National Oil and Hazardous Substance Pollution Contingency Plan; National Priorities List Deletion of the Waste Management of Michigan-Holland Lagoons Superfund Site, 67777-67781 [2012-27706]
Download as PDF
Federal Register / Vol. 77, No. 220 / Wednesday, November 14, 2012 / Rules and Regulations
and TFNG, N-(4trifluoromethylnicotinoyl)glycine,
calculated as the stoichiometric
equivalent of flonicamid, in or on the
following commodities.
Parts per
million
Commodity
Berry, low growing, subgroup
13–07G .............................
*
*
*
1.5
*
*
Cucumber .............................
*
*
*
1.5
*
*
Rapeseed subgroup 20A ......
*
*
*
1.5
*
*
Vegetable, cucurbit, group 9,
except cucumber ...............
*
*
*
0.4
*
*
(2) Tolerances are established for the
residues of the insecticide flonicamid,
including its metabolites and
degradates, in or on the commodities in
the table below. Compliance with the
tolerance levels specified below is to be
determined by measuring only the sum
of flonicamid, N-(cyanomethyl)-4(trifluoromethyl)-3pyridinecarboxamide, and its
metabolites, TFNA (4trifluoromethylnicotinic acid), and
TFNA–AM (4trifluoromethylnicotinamide),
calculated as the Stoichiometric
equivalent of flonicamid, in or on the
following commodities.
*
*
*
*
*
[FR Doc. 2012–27702 Filed 11–13–12; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 300
emcdonald on DSK67QTVN1PROD with RULES
[EPA–HQ–SFUND–1986–0005; FRL 9751–2]
National Oil and Hazardous Substance
Pollution Contingency Plan; National
Priorities List Deletion of the Waste
Management of Michigan-Holland
Lagoons Superfund Site
Environmental Protection
Agency.
ACTION: Direct Final Rule.
AGENCY:
The U.S. Environmental
Protection Agency (EPA) Region 5 is
publishing a direct final Notice of
SUMMARY:
VerDate Mar<15>2010
16:56 Nov 13, 2012
Jkt 229001
Deletion of the Waste Management of
Michigan-Holland Lagoons Superfund
Site (Site), located in Ottawa County,
Michigan from the National Priorities
List (NPL). The NPL, promulgated
pursuant to Section 105 of the
Comprehensive Environmental
Response, Compensation, and Liability
Act (CERCLA) of 1980, as amended, is
an appendix to the National Oil and
Hazardous Substances Pollution
Contingency Plan (NCP). This direct
final deletion is being published by EPA
with the concurrence of the State of
Michigan, through the Michigan
Department of Environmental Quality
(MDEQ), because EPA has determined
that all appropriate response actions
under CERCLA have been completed.
However, this deletion does not
preclude future actions under
Superfund.
This direct final rule is effective
January 14, 2013 unless EPA receives
adverse comments by December 14,
2012. If adverse comments are received,
EPA will publish a timely withdrawal of
the direct final deletion in the Federal
Register informing the public that the
deletion will not take effect.
ADDRESSES: Submit your comments,
identified by Docket ID no. EPA–HQ–
SFUND–1986–0005, by one of the
following methods:
• https://www.regulations.gov: Follow
on-line instructions for submitting
comments.
• Email: Gladys Beard, NPL Deletion
Process Manager, at
beard.gladys@epa.gov or Dave Novak,
Community Involvement Coordinator, at
novak.dave@epa.gov.
• Fax: Gladys Beard, NPL Deletion
Process Manager, at (312) 697–2077.
• Mail: Gladys Beard, NPL Deletion
Process Manager, U.S. Environmental
Protection Agency (SR–6J), 77 West
Jackson Boulevard, Chicago, IL 60604,
(312) 886–7253; or Dave Novak,
Community Involvement Coordinator,
U.S. Environmental Protection Agency
(SI–7J), 77 West Jackson Boulevard,
Chicago, IL 60604, (312) 886–7478 or
(800) 621–8431.
• Hand delivery: Dave Novak,
Community Involvement Coordinator,
U.S. Environmental Protection Agency
(SI–7J), 77 West Jackson Boulevard,
Chicago, IL 60604. Such deliveries are
only accepted during the docket’s
normal hours of operation, and special
arrangements should be made for
deliveries of boxed information. The
normal business hours are Monday
through Friday, 8:30 a.m. to 4:30 p.m.
CST, excluding federal holidays.
Instructions: Direct your comments to
Docket ID no. EPA–HQ–SFUND–1986–
DATES:
PO 00000
Frm 00035
Fmt 4700
Sfmt 4700
67777
0005. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available on-line at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through https://
www.regulations.gov or email. The
https://www.regulations.gov Web site is
an ‘‘anonymous access’’ system, which
means EPA will not know your identity
or contact information unless you
provide it in the body of your comment.
If you send an email comment directly
to EPA without going through https://
www.regulations.gov, your email
address will be automatically captured
and included as part of the comment
that is placed in the public docket and
made available on the Internet. If you
submit an electronic comment, EPA
recommends that you include your
name and other contact information in
the body of your comment and with any
disk or CD–ROM you submit. If EPA
cannot read your comment due to
technical difficulties and cannot contact
you for clarification, EPA may not be
able to consider your comment.
Electronic files should avoid the use of
special characters, any form of
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
may not be 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 at https://
www.regulations.gov or in hard copy at:
• U.S. Environmental Protection
Agency-Region 5, 77 West Jackson
Boulevard, Chicago, IL 60604, Phone:
(312) 353–1063. Hours: Monday through
Friday, 8:30 a.m. to 4:30 p.m. CST,
excluding Federal holidays.
• Herrick District Library, 303 South
River Avenue, Holland, MI 49423,
Phone: (616) 355–3100. Hours: Monday
through Tuesday, 9:00 a.m. to 9:00 p.m.
EST; Wednesday through Friday, 9:00
a.m. to 6:00 p.m. EST.
FOR FURTHER INFORMATION CONTACT:
Gladys Beard, NPL Deletion Process
Manager, U.S. Environmental Protection
Agency (SR–6J), 77 West Jackson
E:\FR\FM\14NOR1.SGM
14NOR1
67778
Federal Register / Vol. 77, No. 220 / Wednesday, November 14, 2012 / Rules and Regulations
Boulevard, Chicago, IL 60604, (312)
886–7253, or beard.gladys@epa.gov.
SUPPLEMENTARY INFORMATION:
received during the public comment
period.
Table of Contents
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.
II. NPL Deletion Criteria
emcdonald on DSK67QTVN1PROD with RULES
I. Introduction
II. NPL Deletion Criteria
III. Deletion Procedures
IV. Basis for Site Deletion
V. Deletion Action
I. Introduction
EPA Region 5 is publishing this direct
final Notice of Deletion of the Waste
Management of Michigan-Holland
Lagoons Superfund Site (Holland
Lagoons Site) from the National
Priorities List (NPL). 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 the list of
sites that appear to present a significant
risk to public health, welfare, or the
environment. Sites on the NPL may be
the subject of remedial actions financed
by the Hazardous Substance Superfund
(Fund). As described in 300.425(e)(3) of
the NCP, sites deleted from the NPL
remain eligible for Fund-financed
remedial actions if future conditions
warrant such actions.
