volatile organic compounds or
hexavalent chromium contamination
exceed industrial soil screening levels.
The declaration also contained the
following: Identification of the
abandoned sanitary sewer lines and
existing sewer line locations; restriction
that the property use is limited to
commercial and industrial; restriction
that groundwater beneath the site
cannot be used; and engineered barriers
must remain in place on portions of the
property where semi-volatile organic
compounds and hexavalent chromium
remain above industrial soil screening
levels. GEA performs normal property
maintenance inspections of the North
Plant 83 and South Plant 83 to identify
fencing integrity issues and to maintain
weed control. These inspections also
observe the integrity of the concrete cap
over the East and West Tank Line
removal area to ensure it is competent.
GEA also ensures that the deed
restriction remains in the Bernalillo
County records.
Five Year Review
Operable Unit 1 (OU1)—A five-year
review is not necessary for OU1 because
no hazardous substances, pollutants, or
contaminants remain at the site above
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36843
levels that allow for unlimited use and
unrestricted exposure.
Operable Unit 2 (OU2)—A five-year
review is not necessary for OU2 because
no hazardous substances, pollutants, or
contaminants remain at the site above
levels that allow for unlimited use and
unrestricted exposure. While still in
effect, the New Mexico State Engineer’s
restriction concerning groundwater well
construction is no longer required for
the protectiveness of the OU5 remedy
because groundwater concentrations are
below the maximum contaminant limits
from the Safe Drinking Water Act and
levels in the New Mexico Water Quality
Control Commission regulations. In
1996, the OU2 groundwater monitoring
program was combined with the OU6
groundwater monitoring program,
which is and has been the subject of
ongoing five-year reviews associated
with the Site. The next five-year review
for the Site is due in July 2020.
Operable Unit 5 (OU5)—A statutory
five-year review is necessary for OU5
because hazardous substances,
pollutants, or contaminants remain at
the site above levels that allow for
unlimited use and unrestricted
exposure. OU5 has been the subject of
ongoing five-year reviews with the next
review due in July 2020. No issues and/
or recommendations were identified in
the 2015 five-year review for OU5.
Community Involvement
The major community involvement
activities associated with the operable
units proposed for deletion are as
follows:
• Open Houses and Workshops:
September 1988; November 1993; July
1995; October 1997; September 1998;
November 1999, October 2000;
November 2001; January 2013.
• Original Proposed Plan Fact Sheet
and Public Meetings: June 1988; July
1988; August 1988; February 1989.
• Public Meetings: October 2000;
November 2001.
• Original ROD Fact Sheets: July
1988; November 1988; April 1989.
• Milestone Fact Sheets: May 1989;
March 1990; April 1990; June 1990;
March 1991; November 1993; June 1995;
April 1996; December 2011; January
2013; June 2015; July 2015; June 2018.
• Citizens on Site Mailing List: 590.
Other notable community
involvement activities are:
• Pre Five-Year Review public notices
published in local newspapers
indicating Five-Year Reviews were
being initiated.
• Post Five-Year Review public
notices published in local newspapers
indicating Five-Year Reviews were
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completed and available in the local
repository or from the State or EPA.
• Monthly site status summaries that
were made available to the public or
more recently, updates to site activities
made on the site web page available on
the internet.
• September 23, 2010, newspaper
article in the Albuquerque Journal
concerning the closure of the General
Electric plant.
• Discussion of the site at public
meetings associated with the Sunport
Boulevard Extension from
approximately 2010 to the present.
• Fact sheets and public notices have
been provided in both English and
Spanish.
Authority: 33 U.S.C. 1321(d); 42 U.S.C.
9601–9657; E.O. 13626, 77 FR 56749, 3 CFR,
2013 Comp., p. 306; E.O. 12777, 56 FR 54757,
3 CFR, 1991 Comp., p. 351; E.O. 12580, 52
FR 2923, 3 CFR, 1987 Comp., p. 193.
Determination That the Criteria for
Deletion Have Been Met
National Oil and Hazardous
Substances Pollution Contingency
Plan; National Priorities List: Deletion
of the Reasor Chemical Company
Superfund Site
daltland on DSKBBV9HB2PROD with PROPOSALS
The implemented remedies have
achieved the degree of cleanup or
protection specified in the OU1, OU2,
and OU5 RODs for the portions of the
Site proposed for deletion. The selected
remedial action goals and associated
cleanup levels for the OU1, OU2, and
OU5 portions of the Site proposed for
deletion are consistent with EPA policy
and guidance. No further Superfund
response for the OU1, OU2, and OU5
portions of the Site proposed for
deletion are needed to protect human
health and the environment. The State
of New Mexico, in an August 11, 2017,
letter from the New Mexico
Environment Department, concurred
with the proposed partial deletion of the
OU1, OU2, and OU5 portions of the Site
from the NPL.
The NCP specifies that EPA may
delete a site from the NPL if all
appropriate response under CERCLA
has been implemented and no further
response action is appropriate. 40 CFR
300.425(e)(1)(ii). EPA, with the
concurrence of the State of New Mexico,
through NMED, believes that this
criterion for the deletion of the OU1,
OU2, and OU5 portions of the Site has
been met and the OU1, OU2, and OU5
portions of the Site no longer pose a
threat to public health or the
environment. Consequently, EPA is
proposing to delete the OU1, OU2, and
OU5 portions of the Site from the NPL.
Documents supporting this action are
available in the Docket.
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.
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Dated: July 19, 2018.
Arturo Blanco,
Acting Regional Administrator, Region 6.
[FR Doc. 2018–16257 Filed 7–30–18; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 300
[EPA–HQ–SFUND–2002–0001; FRL–9981–
51—Region 4]
Environmental Protection
Agency (EPA).
ACTION: Proposed rule; notice of intent.
AGENCY:
The Environmental Protection
Agency (EPA) Region 4 is issuing a
Notice of Intent to Delete the Reasor
Chemical Company Superfund Site
(site) located in Castle Hayne, New
Hanover County, North Carolina, from
the National Priorities List (NPL) and
requests public comments on this
proposed action. 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). The EPA and
the State of North Carolina, through the
North Carolina Department of
Environmental Quality (NCDEQ), have
determined that all appropriate
response actions under CERCLA have
been completed. However, this deletion
does not preclude future actions under
Superfund.
DATES: Comments must be received by
August 30, 2018.
ADDRESSES: Submit your comments,
identified by Docket ID no. EPA–HQ–
SFUND–2002–0001, by one of the
following methods:
• https://www.regulations.gov. Follow
the online instructions for submitting
comments. Once submitted, comments
cannot be edited or removed from
Regulations.gov. The EPA may publish
any comment received to its public
docket. Do not submit electronically any
information you consider to be
Confidential Business Information (CBI)
or other information whose disclosure is
SUMMARY:
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restricted by statute. Multimedia
submissions (audio, video, etc.) must be
accompanied by a written comment.
The written comment is considered the
official comment and should include
discussion of all points you wish to
make. The EPA will generally not
consider comments or comment
contents located outside of the primary
submission (i.e. on the web, cloud, or
other file sharing system). For
additional submission methods, the full
EPA public comment policy,
information about CBI or multimedia
submissions, and general guidance on
making effective comments, please visit
https://www2.epa.gov/dockets/
commenting-epa-dockets.
• Email: URQUHARTFOSTER.SAMANTHA@EPA.GOV.
• Mail: Samantha Urquhart-Foster,
Remedial Project Manager, Remediation
and Site Evaluation Branch, Superfund
Division, U.S. Environmental Protection
Agency, Region 4, 61 Forsyth Street SW,
Atlanta, Georgia 30303–8960.
• Hand delivery: U.S. Environmental
Protection Agency, Region 4, 61 Forsyth
Street SW, Atlanta, Georgia 30303–8960.
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–2002–
0001. The https://www.regulations.gov
website 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
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 statute. Certain other
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Agencies
[Federal Register Volume 83, Number 147 (Tuesday, July 31, 2018)]
[Proposed Rules]
[Pages 36838-36844]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2018-16257]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 300
[EPA-HQ-SFUND-1983-0002; FRL-9981-39--Region 6]
National Oil and Hazardous Substances Pollution Contingency Plan;
National Priorities List: Partial Deletion of the South Valley
Superfund Site
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule; notice of intent.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) Region 6 is issuing
a Notice of Intent to Delete Operable Units 1, 2, and 5 of the South
Valley Superfund Site (Site) located in Albuquerque, New Mexico, from
the National Priorities List (NPL) and requests public comments on this
proposed action. 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). The EPA and the
State of New Mexico, through the New Mexico Environment Department,
have determined that all appropriate response actions at these
identified parcels under CERCLA have been completed, other than five-
year reviews and operation and maintenance activities. However, this
deletion does not preclude future actions under Superfund. This partial
deletion pertains to Operable Units 1, 2, and 5. The remaining Operable
Units 3, 4, and 6 will remain on the NPL and are not being considered
for deletion as part of this action.
DATES: Comments must be received by August 30, 2018.
ADDRESSES: Submit your comments, identified by Docket ID no. EPA-HQ-
SFUND-1983-0002, by one of the following methods:
https://www.regulations.gov . Follow the online
instructions for submitting comments. Once submitted, comments cannot
be edited or removed from Regulations.gov. The EPA may publish any
comment received to its public docket. Do not submit electronically any
information you consider to be Confidential Business Information (CBI)
or other information whose disclosure is restricted by statute.
Multimedia submissions (audio, video, etc.) must be accompanied by a
written comment. The written comment is considered the official comment
and should include discussion of all points you wish to make. The EPA
will generally not consider comments or comment contents located
outside of the primary submission (i.e. on the web, cloud, or other
file sharing system). For additional submission methods, the full EPA
public comment policy, information about CBI or multimedia submissions,
and general guidance on making effective comments, please visit https://www2.epa.gov/dockets/commenting-epa-dockets.
Email: [email protected].
Mail: Michael A. Hebert, Remedial Project Manager, EPA
Region 6, Mail Code--6SF-RL, 1445 Ross Avenue, Dallas, Texas 75202-
2733.
Hand delivery:
[cir] Michael A. Hebert, Remedial Project Manager, EPA Region 6, Mail
Code--6SF-RL, 7th Floor Reception Area, 1445 Ross Avenue, Dallas, Texas
75202-2733.