Because EPA considers this action to
be noncontroversial and routine, this
action will be effective January 14, 2013
unless EPA receives adverse comments
by December 14, 2012. Along with this
direct final Notice of Deletion, EPA is
co-publishing a Notice of Intent to
Delete in the ‘‘Proposed Rules’’ section
of this issue of the Federal Register. If
adverse comments are received within
the 30-day public comment period on
this deletion action, EPA will publish a
timely withdrawal of this direct final
Notice of Deletion before the effective
date of the deletion, and the deletion
will not take effect. EPA will, as
appropriate, prepare a response to
comments and continue with the
deletion process on the basis of the
Notice of Intent to Delete and the
comments already received. There will
be no additional opportunity to
comment.
Section II of this document explains
the criteria for deleting sites from the
NPL. Section III discusses procedures
that EPA is using for this action. Section
IV discusses the Holland Lagoons Site
and demonstrates how it meets the
deletion criteria. Section V discusses
EPA’s action to delete the Site from the
NPL unless adverse comments are
VerDate Mar<15>2010
14:32 Nov 13, 2012
Jkt 229001
III. Deletion Procedures
The following procedures apply to
deletion of the Site:
(1) EPA consulted with the State of
Michigan prior to developing this direct
final Notice of Deletion and the Notice
of Intent to Delete co-published today in
the ‘‘Proposed Rules’’ section of the
Federal Register.
(2) EPA has provided the State 30
working days for review of this notice
and the parallel Notice of Intent to
Delete prior to their publication today,
and the State, through MDEQ, has
concurred on the deletion of the Site
from the NPL.
(3) Concurrently with the publication
of this direct final Notice of Deletion, a
notice of the availability of the parallel
Notice of Intent to Delete is being
published in a major local newspaper,
the Holland Sentinel Newspaper. The
newspaper notice announces the 30-day
public comment period concerning the
Notice of Intent to Delete the Site from
the NPL.
(4) EPA placed copies of documents
supporting the proposed deletion in the
deletion docket and made these items
available for public inspection and
copying at the Site information
repositories identified above.
(5) If adverse comments are received
within the 30-day public comment
period on this deletion action, EPA will
publish a timely notice of withdrawal of
this direct final Notice of Deletion
before its effective date and will prepare
a response to comments and continue
with the deletion process on the basis of
PO 00000
Frm 00036
Fmt 4700
Sfmt 4700
the Notice of Intent to Delete and the
comments already received.
Deletion of a site from the NPL does
not itself create, alter, or revoke any
individual’s rights or obligations.
Deletion 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.
IV. Basis for Site Deletion
The following information provides
EPA’s rationale for deleting the Site
from the NPL.
Site Background and History
The Holland Lagoons Site (CERCLIS
ID# MID060179587) is located at 2700
North 168th Avenue, between Riley and
James Streets, in unincorporated Park
Township, near Holland, Michigan. The
Site is an 80-acre property located about
0.5 miles from the eastern shore of Lake
Michigan in Ottawa County. The Site
consists of a site entrance, former lagoon
area, dewatering lagoons, former landfill
area, a haul road on the eastern half of
the Site, and an office/maintenance
garage building. The area around the
Site consists of mixed residential,
recreational, and agricultural use.
Properties adjoining the Holland
Lagoons Site include the Riley Road
Recreational Area, several small
subdivisions of homes, privately held
parcels, and a blueberry field to the
southeast. The Southwest Ottawa
County Landfill (SWOCLF) Superfund
Site is adjacent to, northeast, and
upgradient of the Holland Lagoons Site.
The SWOCLF Site is a state-lead
enforcement site. A groundwater plume
migrating from the SWOCLF Site
impacts the groundwater southwest and
downgradient of the county landfill,
including groundwater beneath the
Holland Lagoons Site.
The Holland Lagoons Site was
operated by Jacobusse Refuse Service
Company as a municipal garbage dump,
liquid waste dewatering facility, and
headquarters for its hauling company
from the mid 1940’s until 1977. The
company was purchased by Refuse
Services, Inc., in 1972 and the name was
changed to Holland Lagoons. Refuse
Services, Inc., merged into Michigan
Waste Systems, Inc. in 1973 and
Michigan Waste Systems, Inc.
subsequently changed its name to Waste
Management of Michigan, Inc. (WMMI).
E:\FR\FM\14NOR1.SGM
14NOR1
Federal Register / Vol. 77, No. 220 / Wednesday, November 14, 2012 / Rules and Regulations
emcdonald on DSK67QTVN1PROD with RULES
A portion of the Site was originally
used for the disposal of vegetable
pickling waste, apple pulp, digester
sludge, barrels of spent extracts, brine,
the dewatering of liquid industrial
wastes, including aluminum and metal
hydroxide wastes, and wastewater
treatment plant sludge. Disposal
occurred in up to as many as nine
dewatering lagoons located in the north
central area of the Site. The dewatering
of metallic wastes using these lagoons
ceased in October 1977. Permits
indicate that Jacobusse discontinued
disposal of all liquid waste at the Site
in 1980. In addition, the southwest area
of the Site was used for the temporary
burial of drums of chloral hydrate,
which were removed in 1980.
Municipal refuse was hauled to a
landfill located in the south central area
of the Site from 1957 to 1964. The
landfill operated as an open burning
dump and the northwest corner of the
Site was used as a maintenance facility
for the Jacobusse fleet of trucks.
The Thomas residential well, located
due west of the Site, was discovered to
be contaminated with trichloroethylene
(TCE) in 1970. The TCE was suspected
to have migrated from the Holland
Lagoons Site. The continued presence of
elevated concentrations of TCE was
confirmed in a Michigan Department of
Natural Resources (MDNR) follow-up
sampling event in 1979. Park Township
began to hook up residences located
within the vicinity of the Holland
Lagoons Site, including the Thomas
residence, to the expanded municipal
water supply line by 1984. The county
and township continued to hook up
residences downgradient of the Holland
Lagoons and SWOCLF Sites into the
expanded municipal water supply
system. The Holland Lagoons Site was
proposed to the NPL on October 15,
1984 (49 FR 40320) and finalized on the
NPL on June 10, 1986 (51 FR 21099).
From 1993 through 1997, EPA and
MDEQ (formerly a part of MDNR) held
discussions to allow NPL sites with a
state-lead enforcement designation to
follow the Remedial Action Plan
process in Part 201 of the Michigan
Natural Resources and Environmental
Protection Act (NREPA). The EPA and
MDEQ signed a Memorandum of
Agreement in 1997 for the Holland
Lagoons Site.