[cir] Such deliveries are only accepted during the Docket's normal
hours of operation (Monday through Friday, 7 a.m. to 4 p.m.) and
special arrangements should be made for deliveries of boxed
information.
Instructions: Direct your comments to Docket ID no. EPA-HQ-SFUND-
1983-0002. The https://www.regulations.gov website 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 encryption, and be free of any defects or
viruses.
[[Page 36839]]
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 statute. Certain other material, such
as copyrighted material, will be publicly available only in the hard
copy. Publicly available docket materials are available either
electronically in https://www.regulations.gov or in hard copy at:
Zimmerman Library, Government Information Department, University of New
Mexico, Albuquerque NM 87131, 505.277.9100, Monday-Thursday--7 a.m.-2
a.m., Friday--7 a.m.-9 p.m., Saturday--10 a.m.-6 p.m., Sunday--12 p.m.-
2 a.m.
New Mexico Environment Department, Harold Runnels Building, 1190 St.
Francis Drive, Santa Fe, NM 87505, 505.827.2855, Monday-Friday--8 a.m.-
5 p.m.
FOR FURTHER INFORMATION CONTACT: Michael A. Hebert, Remedial Project
Manager, U.S. Environmental Protection Agency, Region 6, Mail Code--
6SF-RL, 1445 Ross Avenue, Dallas, Texas, 75202-2733, (214) 665-8315,
email: [email protected].
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Introduction
II. NPL Deletion Criteria
III. Deletion Procedures
IV. Basis for Intended Partial Site Deletion
I. Introduction
EPA Region 6 announces its intent to delete Operable Units 1, 2,
and 5 of the South Valley Superfund Site (Site), from the National
Priorities List (NPL) and requests public comment on this proposed
action. The NPL constitutes Appendix B of 40 CFR part 300 which is the
National 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 those 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 South Valley Superfund Site 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 Sec. 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.
EPA will accept comments on the proposal to partially delete this
site for 30 days after publication of this document in the Federal
Register.
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 Operable Units 1, 2, and 5 of the
South Valley Superfund Site and demonstrates how the operable units
meet the deletion criteria.
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. Deletion Procedures
The following procedures apply to deletion of Operable Units 1, 2,
and 5 of the Site:
(1) EPA consulted with the State of New Mexico before developing
this Notice of Intent for Partial Deletion.
(2) EPA has provided the State of New Mexico 30 working days for
review of this notice prior to publication of it today.
(3) In accordance with the criteria discussed above, EPA has
determined that no further response is appropriate.
(4) The State of New Mexico, through the New Mexico Environment
Department, has concurred with the deletion of Operable Units 1, 2, and
5 of the South Valley Superfund Site, from the NPL.
(5) Concurrently, with the publication of this Notice of Intent for
Partial Deletion in the Federal Register, a notice is being published
in a major local newspaper, the Albuquerque Journal, https://www.abqjournal.com. The newspaper announces the 30-day public comment
period concerning the Notice of Intent for Partial Deletion of the Site
from the NPL.
(6) The EPA placed copies of documents supporting the proposed
partial deletion in the deletion docket, made these items available for
public inspection, and copying at the Site information repositories
identified above.
If comments are received within the 30-day comment period on this
document, EPA will evaluate and respond accordingly to the comments
before making a final decision to delete Operable Units 1, 2, and 5. If
necessary, EPA will prepare a Responsiveness Summary to address any
significant public comments received. After the public comment period,
if EPA determines it is still appropriate to delete Operable Units 1,
2, and 5 of the South Valley Superfund Site, the Regional Administrator
will publish a final Notice of Partial Deletion in the Federal
Register. Public notices, public submissions and copies of the
Responsiveness Summary, if prepared, will be made available to
interested parties and included in the site information repositories
listed above.
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 future
response actions, should future conditions warrant such actions.
[[Page 36840]]
IV. Basis for Partial Site Deletion
The following information provides EPA's rationale for deleting
Operable Units 1, 2, and 5 of the South Valley Superfund Site from the
NPL:
Site Background and History
The EPA ID for the South Valley Superfund Site is NMD980745558. The
South Valley Superfund Site is in the southern portion of Albuquerque,
in Bernillo County, New Mexico, directly across Interstate 25 from the
Albuquerque International Airport and the University of New Mexico Golf
Course. The South Valley Superfund Site consists of an area of
approximately one square mile proximate to the intersection of South
Broadway Boulevard and Woodward Road and is divided into two
properties: the former Air Force Plant 83 site and the Univar site. The
Air Force Plant 83 site is further divided into two parcels located
north and south of Woodward Road known as North Plant 83 and South
Plant 83, respectively. Various manufacturing operations occurred at
the Air Force Plant 83 site from the 1940s until 1967, when the United
States Air Force took ownership of the property and its contractor,
General Electric Aircraft Engines (GEA), began manufacturing aircraft
engine components at the property. GEA purchased the Air Force Plant 83
in 1983 and continued operations until October 1997, when North Plant
83 was closed, and until October 2010, when South Plant 83 was closed.
Groundwater beneath the Site is in the Santa Fe Group which is
comprised of several layers within the formation. The shallow zone
aquifer (approximately 175-225 below ground surface [bgs]) beneath the
North Plant 83 area has a continuous silty clay layer underneath it and
is therefore primarily perched and does not have a uniform flow
direction. The shallow groundwater in the South Plant 83 area flows
east to west. Unlike North Plant 83, the silty clay layer beneath the
South Plant 83 area is discontinuous and therefore is in hydraulic
connection with the deeper aquifer zones. The deeper aquifer sand zones
(approximately 225-355 bgs, 255-415 bgs, and 415-515 bgs) have
discontinuous silts and clays interbedded within them which are not
laterally extensive but may limit downward movement through the
formation. Groundwater flows generally east to west in all the deeper
aquifer zones.
Groundwater contamination was first suspected in the late 1970s in
two municipal wells--San Jose No. 6 and San Jose No. 3. The wells were
taken out of service after subsequent sampling indicated contamination.
Groundwater monitoring results in the vicinity of the wells indicated
the potential for a number of sources, including several industrial
operations located in close proximity to the contaminated wells. When
the Site was proposed to the NPL on December 30, 1982, (47 FR 58476),
it was the number one priority of the State of New Mexico. EPA
finalized the NPL listing on September 8, 1983, (48 FR 40658).
The Operable Units at the South Valley Superfund Site are as
follows:
Operable Unit 1 (OU1) (included in partial deletion)--OU1 consists
of the City of Albuquerque San Jose 6 (SJ-6) and San Jose 3 (SJ-3)
wells, which were contaminated with volatile organic compounds (VOCs).
EPA signed the Record of Decision (ROD) for OU1 on March 22, 1985 but
did not identify a Potentially Responsible Party (PRP). The remedial
goal was to eliminate the threat to human health posed by introducing
water from the San Jose 6 and San Jose 3 wells into the City of
Albuquerque drinking water supply. The objective was achieved by EPA
replacing wells SJ-6 and SJ-3 with the Burton No. 4 well, which was
completed in April 1987.
Operable Unit 2 (OU2) (included in partial deletion)--The remedial
goals of OU2 were to eliminate the conduit(s) for contaminant migration
from the shallow to the deeper aquifers and to restrict groundwater use
under the Site. EPA signed the OU2 ROD on September 30, 1988 and
identified GEA as a PRP. GEA implemented the remedial action by
plugging SJ-6 and SJ-3 and any shallow wells that could act as conduits
for contaminant transport from the shallow to the deeper aquifers,
restricting groundwater use, and implementing groundwater monitoring.
GEA integrated the OU2 groundwater monitoring program into Operable
Unit 6 and continues the monitoring program today.
Operable Unit 3 (OU3)--The remedial goal of OU3 included reducing
the concentrations of site-related VOCs in groundwater to acceptable
levels (aquifer restoration) via a pump-treat-injection system. EPA
signed the ROD on June 28, 1988 and identified Univar as the
Potentially Responsible Party. Univar initiated groundwater recovery
system in April 1992 and a vapor recovery system in November 1999.
Univar shut off both systems in November 2006. Subsequent monitoring
has shown that the groundwater and vapor recovery systems reduced the
dissolved chlorinated VOC concentrations to levels below and compliant
with applicable or relevant and appropriate requirements as defined in
the ROD. On June 10, 2014, the EPA acknowledged that Univar completed
all requirements of the Consent Decree dated March 27, 1990, as they
relate to the constituents of concern in groundwater identified in the
ROD and the subsequent Explanation of Significant Differences dated
September 26, 2006, except for addressing 1,4-dioxane contamination.
The EPA acknowledged that Univar is addressing 1,4-dioxane in
groundwater at OU3 pursuant to Section XVI(D) of the above Consent
Decree.
Operable Unit 4 (OU4)--OU4 consists of the vadose zone at the
Univar site. As the PRP, Univar was required to investigate the soil
around a pit on its property to establish the source of the solvents
under their plant. The investigation found no evidence in the vadose
zone that a release occurred at this location. EPA signed the ROD on
June 28, 1988 and specified No Further Action.
Operable Unit 5 (OU5) (included in partial deletion)--OU5 consists
of the unsaturated and saturated portion of the shallow zone aquifer at
North Plant 83 and South Plant 83. EPA signed the ROD on September 30,
1988, and identified GEA as the PRP. The remedial goals for this
operable unit were remediating shallow zone groundwater and eliminating
source materials via enhanced dewatering, soil flushing, and soil vapor
extraction (SVE) to result in aquifer restoration. GEA conducted soil
vapor surveys and collected soil borings in the South Plant 83 area and
the North Plant 83 area to identify VOC contamination. The result of
these investigations indicated that the concentrations of VOCs would
best be remediated using SVE. GEA operated SVE systems at the North
Plant 83 and South Plant 83 areas in 1992 and 1993. Prior to
remediation, the groundwater contamination encompassed approximately
twelve acres at North Plant 83 and approximately seven acres at South
Plant 83. GEA initiated shallow groundwater recovery systems at the
North Plant 83 and South Plant 83 areas in May 1994 and completely shut
down the groundwater recovery systems in July 2010. GEA completed
compliance groundwater monitoring and on September 22, 2014 requested
closure of OU5 stating that GEA had satisfactorily completed all
requirements of the Administrative Order dated July 3, 1989. All wells
and infrastructure associated with the OU5 groundwater treatment system
have been plugged and
[[Page 36841]]
abandoned or removed as approved by EPA.