Remedial Investigation and Feasibility
Study
In 1994, the MDNR and WMMI
entered into an Administrative Order by
Consent (AOC) for Response Activities
for WMMI to undertake a Remedial
Investigation/Feasibility Study (RI/FS)
at the Site. In addition to actions taken
VerDate Mar<15>2010
14:32 Nov 13, 2012
Jkt 229001
earlier, WMMI removed four
underground storage tanks from within
the truck maintenance area in 1985.
Concurrent with the RI, WMMI
performed an Interim Response Action
(IRA) at the Site by excavating
discolored soils plausibly contaminated
with heavy metals on the haul road and
from other on-site areas and to remove
general surface debris from the Site.
WMMI also excavated the former
municipal trash landfill area and
disposed of the material off-site. The
interim response was completed by the
end of 2000. All subsequent soil
samples showed levels of metals at or
below generic residential criteria or
background values for the State of
Michigan. Michigan Part 201 Cleanup
Criteria is within EPA’s acceptable risk
range. WMMI performed a RI and
baseline risk assessment, including an
ecological assessment at the Site from
1994–1996 and additional sampling
between 1998 and 2007.
Area A—Site Entrance: Soil boring
samples were collected and analyzed for
inorganic and organic parameters. The
white powder found on the ground
surface north of the Site building
appeared to be lime based on the
elevated calcium level; however, the
calcium levels were below background
concentrations. No organic
contaminants were detected above
background or Part 201 Residential
Cleanup Criteria. A trench
approximately 80 feet by 10 feet was
discovered in an area south of the
building. A soil boring was collected
and analysis detected lead and zinc at
concentrations above background. The
approximately 40 cubic yards of
impacted soil was excavated during the
IRA. No contaminants were detected
above background or Part 201
Residential Cleanup Criteria in
verification samples.
Additional soil samples were
collected from the same location as the
previous collection and consisted
mostly of the white powder material.
Analysis detected no inorganic
contaminants at concentrations that
exceeded Part 201 Residential Cleanup
Criteria.
Area B—Former Dewatering Lagoon
Area: Analysis of the soil boring
samples collected from the former
dewatering lagoon area did not detect
any organic or inorganic contaminants
above background or Part 201
Residential Cleanup Criteria. The results
of the soil borings and analysis from the
investigation demonstrated that the
lagoons were properly abandoned.
Area C—Former Landfill Area:
Analysis of the soil boring samples
collected from the former landfill area
PO 00000
Frm 00037
Fmt 4700
Sfmt 4700
67779
did not detect any organic or inorganic
contaminants above background or Part
201 Residential Cleanup Criteria. The
ash, metal cans, and glass bottles in the
former landfill area were excavated
during the IRA for disposal off-site.
Approximately 1,855 cubic yards of
material was removed from the area.
Results of the analysis of verification
samples showed there were two small
areas with levels of inorganic
parameters exceeding the background
concentration. An additional 40 cubic
yards of soil was removed during the
interim response and disposed of offsite. No contaminants were detected
above background or Part 201
Residential Cleanup Criteria in
verification samples.
A bermed drum area was located in
the south end of the former landfill. The
berm was 70 by 30 feet and contained
six old, rusted drums. These drums
were removed during the IRA along
with 224 cubic feet of bluish-green
stained soil found at the bottom of the
bermed area. No contaminants were
detected above background or Part 201
Residential Cleanup Criteria in
verification samples.
Area D—Haul Road: The results of the
soil boring sampling from the haul road
indicated that the bluish-green soil
found at the ground surface along parts
of the road was contaminated with
heavy metals. Analysis of the soil
sample detected chromium, copper,
lead, nickel, selenium, zinc, and
cyanide above their background values.
Impacted soil which was identified in
the previous investigations was
removed during the IRA. An area 400
feet by 70 feet by 1.5 feet deep was
excavated, removing approximately
1,433 cubic yards of soil. Verification
samples indicated the soil that remained
was not impacted above background
concentrations for heavy metals. An
additional 30 cubic yards of soil was
removed from the adjacent Ottawa
County property.
During an additional investigation,
another 540 cubic yards of soil was
excavated from the haul road area and
disposed of off-site. The verification
samples collected demonstrated that the
remaining soil met the Part 201
Residential Cleanup Criteria.
Area E—Former Drum Burial Area:
Analysis of the soil boring samples
collected from the former drum burial
area did not detect any organic or
inorganic contaminants above
background or Part 201 Residential
Cleanup Criteria.
Area F—Eastern Half of Site: The
investigation of this area of concern
involved collecting two soil samples
from four boring locations. Four
E:\FR\FM\14NOR1.SGM
14NOR1
emcdonald on DSK67QTVN1PROD with RULES
67780
Federal Register / Vol. 77, No. 220 / Wednesday, November 14, 2012 / Rules and Regulations
additional borings were collected from
along the eastern edge of the area for
background analysis. The results of the
background borings and the soil borings
indicated no contaminants were
detected above the Part 201 Residential
Cleanup Criteria. No environmental
hazard was found in the eastern half of
the Site.
Underground Storage Tanks (USTs):
An initial review of the 1985 UST report
did not clearly indicate that the four
USTs had been removed, as a result
subsequent investigations focused on
finding these USTs and determining
whether there was any related
contamination.
During the investigations, soil boring
samples were collected from the areas of
the USTs at the northeast corner and
southwest corner of the building. The
investigation also involved searching
the area with an electro-magnetic (EM)
detector to determine if there were any
large metal objects buried in the area.
No drums were detected; therefore, it
was concluded that all four of the USTs
had been removed. The results of these
soil boring samples did not detect any
petroleum hydrocarbon or organic
contaminants above Part 201 Residential
Cleanup Criteria.
Groundwater: Groundwater was
sampled as part of several
investigations. The results of the
groundwater samples collected
upgradient of the Site were used to
develop inorganic parameters
background and anthropogenic
background concentrations for the area.
Background concentrations are
concentrations of chemicals common to
groundwater that have not been
impacted by anthropogenic effects.
Anthropogenic background levels are
determined by analyzing groundwater
that has been impacted by an upgradient
source such as the SWOCLF Site.
Anthropogenic background
concentrations were determined from
several wells located downgradient of
the SWOCLF Site, but upgradient of any
known disposal areas on the Holland
Lagoons Site.
Benzene was the only organic
contaminant detected in the on-site
monitoring wells above the Maximum
Contaminant Levels (MCL) established
under the Safe Drinking Water Act
(SDWA) and Part 201 Residential
Cleanup Criteria of 5 micrograms per
liter (mg/1). All of these detections were
found in wells located southwest of the
Site at concentrations ranging from 14
mg/l to 28 mg/1 and no on-site source
was detected. Benzene is a contaminant
being monitored at the SWOCLF Site. At
the SWOCLF Site, benzene had been
detected at levels as high as 149 mg/1 in
VerDate Mar<15>2010
14:32 Nov 13, 2012
Jkt 229001
purge wells and 305 mg/1 in monitoring
wells; therefore, the MDEQ concluded
that the source of the benzene is the
SWOCLF Site.