After the closure of South Plant 83 in October 2010, GEA performed
additional remedial activities associated with OU5 soils. Specifically,
GEA performed investigations within the North Plant 83 and South Plant
83 building footprints and excavated and disposed of hexavalent
chromium contaminated soil from the East and West Tank Line area in
South Plant 83. In addition, GEA filed a deed restriction in the
Bernalillo County records covering areas where semi-volatile organic
compounds (i.e., polyaromatic hydrocarbons) or hexavalent chromium
contamination remained above industrial soil screening levels.
Operable Unit 6 (OU6)--OU6 consists of the deep aquifer at North
Plant 83 and South Plant 83. EPA signed the ROD on September 30, 1988
and identified GEA as the PRP. The remedial goals of OU6 are
hydraulically containing the plume to protect the City of Albuquerque's
water supply wells and reducing the concentrations of site-related VOC
compounds in groundwater to acceptable levels (aquifer restoration).
The original plume was approximately 100 acres in size but as of 2018,
only two wells have constituents above cleanup levels. The groundwater
remediation system at OU6 began operation in March 1996. Remedial
action activities have hydraulically contained the plume and shrunk it
significantly from its former volume and mass. To date, over 7.5
billion gallons of contaminated water have been recovered, treated, and
reinjected back into the deep aquifer.
The South Valley area of Albuquerque has experienced ongoing
development and redevelopment for decades. The proposed extension of
Sunport Boulevard from east of Interstate 25 to west of Interstate 25,
if constructed, is expected to spur local economic growth and
redevelopment.
Remedial Investigation and Feasibility Study
Operable Unit 1 (OU1)--Other than the sampling that established
that San Jose No. 6 and San Jose No. 3 municipal water supply wells had
been impacted, there was no remedial investigation performed for OU1.
Upon detection of contamination, the City of Albuquerque discontinued
use of the water supply wells. Subsequently, the EPA, the City of
Albuquerque, and other stakeholders conducted several meetings to
discuss potential sites for a replacement municipal well, which
culminated in the final design and ultimate installation of a
replacement municipal water supply well, Burton Well No. 4. In
addition, a remedial investigation was initiated which provided
information utilized to develop remedial activities for the remaining
operable units at the Site.
Operable Unit 2 (OU2)--GEA conducted a remedial investigation for
OU2 because of the contamination identified in OU1. As part of the
remedial investigation, GEA compiled existing investigative information
and collected additional soil, groundwater, surface water, and sediment
information associated with the one-square-mile boundary area of the
South Valley Superfund Site. In addition, GEA identified contamination
associated with several different sources. Based upon the remedial
investigation data, GEA determined in the feasibility study that
contaminated groundwater in the shallow zone was potentially migrating
into the intermediate zone throughout the Site through improperly
constructed groundwater wells. The contaminants of concern identified
in the remedial investigation were VOCs, with the main contaminant
being trichloroethylene (TCE).
Operable Unit 5 (OU5)--GEA conducted a remedial investigation for
OU5 because of the contamination identified in OU1. As part of the
remedial investigation GEA, compiled existing investigative information
and collected additional soil, groundwater, surface water, and sediment
information associated with the one-square-mile boundary area of the
South Valley Superfund Site. Further, GEA identified contamination
associated with several different sources. The contaminants of concern
identified in the remedial investigation were VOCs, with the main
contaminant being TCE.
Based upon the remedial investigation data, GEA determined in the
feasibility study that OU5 soil contamination occurs in areas
associated with the two areas, North Plant 83 and South Plant 83, and
groundwater contamination occurs in the shallow aquifer below portions
of both the North Plant 83 and South Plant 83 areas. GEA also
identified groundwater contamination comprising of similar constituents
of concerns as in OU5 in several other hydrogeological units beneath
the Site, which are addressed in OU6.
After the closure of South Plant 83 in October 2010, GEA performed
additional remedial activities associated with OU5, including soil
investigations within the North Plant 83 and South Plant 83 building
footprints. GEA identified 68 separate areas as a potential concern
with 41 of these locations being identified for investigation. In
addition, GEA sampled soil borings for VOCs, semi-volatile organic
compounds, polychlorinated biphenyls, and selected metals. GEA did not
detect VOCs above industrial soil screening levels and did not detect
any polychlorinated biphenyls. GEA detected semi-volatile organic
compounds (i.e., polyaromatic hydrocarbons) and hexavalent chromium in
a few of the 41 locations investigated. In addition, GEA inspected,
investigated, and cleaned out sanitary sewer lines for both North Plant
83 and South Plant 83. While GEA detected concentrations of metal
contaminants in sediments within the sewer lines, it did not identify
impacts in the soils adjacent and beneath the sewer lines.
Selected Remedy
Operable Unit 1 (OU1)--EPA signed the ROD for OU1 on March 22,
1985. The selected remedy was installation of a new water supply well
to replace the capacity of the contaminated well San Jose No. 6. The
remedial goal was to eliminate the threat to human health posed by
introducing water from this well into the City of Albuquerque drinking
water supply.