Inorganic contaminants found in
wells on-site includes: aluminum,
arsenic, antimony, beryllium, cadmium,
lead, manganese, zinc, and vanadium.
Aluminum, antimony, lead, manganese,
and zinc were found in background or
anthropogenic background wells.
Arsenic did not exceed the MCL or Part
201 Residential Cleanup Criteria.
Subsequent sampling results indicated
that aluminum, antimony, beryllium,
cadmium, lead, manganese, zinc, and
vanadium did not exceed MCLs, Part
201 Residential Cleanup Criteria,
background and/or anthropogenic
background.
In March 2005, the MDEQ and Ottawa
County entered into a Stipulation for the
SWOCLF Site, under which Ottawa
County is required to perform the
following remedial actions at the
SWOCLF Site: construct a new landfill
cap; install and operate a new extraction
well system around the landfill; prevent
the discharge to Lake Michigan of
groundwater containing hazardous
substances exceeding Groundwater to
Surface Water Interface Criteria;
implement reliable land and resource
use restrictions (institutional controls)
to restrict construction and use of wells
within the groundwater plume; properly
abandon all existing residential wells
once residents have been hooked into
the municipal water supply; and operate
the then current downgradient
extraction system until it was
demonstrated that requirements have
been achieved. The responsibility for
the remaining wells on the Holland
Lagoons Site has been transferred to
Ottawa County to use in monitoring the
SWOCLF plume.
Currently, Ottawa County has
constructed the new landfill cap and
completed the hook up of residents to
the municipal water supply. In 2009,
Ottawa County implemented an areawide groundwater use restriction which
prohibits human consumption of
groundwater, limits well installation/
use and outlines procedures for well
abandonments. All hook ups and
abandonments were completed in 2009.
Ottawa County continues to operate the
downgradient extraction system. In
2009, Ottawa County installed and
began operating the new extraction well
system along the west and south
boundary of the SWOCLF Site.
Former Facility Office and
Maintenance Garage Building: WMMI
conducted soil and groundwater
sampling below the former facility office
and maintenance garage building as
PO 00000
Frm 00038
Fmt 4700
Sfmt 4700
noted as a recommendation in the 2006
Five-Year Review Report. The soil and
groundwater sampling results did not
reveal any chemicals of concerns above
MCLs or Part 201 Residential Criteria.
Decision Summary: The Final
Feasibility Study and Remedial Action
Plan Closure Report, which called for
No Further Action to be implemented at
the Site was approved by MDEQ on
October 13, 2008. On May 19, 2011, the
MDEQ approved WMMI’s request to
rescind the August 18, 1997 restrictive
covenant because Ottawa County has
implemented an area-wide groundwater
restriction as part of the SWOCLF
cleanup program. The Notice of
Rescission of Land and/or Resources
Use Restrictions was filed and recorded
by the Ottawa County Register of Deeds
on June 2, 2011. The Ottawa County
Contaminated Groundwater Use
Ordinance (March 2009) meets the
requirements of a ‘‘reliable use
restriction’’ under Michigan’s cleanup
rules (Part 201).
The rescinded restrictive covenant
provided the following restrictions at
the Holland Lagoons Site: (1) Restricts
the use of the property to those uses
compatible with the limited residential
land use criteria as defined in Section
20120a(1)(f) of Part 201; (2) prohibits
groundwater well installation and
groundwater use within the property
boundary for all domestic, commercial,
and industrial uses; (3) prohibits the
construction of groundwater fed
impoundments; (4) prohibits excavation
of soil beyond the saturated zone; and
(5) requires soil sampling if existing
structure is razed and 30-days notice to
MDEQ.
Selected Remedy
EPA signed a ROD on August 17, 2011
and has determined that no further
remedial action is necessary for the
Holland Lagoons Site. The remedy is
protective of human health and the
environment; and allows for unlimited
exposure and unrestricted use.
Response Actions
The August 2011, ‘‘No Further
Action’’ ROD determined that no further
Federal response was required.
Operation and Maintenance
The groundwater underneath the Site
is monitored as part of the Ottawa
County SWOCLF groundwater
monitoring program and contamination
in the groundwater plumes is not
related to contamination and sources at
Holland Lagoons Site. There will be no
active remediation at the Site; therefore,
no operation and maintenance (O&M) is
necessary.
E:\FR\FM\14NOR1.SGM
14NOR1
Federal Register / Vol. 77, No. 220 / Wednesday, November 14, 2012 / Rules and Regulations
Five-Year Review
emcdonald on DSK67QTVN1PROD with RULES
The first and only five-year review,
completed on September 25, 2006,
found the remedy to be protective in the
short-term and identified five issues that
needed to be addressed in order for the
remedy to be protective in the longterm. All of the issues have now been
addressed as described below:
1. Issue: Noncompliance with the
AOC requires the completion of a Part
201 approved Feasibility Study and
Remedial Action Plan Closure Report.
Follow-Up: The MDEQ approved the
Final Feasibility Study and Remedial
Action Plan Closure Report on October
13, 2008, which was submitted by
WMMI.
2. Issue: WMMI must provide
information to prove the six on-site
source areas, due to the completion of
past remediation activities, are no
longer contributing contaminants to the
groundwater plume migrating under the
Site and that all of the contaminants
found in the groundwater plume
originate from the adjacent and
upgradient SWOCLF Site. Follow-Up:
The Final Feasibility Study and
Remedial Action Plan Closure Report
included data to confirm that the past
remediation activities were completed
at the six on-site areas and that no onsite sources were contributing to the
groundwater plume migrating onto the
Holland Lagoons Site from the SWOCLF
Site.
3. Issue: Ensure that effective interim
institutional controls (ICs) are in place.
Follow-Up: EPA’s ‘‘No Further Action’’
ROD did not require any additional ICs
because: (1) groundwater impacts were
determined to be migrating from the
SWOCLF Site and not part of siterelated contamination from Holland
Lagoons and (2) an area-wide
groundwater ordinance has been
implemented as part of the response at
the SWOCLF Site. As a result, the
Declaration of Restrictive Covenant has
been rescinded. The Notice of
Rescission of Land and/or Resources
Use Restrictions was filed and recorded
by the Ottawa County Register of Deeds
on June 2, 2011. Ottawa County will
continue conducting a cleanup of the
SWOCLF Site, including maintenance of
VerDate Mar<15>2010
14:32 Nov 13, 2012
Jkt 229001
an area-wide groundwater use
restriction to prevent groundwater use.
4. Issue: For the remedy to be
protective in the long-term, effective ICs
may be implemented and maintained as
part of the final RAP. Follow-up: EPA’s
‘‘No Further Action’’ ROD did not
require ICs. The ROD allows for
unlimited use and unrestricted
exposure.
5. Issue: A contamination source area
may exist beneath the former office
building. Follow-up: In 2007, WMMI
conducted soil and groundwater
sampling below the former facility office
and maintenance garage building. The
soil and groundwater sampling results
did not reveal any chemicals of concern
above the MCLs or Part 201 criteria.
In summary, EPA has determined that
no further remedial action is necessary
for the Holland Lagoons Site. Previous
responses at the Site eliminated the
need for a further remedial action.
Contaminated soil from on-site disposal
pits was excavated and disposed of offsite. No further five-year reviews are
required because contamination has
been remediated to allow for unlimited
use and unrestricted exposure.
Community Involvement
Public participation activities have
been satisfied as required in CERCLA
Section 113(k), 42 U.S.C. 9613(k), and
CERCLA Section 117, 42 U.S.C. 9617.
Documents in the deletion docket,
which EPA relied on for
recommendation of the deletion of this
Site from the NPL, are available to the
public in the information repositories
and at www.regulations.gov.
Determination That the Site Meets the
Criteria for Deletion in the NCP
The NCP (40 CFR 300.425(e)) states
that a site may be deleted from the NPL
when no further response action is
appropriate. EPA, in consultation with
the State of Michigan, has determined
that the responsible parties have
implemented all response actions
required, and no further response action
by responsible parties is appropriate.
V. Deletion Action
EPA, with concurrence from State of
Michigan through the MDEQ, has
PO 00000
Frm 00039
Fmt 4700
Sfmt 9990
67781
determined that all appropriate
response actions under CERCLA have
been completed. EPA received
concurrence from the State of Michigan
on April 5, 2012. Therefore, EPA is
deleting this Site from the NPL.
Because EPA considers this action to
be noncontroversial and routine, EPA is
taking it without prior publication. This
action will be effective January 14, 2013
unless EPA receives adverse comments
by December 14, 2012. If adverse
comments are received within the 30day public comment period, EPA will
publish a timely withdrawal of this
direct final Notice of Deletion before the
effective date of the deletion, and it will
not take effect. EPA will prepare a
response to comments and continue
with the deletion process on the basis of
the notice of intent to delete and the
comments already received. There will
be no additional opportunity to
comment.
List of Subjects in 40 CFR Part 300
Environmental protection, Air
pollution control, Chemicals, Hazardous
waste, Hazardous substances,
Intergovernmental relations, Penalties,
Reporting and recordkeeping
requirements, Superfund, Water
pollution control, and Water supply.
Dated: October 31, 2012.
Susan Hedman,
Regional Administrator, Region 5.
For the reasons set out in this
document, 40 CFR part 300 is amended
as follows:
PART 300—[AMENDED]
1. The authority citation for part 300
continues to read as follows:
■
Authority: 33 U.S.C. 1321(c)(2); 42 U.S.C.
9601–9657; E.O. 12777, 56 FR 54757, 3 CFR,
1991 Comp., p. 351; E.O. 12580, 52 FR 2923;
3 CFR, 1987 Comp., p. 193.
Appendix B to Part 300 [Amended]
2. Table 1 of Appendix B to part 300
is amended by removing, the entry for
‘‘MI, Waste Management of Michigan
(Holland), Holland’’.
■
[FR Doc. 2012–27706 Filed 11–13–12; 8:45 am]
BILLING CODE P
E:\FR\FM\14NOR1.SGM
14NOR1
Agencies
[Federal Register Volume 77, Number 220 (Wednesday, November 14, 2012)]
[Rules and Regulations]
[Pages 67777-67781]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2012-27706]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 300
[EPA-HQ-SFUND-1986-0005; FRL 9751-2]
National Oil and Hazardous Substance Pollution Contingency Plan;
National Priorities List Deletion of the Waste Management of Michigan-
Holland Lagoons Superfund Site
AGENCY: Environmental Protection Agency.
ACTION: Direct Final Rule.
-----------------------------------------------------------------------
SUMMARY: The U.S. Environmental Protection Agency (EPA) Region 5 is
publishing a direct final Notice of Deletion of the Waste Management of
Michigan-Holland Lagoons Superfund Site (Site), located in Ottawa
County, Michigan from the National Priorities List (NPL). The NPL,
promulgated pursuant to Section 105 of the Comprehensive Environmental
Response, Compensation, and Liability Act (CERCLA) of 1980, as amended,
is an appendix to the National Oil and Hazardous Substances Pollution
Contingency Plan (NCP). This direct final deletion is being published
by EPA with the concurrence of the State of Michigan, through the
Michigan Department of Environmental Quality (MDEQ), because EPA has
determined that all appropriate response actions under CERCLA have been
completed. However, this deletion does not preclude future actions
under Superfund.
DATES: This direct final rule is effective January 14, 2013 unless EPA
receives adverse comments by December 14, 2012. If adverse comments are
received, EPA will publish a timely withdrawal of the direct final
deletion in the Federal Register informing the public that the deletion
will not take effect.
ADDRESSES: Submit your comments, identified by Docket ID no. EPA-HQ-
SFUND-1986-0005, by one of the following methods:
https://www.regulations.gov: Follow on-line instructions
for submitting comments.
Email: Gladys Beard, NPL Deletion Process Manager, at
beard.gladys@epa.gov or Dave Novak, Community Involvement Coordinator,
at novak.dave@epa.gov.
Fax: Gladys Beard, NPL Deletion Process Manager, at (312)
697-2077.
Mail: Gladys Beard, NPL Deletion Process Manager, U.S.
Environmental Protection Agency (SR-6J), 77 West Jackson Boulevard,
Chicago, IL 60604, (312) 886-7253; or Dave Novak, Community Involvement
Coordinator, U.S. Environmental Protection Agency (SI-7J), 77 West
Jackson Boulevard, Chicago, IL 60604, (312) 886-7478 or (800) 621-8431.
Hand delivery: Dave Novak, Community Involvement
Coordinator, U.S. Environmental Protection Agency (SI-7J), 77 West
Jackson Boulevard, Chicago, IL 60604. Such deliveries are only accepted
during the docket's normal hours of operation, and special arrangements
should be made for deliveries of boxed information. The normal business
hours are Monday through Friday, 8:30 a.m. to 4:30 p.m. CST, excluding
federal holidays.
Instructions: Direct your comments to Docket ID no. EPA-HQ-SFUND-
1986-0005. EPA's policy is that all comments received will be included
in the public docket without change and may be made available on-line
at https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through https://www.regulations.gov or email. The https://www.regulations.gov Web site
is an ``anonymous access'' system, which means EPA will not know your
identity or contact information unless you provide it in the body of
your comment. If you send an email comment directly to EPA without
going through https://www.regulations.gov, your email address will be
automatically captured and included as part of the comment that is
placed in the public docket and made available on the Internet. If you
submit an electronic comment, EPA recommends that you include your name
and other contact information in the body of your comment and with any
disk or CD-ROM you submit. If EPA cannot read your comment due to
technical difficulties and cannot contact you for clarification, EPA
may not be able to consider your comment. Electronic files should avoid
the use of special characters, any form of 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 may not be 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 at https://www.regulations.gov or in hard copy at:
U.S. Environmental Protection Agency-Region 5, 77 West
Jackson Boulevard, Chicago, IL 60604, Phone: (312) 353-1063. Hours:
Monday through Friday, 8:30 a.m. to 4:30 p.m. CST, excluding Federal
holidays.