Operable Unit 2 (OU2)--EPA signed the ROD for OU2 on September 30,
1988. The selected remedy consisted of cleaning out and sealing
abandoned wells that were acting as conduits for contaminant migration,
groundwater quality monitoring during and after implementation of any
remedial action, and the imposition of access restrictions regarding
well construction specifications and depth of completions through the
State Engineer's office. The remedial goals were eliminating conduit(s)
for contaminant migration from the shallow to intermediate aquifers and
preventing the use of contaminated groundwater in the site area.
Operable Unit 5 (OU5)--EPA signed the ROD for OU5 on September 30,
1988. The selected remedy consisted of further investigation to define
the extent of soil and groundwater contamination, soil remediation
utilizing SVE on portions of North Plant 83 and South Plant 83,
groundwater remediation through extraction, treatment with air
stripping followed by carbon adsorption, and reinjection into the
aquifer for shallow (OU5) groundwater contaminated zones located under
portions of North Plant 83 and South Plant 83 along with intermediate/
deep (OU6) groundwater contaminated zones on-site and off-site. The
remedial goals for OU5 were remediating shallow zone groundwater and
eliminating source
[[Page 36842]]
materials via enhanced dewatering, soil flushing, and SVE. Further, as
a result of the investigations performed by GEA after closure of South
Plant 83 in October 2010, GEA conducted removal of soil proximate to
the East and West Tank Line area in South Plant 83 in 2011.
Response Actions
Operable Unit 1 (OU1)--The United State Corps of Engineers
completed a final design for a new municipal water supply well in late
1986. The remedial action performed at OU1 was the replacement of wells
SJ-6 and SJ-3 with the Burton No. 4 well, which was completed in April
1987.
Operable Unit 2 (OU2)--GEA completed a final design dated July 20,
1990, that contained plans to install monitoring wells, clean out and
plug abandoned wells including the SJ-6 well (OU1), and conduct a
groundwater monitoring program. GEA completed the installation of new
monitoring wells and the plugging and abandonment of wells that could
act as conduits for contaminant transport to lower groundwater zones by
the end of 1992. GEA initiated an OU2 groundwater monitoring program,
which in 1996 was combined with the OU6 groundwater monitoring program
to simplify groundwater monitoring and reporting at the Site. The New
Mexico State Engineer's office issued a restriction concerning
groundwater well construction within the boundaries of the South Valley
Superfund Site on December 19, 1988.
Operable Unit 5 (OU5)--Because the remedial investigation
identified both soil and groundwater contamination, the response
actions for OU5 were separated by media into soil and groundwater
actions. For soils, GEA finalized the remedial design for the SVE
systems in late 1991, which EPA subsequently approved on January 24,
1992. GEA installed and operated SVE systems on both the North Plant 83
and South Plant 83 areas. The North Plant 83 SVE system operated for
approximately four months from June 1992 to June 1993. The South Plant
83 SVE system operated for approximately five months from October 1992
to March 1993. For groundwater, GEA's contractor, Canonie
Environmental, completed a final design dated July 21, 1993, that
contained construction details for the remedial systems for the shallow
zone groundwater remediation on the North Plant 83 and South Plant 83
areas. The North Plant 83 system initially was comprised of seven
extraction wells, and the South Plant 83 system was comprised of three
wells. These systems were augmented through their operational lifetime
to adapt to changes in groundwater concentrations and flow patterns.
After the closure of South Plant 83 in October 2010, GEA performed
additional remedial activities associated with OU5. GEA conducted
removal of soil proximate to the East and West Tank Line area in South
Plant 83 in 2011. Approximately 3.5 tons of contaminated soil and
concrete were removed and transported for final disposal at an off-site
hazardous waste disposal facility. Following removal, GEA backfilled
the area with clean fill and capped the area with a five-inch-thick,
3,000 pounds/square inch layer of reinforced concrete. GEA filed a deed
restriction in the Bernalillo County records covering areas where semi-
volatile organic compounds (i.e., polyaromatic hydrocarbons) or
hexavalent chromium contamination remained present above industrial
soil screening levels. GEA removed approximately 1,750 feet of primary
4-inch to 8-inch diameter cast iron process sewer lines, 435 feet of
similar smaller branch lines, and seven manholes and disposed these
materials at a Resource Conservation and Recovery Act treatment,
storage, and disposal facility. Finally, GEA cleaned and abandoned in
place the South Plant 83 sewer system piping and plugged the connection
to the City of Albuquerque sewer system.
Cleanup Levels
Operable Unit 1 (OU1)--There were no cleanup levels established for
OU1, as the remedy was simply replacement of a municipal water supply
well to replace the capacity lost by the contaminated SJ-6 well.
Operable Unit 2 (OU2)--There were no cleanup levels established for
OU2, as the remedy was simply the installation of additional
groundwater monitoring wells, the plugging and abandonment of wells
that could act as conduits for contaminant transport to lower
groundwater zones, the imposition of access restrictions regarding well
construction specifications and depth of completions through the State
Engineer's office, and the establishment of a groundwater monitoring
program to obtain data concerning groundwater contamination.