Herrick District Library, 303 South River Avenue, Holland,
MI 49423, Phone: (616) 355-3100. Hours: Monday through Tuesday, 9:00
a.m. to 9:00 p.m. EST; Wednesday through Friday, 9:00 a.m. to 6:00 p.m.
EST.
FOR FURTHER INFORMATION CONTACT: Gladys Beard, NPL Deletion Process
Manager, U.S. Environmental Protection Agency (SR-6J), 77 West Jackson
[[Page 67778]]
Boulevard, Chicago, IL 60604, (312) 886-7253, or beard.gladys@epa.gov.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Introduction
II. NPL Deletion Criteria
III. Deletion Procedures
IV. Basis for Site Deletion
V. Deletion Action
I. Introduction
EPA Region 5 is publishing this direct final Notice of Deletion of
the Waste Management of Michigan-Holland Lagoons Superfund Site
(Holland Lagoons Site) from the National Priorities List (NPL). 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 the list of sites that appear to present a
significant risk to public health, welfare, or the environment. Sites
on the NPL may be the subject of remedial actions financed by the
Hazardous Substance Superfund (Fund). As described in 300.425(e)(3) of
the NCP, sites deleted from the NPL remain eligible for Fund-financed
remedial actions if future conditions warrant such actions.
Because EPA considers this action to be noncontroversial and
routine, this action will be effective January 14, 2013 unless EPA
receives adverse comments by December 14, 2012. Along with this direct
final Notice of Deletion, EPA is co-publishing a Notice of Intent to
Delete in the ``Proposed Rules'' section of this issue of the Federal
Register. If adverse comments are received within the 30-day public
comment period on this deletion action, EPA will publish a timely
withdrawal of this direct final Notice of Deletion before the effective
date of the deletion, and the deletion will not take effect. EPA will,
as appropriate, prepare a response to comments and continue with the
deletion process on the basis of the Notice of Intent to Delete and the
comments already received. There will be no additional opportunity to
comment.
Section II of this document explains the criteria for deleting
sites from the NPL. Section III discusses procedures that EPA is using
for this action. Section IV discusses the Holland Lagoons Site and
demonstrates how it meets the deletion criteria. Section V discusses
EPA's action to delete the Site from the NPL unless adverse comments
are received during the public comment period.
II. NPL Deletion Criteria
The NCP establishes the criteria that EPA uses to delete sites from
the NPL. In accordance with 40 CFR 300.425(e), sites may be deleted
from the NPL where no further response is appropriate. In making such a
determination pursuant to 40 CFR 300.425(e), EPA will consider, in
consultation with the State, whether any of the following criteria have
been met:
i. Responsible parties or other persons have implemented all
appropriate response actions required;
ii. All appropriate Fund-financed response under CERCLA has been
implemented, and no further response action by responsible parties is
appropriate; or
iii. The remedial investigation has shown that the release poses no
significant threat to public health or the environment and, therefore,
the taking of remedial measures is not appropriate.
III. Deletion Procedures
The following procedures apply to deletion of the Site:
(1) EPA consulted with the State of Michigan prior to developing
this direct final Notice of Deletion and the Notice of Intent to Delete
co-published today in the ``Proposed Rules'' section of the Federal
Register.
(2) EPA has provided the State 30 working days for review of this
notice and the parallel Notice of Intent to Delete prior to their
publication today, and the State, through MDEQ, has concurred on the
deletion of the Site from the NPL.
(3) Concurrently with the publication of this direct final Notice
of Deletion, a notice of the availability of the parallel Notice of
Intent to Delete is being published in a major local newspaper, the
Holland Sentinel Newspaper. The newspaper notice announces the 30-day
public comment period concerning the Notice of Intent to Delete the
Site from the NPL.
(4) EPA placed copies of documents supporting the proposed deletion
in the deletion docket and made these items available for public
inspection and copying at the Site information repositories identified
above.
(5) If adverse comments are received within the 30-day public
comment period on this deletion action, EPA will publish a timely
notice of withdrawal of this direct final Notice of Deletion before its
effective date and will prepare a response to comments and continue
with the deletion process on the basis of the Notice of Intent to
Delete and the comments already received.
Deletion of a site from the NPL does not itself create, alter, or
revoke any individual's rights or obligations. Deletion 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.
IV. Basis for Site Deletion
The following information provides EPA's rationale for deleting the
Site from the NPL.
Site Background and History
The Holland Lagoons Site (CERCLIS ID MID060179587) is
located at 2700 North 168th Avenue, between Riley and James Streets, in
unincorporated Park Township, near Holland, Michigan. The Site is an
80-acre property located about 0.5 miles from the eastern shore of Lake
Michigan in Ottawa County. The Site consists of a site entrance, former
lagoon area, dewatering lagoons, former landfill area, a haul road on
the eastern half of the Site, and an office/maintenance garage
building. The area around the Site consists of mixed residential,
recreational, and agricultural use.
Properties adjoining the Holland Lagoons Site include the Riley
Road Recreational Area, several small subdivisions of homes, privately
held parcels, and a blueberry field to the southeast. The Southwest
Ottawa County Landfill (SWOCLF) Superfund Site is adjacent to,
northeast, and upgradient of the Holland Lagoons Site. The SWOCLF Site
is a state-lead enforcement site. A groundwater plume migrating from
the SWOCLF Site impacts the groundwater southwest and downgradient of
the county landfill, including groundwater beneath the Holland Lagoons
Site.
The Holland Lagoons Site was operated by Jacobusse Refuse Service
Company as a municipal garbage dump, liquid waste dewatering facility,
and headquarters for its hauling company from the mid 1940's until
1977. The company was purchased by Refuse Services, Inc., in 1972 and
the name was changed to Holland Lagoons. Refuse Services, Inc., merged
into Michigan Waste Systems, Inc. in 1973 and Michigan Waste Systems,
Inc. subsequently changed its name to Waste Management of Michigan,
Inc. (WMMI).
[[Page 67779]]
A portion of the Site was originally used for the disposal of
vegetable pickling waste, apple pulp, digester sludge, barrels of spent
extracts, brine, the dewatering of liquid industrial wastes, including
aluminum and metal hydroxide wastes, and wastewater treatment plant
sludge. Disposal occurred in up to as many as nine dewatering lagoons
located in the north central area of the Site. The dewatering of
metallic wastes using these lagoons ceased in October 1977. Permits
indicate that Jacobusse discontinued disposal of all liquid waste at
the Site in 1980. In addition, the southwest area of the Site was used
for the temporary burial of drums of chloral hydrate, which were
removed in 1980. Municipal refuse was hauled to a landfill located in
the south central area of the Site from 1957 to 1964. The landfill
operated as an open burning dump and the northwest corner of the Site
was used as a maintenance facility for the Jacobusse fleet of trucks.
The Thomas residential well, located due west of the Site, was
discovered to be contaminated with trichloroethylene (TCE) in 1970. The
TCE was suspected to have migrated from the Holland Lagoons Site. The
continued presence of elevated concentrations of TCE was confirmed in a
Michigan Department of Natural Resources (MDNR) follow-up sampling
event in 1979. Park Township began to hook up residences located within
the vicinity of the Holland Lagoons Site, including the Thomas
residence, to the expanded municipal water supply line by 1984. The
county and township continued to hook up residences downgradient of the
Holland Lagoons and SWOCLF Sites into the expanded municipal water
supply system. The Holland Lagoons Site was proposed to the NPL on
October 15, 1984 (49 FR 40320) and finalized on the NPL on June 10,
1986 (51 FR 21099).
From 1993 through 1997, EPA and MDEQ (formerly a part of MDNR) held
discussions to allow NPL sites with a state-lead enforcement
designation to follow the Remedial Action Plan process in Part 201 of
the Michigan Natural Resources and Environmental Protection Act
(NREPA). The EPA and MDEQ signed a Memorandum of Agreement in 1997 for
the Holland Lagoons Site.
Remedial Investigation and Feasibility Study
In 1994, the MDNR and WMMI entered into an Administrative Order by
Consent (AOC) for Response Activities for WMMI to undertake a Remedial
Investigation/Feasibility Study (RI/FS) at the Site. In addition to
actions taken earlier, WMMI removed four underground storage tanks from
within the truck maintenance area in 1985. Concurrent with the RI, WMMI
performed an Interim Response Action (IRA) at the Site by excavating
discolored soils plausibly contaminated with heavy metals on the haul
road and from other on-site areas and to remove general surface debris
from the Site. WMMI also excavated the former municipal trash landfill
area and disposed of the material off-site. The interim response was
completed by the end of 2000. All subsequent soil samples showed levels
of metals at or below generic residential criteria or background values
for the State of Michigan. Michigan Part 201 Cleanup Criteria is within
EPA's acceptable risk range. WMMI performed a RI and baseline risk
assessment, including an ecological assessment at the Site from 1994-
1996 and additional sampling between 1998 and 2007.
Area A--Site Entrance: Soil boring samples were collected and
analyzed for inorganic and organic parameters. The white powder found
on the ground surface north of the Site building appeared to be lime
based on the elevated calcium level; however, the calcium levels were
below background concentrations. No organic contaminants were detected
above background or Part 201 Residential Cleanup Criteria. A trench
approximately 80 feet by 10 feet was discovered in an area south of the
building. A soil boring was collected and analysis detected lead and
zinc at concentrations above background. The approximately 40 cubic
yards of impacted soil was excavated during the IRA. No contaminants
were detected above background or Part 201 Residential Cleanup Criteria
in verification samples.
Additional soil samples were collected from the same location as
the previous collection and consisted mostly of the white powder
material. Analysis detected no inorganic contaminants at concentrations
that exceeded Part 201 Residential Cleanup Criteria.
Area B--Former Dewatering Lagoon Area: Analysis of the soil boring
samples collected from the former dewatering lagoon area did not detect
any organic or inorganic contaminants above background or Part 201
Residential Cleanup Criteria. The results of the soil borings and
analysis from the investigation demonstrated that the lagoons were
properly abandoned.
Area C--Former Landfill Area: Analysis of the soil boring samples
collected from the former landfill area did not detect any organic or
inorganic contaminants above background or Part 201 Residential Cleanup
Criteria. The ash, metal cans, and glass bottles in the former landfill
area were excavated during the IRA for disposal off-site. Approximately
1,855 cubic yards of material was removed from the area. Results of the
analysis of verification samples showed there were two small areas with
levels of inorganic parameters exceeding the background concentration.
An additional 40 cubic yards of soil was removed during the interim
response and disposed of off-site. No contaminants were detected above
background or Part 201 Residential Cleanup Criteria in verification
samples.
A bermed drum area was located in the south end of the former
landfill. The berm was 70 by 30 feet and contained six old, rusted
drums. These drums were removed during the IRA along with 224 cubic
feet of bluish-green stained soil found at the bottom of the bermed
area. No contaminants were detected above background or Part 201
Residential Cleanup Criteria in verification samples.
Area D--Haul Road: The results of the soil boring sampling from the
haul road indicated that the bluish-green soil found at the ground
surface along parts of the road was contaminated with heavy metals.
Analysis of the soil sample detected chromium, copper, lead, nickel,
selenium, zinc, and cyanide above their background values. Impacted
soil which was identified in the previous investigations was removed
during the IRA. An area 400 feet by 70 feet by 1.5 feet deep was
excavated, removing approximately 1,433 cubic yards of soil.
Verification samples indicated the soil that remained was not impacted
above background concentrations for heavy metals. An additional 30
cubic yards of soil was removed from the adjacent Ottawa County
property.
During an additional investigation, another 540 cubic yards of soil
was excavated from the haul road area and disposed of off-site. The
verification samples collected demonstrated that the remaining soil met
the Part 201 Residential Cleanup Criteria.
Area E--Former Drum Burial Area: Analysis of the soil boring
samples collected from the former drum burial area did not detect any
organic or inorganic contaminants above background or Part 201
Residential Cleanup Criteria.
Area F--Eastern Half of Site: The investigation of this area of
concern involved collecting two soil samples from four boring
locations. Four
[[Page 67780]]
additional borings were collected from along the eastern edge of the
area for background analysis. The results of the background borings and
the soil borings indicated no contaminants were detected above the Part
201 Residential Cleanup Criteria. No environmental hazard was found in
the eastern half of the Site.
Underground Storage Tanks (USTs): An initial review of the 1985 UST
report did not clearly indicate that the four USTs had been removed, as
a result subsequent investigations focused on finding these USTs and
determining whether there was any related contamination.
During the investigations, soil boring samples were collected from
the areas of the USTs at the northeast corner and southwest corner of
the building. The investigation also involved searching the area with
an electro-magnetic (EM) detector to determine if there were any large
metal objects buried in the area. No drums were detected; therefore, it
was concluded that all four of the USTs had been removed. The results
of these soil boring samples did not detect any petroleum hydrocarbon
or organic contaminants above Part 201 Residential Cleanup Criteria.
Groundwater: Groundwater was sampled as part of several
investigations. The results of the groundwater samples collected
upgradient of the Site were used to develop inorganic parameters
background and anthropogenic background concentrations for the area.
Background concentrations are concentrations of chemicals common to
groundwater that have not been impacted by anthropogenic effects.
Anthropogenic background levels are determined by analyzing groundwater
that has been impacted by an upgradient source such as the SWOCLF Site.
Anthropogenic background concentrations were determined from several
wells located downgradient of the SWOCLF Site, but upgradient of any
known disposal areas on the Holland Lagoons Site.