Operable Unit 5 (OU5)--The investigations and remediation work for
OU5 was separated by media into soil and groundwater work. For soil,
the ROD required the utilization of SVE for soil remediation but did
not specify cleanup levels. The ROD stated, ``Soils treatment will
continue until the vapor extraction system ceases to produce volatile
contaminants and will be followed by sampling to confirm soil
remediation.'' GEA obtained post remediation soil samples after the SVE
systems ceased operations and proposed cleanup levels for soils in
April 1993. The proposed cleanup levels considered soil exposure
pathways including dermal contact, inhalation, and ingestion (i.e., by
children ages 2 to 6) as well as the potential for contaminants to
leach from soil into groundwater that would exceed drinking water
standards. GEA based the cleanup levels on the assumption of an
operating manufacturing facility with restricted access but also on the
worst-case exposure scenario that the site could be converted to
residential use. During a meeting with GEA on November 2, 1993, EPA
verbally agreed to the proposed cleanup levels. In a letter dated June
21, 1994, EPA indicated that the levels of contaminants found in the
soils were below limits that required removal. In addition, out of an
abundance of caution, as part of the 2017 Remedial Action Report for
OU5, GEA performed a comparison of the post remediation soil
concentrations to the EPA Industrial and Residential Soil Screening
Levels (November 2015) which indicated all the post soil remediation
soil concentrations were below the EPA Industrial and Residential Soil
Screening Levels. For groundwater, the ROD specified that cleanup
levels would be maximum contaminant limits from the Safe Drinking Water
Act and levels in the New Mexico Water Quality Control Commission
regulations, whichever was more stringent. These levels were updated in
an Explanation of Significant Differences dated October 16, 2006, which
added a level for tetrachloroethylene promulgated under the Safe
Drinking Water Act in 1992. GEA implemented and conducted a groundwater
monitoring program throughout the operation of the shallow zone
groundwater remediation systems. After six years of monitoring
indicating that none of the off-site wells of the North Plant 83 system
well network exceeded cleanup levels, EPA approved closure of the off-
site wells and conveyance system. GEA flushed, cleaned, and abandoned
conveyance piping in place and plugged and abandoned wells in 2010. One
on-site well associated with the North Plant 83 system remained
slightly above cleanup levels. In 2010, GEA performed in-situ chemical
oxidation around this well which subsequent sampling confirmed that
contaminant concentrations fell and
[[Page 36843]]
remained below cleanup levels. The South Plant 83 system experienced a
similar history to the North Plant 83 system. By 1999, all wells
associated with the South Plant 83 system except for two wells were
below cleanup levels. By 2006, only one well had concentrations above
cleanup levels. Like the North Plant 83 system, GEA performed in-situ
chemical oxidation in 2010 around this well, which subsequent sampling
confirmed that contaminant concentrations fell below cleanup levels
shortly after the in-situ treatment and remained below cleanup levels
through 2012.
After the closure of South Plant 83 in October 2010, GEA performed
additional remedial activities associated with OU5. Utilizing
investigations results, GEA completed an assessment of the risk for the
contaminants identified in the investigation. This assessment indicated
that hexavalent chromium contamination in deep soils would not pose a
risk to human health and the environment assuming that an impermeable
cover remained in place and institutional controls were implemented.
The assessment also indicated that the semi-volatile organic compounds
(i.e., polyaromatic hydrocarbons) identified in soils would not pose a
risk to human health and the environment if the existing concrete cap
was left in place. GEA removed soil with concentrations of hexavalent
chromium above 50 milligrams per kilogram (mg/kg) but did not remove
soil with hexavalent chromium contamination ranging from 5.6 to 50 mg/
kg at depths between 5 to 14 feet below the existing concrete slab. GEA
filed a deed restriction in the Bernalillo County records covering
areas where semi-volatile organic compounds or hexavalent chromium
contamination remained above industrial soil screening levels.
Operation and Maintenance
Operable Unit 1 (OU1)--The operation and maintenance concerning the
Burton No. 4 replacement well is performed by the City of Albuquerque.
Operable Unit 2 (OU2)--There is no operation and maintenance
associated with OU2. The restriction concerning groundwater well
construction within the boundaries of the South Valley Superfund Site
issued by the New Mexico State Engineer's office on December 19, 1988,
remains in effect but is now monitored under OU6. This restriction is
not needed and does not affect the protectiveness of the actions
performed at OU2.
Operable Unit 5 (OU5)--Since the soil and groundwater remediation
systems associated with OU5 have met their associated cleanup levels
and have been dismantled, there are no operation and maintenance
activities required or ongoing for the OU5 SVE and groundwater
remediation systems. In addition, while still in effect, the New Mexico
State Engineer's restriction concerning groundwater well construction
is no longer required for the protectiveness of the OU5 remedy because
groundwater concentrations are below the maximum contaminant limits
from the Safe Drinking Water Act and levels in the New Mexico Water
Quality Control Commission regulations. After ceasing operations in
September 2010 and completing demolition of the South Plant 83
buildings in May 2011, GEA performed investigations of the South Plant
83 property which included evaluating soil impacts near any existing
sub-grade foundation features as well as the North Plant 83 and South
Plant 83 sewer systems. In addition, GEA cleaned out and abandoned in
place the sewer systems. Because of the soil investigation, GEA removed
hexavalent chromium contamination near the location of the East and
West Tank Line on the South Plant 83 property. Some contamination
remained in place and, as a result, GEA filed a declaration of
restrictive covenants on September 9, 2014 in the Bernalillo County
property records. The declaration identified five areas where semi-
volatile organic compounds or hexavalent chromium contamination exceed
industrial soil screening levels. The declaration also contained the
following: Identification of the abandoned sanitary sewer lines and
existing sewer line locations; restriction that the property use is
limited to commercial and industrial; restriction that groundwater
beneath the site cannot be used; and engineered barriers must remain in
place on portions of the property where semi-volatile organic compounds
and hexavalent chromium remain above industrial soil screening levels.
GEA performs normal property maintenance inspections of the North Plant
83 and South Plant 83 to identify fencing integrity issues and to
maintain weed control. These inspections also observe the integrity of
the concrete cap over the East and West Tank Line removal area to
ensure it is competent. GEA also ensures that the deed restriction
remains in the Bernalillo County records.
Five Year Review
Operable Unit 1 (OU1)--A five-year review is not necessary for OU1
because no hazardous substances, pollutants, or contaminants remain at
the site above levels that allow for unlimited use and unrestricted
exposure.
Operable Unit 2 (OU2)--A five-year review is not necessary for OU2
because no hazardous substances, pollutants, or contaminants remain at
the site above levels that allow for unlimited use and unrestricted
exposure. While still in effect, the New Mexico State Engineer's
restriction concerning groundwater well construction is no longer
required for the protectiveness of the OU5 remedy because groundwater
concentrations are below the maximum contaminant limits from the Safe
Drinking Water Act and levels in the New Mexico Water Quality Control
Commission regulations. In 1996, the OU2 groundwater monitoring program
was combined with the OU6 groundwater monitoring program, which is and
has been the subject of ongoing five-year reviews associated with the
Site. The next five-year review for the Site is due in July 2020.
Operable Unit 5 (OU5)--A statutory five-year review is necessary
for OU5 because hazardous substances, pollutants, or contaminants
remain at the site above levels that allow for unlimited use and
unrestricted exposure. OU5 has been the subject of ongoing five-year
reviews with the next review due in July 2020. No issues and/or
recommendations were identified in the 2015 five-year review for OU5.
Community Involvement
The major community involvement activities associated with the
operable units proposed for deletion are as follows:
Open Houses and Workshops: September 1988; November 1993;
July 1995; October 1997; September 1998; November 1999, October 2000;
November 2001; January 2013.
Original Proposed Plan Fact Sheet and Public Meetings:
June 1988; July 1988; August 1988; February 1989.
Public Meetings: October 2000; November 2001.
Original ROD Fact Sheets: July 1988; November 1988; April
1989.
Milestone Fact Sheets: May 1989; March 1990; April 1990;
June 1990; March 1991; November 1993; June 1995; April 1996; December
2011; January 2013; June 2015; July 2015; June 2018.
Citizens on Site Mailing List: 590.
Other notable community involvement activities are:
Pre Five-Year Review public notices published in local
newspapers indicating Five-Year Reviews were being initiated.
Post Five-Year Review public notices published in local
newspapers indicating Five-Year Reviews were
[[Page 36844]]
completed and available in the local repository or from the State or
EPA.
Monthly site status summaries that were made available to
the public or more recently, updates to site activities made on the
site web page available on the internet.
September 23, 2010, newspaper article in the Albuquerque
Journal concerning the closure of the General Electric plant.
Discussion of the site at public meetings associated with
the Sunport Boulevard Extension from approximately 2010 to the present.
Fact sheets and public notices have been provided in both
English and Spanish.
Determination That the Criteria for Deletion Have Been Met
The implemented remedies have achieved the degree of cleanup or
protection specified in the OU1, OU2, and OU5 RODs for the portions of
the Site proposed for deletion. The selected remedial action goals and
associated cleanup levels for the OU1, OU2, and OU5 portions of the
Site proposed for deletion are consistent with EPA policy and guidance.
No further Superfund response for the OU1, OU2, and OU5 portions of the
Site proposed for deletion are needed to protect human health and the
environment. The State of New Mexico, in an August 11, 2017, letter
from the New Mexico Environment Department, concurred with the proposed
partial deletion of the OU1, OU2, and OU5 portions of the Site from the
NPL.
The NCP specifies that EPA may delete a site from the NPL if all
appropriate response under CERCLA has been implemented and no further
response action is appropriate. 40 CFR 300.425(e)(1)(ii). EPA, with the
concurrence of the State of New Mexico, through NMED, believes that
this criterion for the deletion of the OU1, OU2, and OU5 portions of
the Site has been met and the OU1, OU2, and OU5 portions of the Site no
longer pose a threat to public health or the environment. Consequently,
EPA is proposing to delete the OU1, OU2, and OU5 portions of the Site
from the NPL. Documents supporting this action are available in the
Docket.
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.
Authority: 33 U.S.C. 1321(d); 42 U.S.C. 9601-9657; E.O. 13626,
77 FR 56749, 3 CFR, 2013 Comp., p. 306; E.O. 12777, 56 FR 54757, 3
CFR, 1991 Comp., p. 351; E.O. 12580, 52 FR 2923, 3 CFR, 1987 Comp.,
p. 193.
Dated: July 19, 2018.
Arturo Blanco,
Acting Regional Administrator, Region 6.
[FR Doc. 2018-16257 Filed 7-30-18; 8:45 am]
BILLING CODE 6560-50-P