Benzene was the only organic contaminant detected in the on-site
monitoring wells above the Maximum Contaminant Levels (MCL) established
under the Safe Drinking Water Act (SDWA) and Part 201 Residential
Cleanup Criteria of 5 micrograms per liter ([micro]g/1). All of these
detections were found in wells located southwest of the Site at
concentrations ranging from 14 [micro]g/l to 28 [micro]g/1 and no on-
site source was detected. Benzene is a contaminant being monitored at
the SWOCLF Site. At the SWOCLF Site, benzene had been detected at
levels as high as 149 [micro]g/1 in purge wells and 305 [micro]g/1 in
monitoring wells; therefore, the MDEQ concluded that the source of the
benzene is the SWOCLF Site.
Inorganic contaminants found in wells on-site includes: aluminum,
arsenic, antimony, beryllium, cadmium, lead, manganese, zinc, and
vanadium. Aluminum, antimony, lead, manganese, and zinc were found in
background or anthropogenic background wells. Arsenic did not exceed
the MCL or Part 201 Residential Cleanup Criteria. Subsequent sampling
results indicated that aluminum, antimony, beryllium, cadmium, lead,
manganese, zinc, and vanadium did not exceed MCLs, Part 201 Residential
Cleanup Criteria, background and/or anthropogenic background.
In March 2005, the MDEQ and Ottawa County entered into a
Stipulation for the SWOCLF Site, under which Ottawa County is required
to perform the following remedial actions at the SWOCLF Site: construct
a new landfill cap; install and operate a new extraction well system
around the landfill; prevent the discharge to Lake Michigan of
groundwater containing hazardous substances exceeding Groundwater to
Surface Water Interface Criteria; implement reliable land and resource
use restrictions (institutional controls) to restrict construction and
use of wells within the groundwater plume; properly abandon all
existing residential wells once residents have been hooked into the
municipal water supply; and operate the then current downgradient
extraction system until it was demonstrated that requirements have been
achieved. The responsibility for the remaining wells on the Holland
Lagoons Site has been transferred to Ottawa County to use in monitoring
the SWOCLF plume.
Currently, Ottawa County has constructed the new landfill cap and
completed the hook up of residents to the municipal water supply. In
2009, Ottawa County implemented an area-wide groundwater use
restriction which prohibits human consumption of groundwater, limits
well installation/use and outlines procedures for well abandonments.
All hook ups and abandonments were completed in 2009. Ottawa County
continues to operate the downgradient extraction system. In 2009,
Ottawa County installed and began operating the new extraction well
system along the west and south boundary of the SWOCLF Site.
Former Facility Office and Maintenance Garage Building: WMMI
conducted soil and groundwater sampling below the former facility
office and maintenance garage building as noted as a recommendation in
the 2006 Five-Year Review Report. The soil and groundwater sampling
results did not reveal any chemicals of concerns above MCLs or Part 201
Residential Criteria.
Decision Summary: The Final Feasibility Study and Remedial Action
Plan Closure Report, which called for No Further Action to be
implemented at the Site was approved by MDEQ on October 13, 2008. On
May 19, 2011, the MDEQ approved WMMI's request to rescind the August
18, 1997 restrictive covenant because Ottawa County has implemented an
area-wide groundwater restriction as part of the SWOCLF cleanup
program. The Notice of Rescission of Land and/or Resources Use
Restrictions was filed and recorded by the Ottawa County Register of
Deeds on June 2, 2011. The Ottawa County Contaminated Groundwater Use
Ordinance (March 2009) meets the requirements of a ``reliable use
restriction'' under Michigan's cleanup rules (Part 201).
The rescinded restrictive covenant provided the following
restrictions at the Holland Lagoons Site: (1) Restricts the use of the
property to those uses compatible with the limited residential land use
criteria as defined in Section 20120a(1)(f) of Part 201; (2) prohibits
groundwater well installation and groundwater use within the property
boundary for all domestic, commercial, and industrial uses; (3)
prohibits the construction of groundwater fed impoundments; (4)
prohibits excavation of soil beyond the saturated zone; and (5)
requires soil sampling if existing structure is razed and 30-days
notice to MDEQ.
Selected Remedy
EPA signed a ROD on August 17, 2011 and has determined that no
further remedial action is necessary for the Holland Lagoons Site. The
remedy is protective of human health and the environment; and allows
for unlimited exposure and unrestricted use.
Response Actions
The August 2011, ``No Further Action'' ROD determined that no
further Federal response was required.
Operation and Maintenance
The groundwater underneath the Site is monitored as part of the
Ottawa County SWOCLF groundwater monitoring program and contamination
in the groundwater plumes is not related to contamination and sources
at Holland Lagoons Site. There will be no active remediation at the
Site; therefore, no operation and maintenance (O&M) is necessary.
[[Page 67781]]
Five-Year Review
The first and only five-year review, completed on September 25,
2006, found the remedy to be protective in the short-term and
identified five issues that needed to be addressed in order for the
remedy to be protective in the long-term. All of the issues have now
been addressed as described below:
1. Issue: Noncompliance with the AOC requires the completion of a
Part 201 approved Feasibility Study and Remedial Action Plan Closure
Report. Follow-Up: The MDEQ approved the Final Feasibility Study and
Remedial Action Plan Closure Report on October 13, 2008, which was
submitted by WMMI.
2. Issue: WMMI must provide information to prove the six on-site
source areas, due to the completion of past remediation activities, are
no longer contributing contaminants to the groundwater plume migrating
under the Site and that all of the contaminants found in the
groundwater plume originate from the adjacent and upgradient SWOCLF
Site. Follow-Up: The Final Feasibility Study and Remedial Action Plan
Closure Report included data to confirm that the past remediation
activities were completed at the six on-site areas and that no on-site
sources were contributing to the groundwater plume migrating onto the
Holland Lagoons Site from the SWOCLF Site.
3. Issue: Ensure that effective interim institutional controls
(ICs) are in place. Follow-Up: EPA's ``No Further Action'' ROD did not
require any additional ICs because: (1) groundwater impacts were
determined to be migrating from the SWOCLF Site and not part of site-
related contamination from Holland Lagoons and (2) an area-wide
groundwater ordinance has been implemented as part of the response at
the SWOCLF Site. As a result, the Declaration of Restrictive Covenant
has been rescinded. The Notice of Rescission of Land and/or Resources
Use Restrictions was filed and recorded by the Ottawa County Register
of Deeds on June 2, 2011. Ottawa County will continue conducting a
cleanup of the SWOCLF Site, including maintenance of an area-wide
groundwater use restriction to prevent groundwater use.
4. Issue: For the remedy to be protective in the long-term,
effective ICs may be implemented and maintained as part of the final
RAP. Follow-up: EPA's ``No Further Action'' ROD did not require ICs.
The ROD allows for unlimited use and unrestricted exposure.
5. Issue: A contamination source area may exist beneath the former
office building. Follow-up: In 2007, WMMI conducted soil and
groundwater sampling below the former facility office and maintenance
garage building. The soil and groundwater sampling results did not
reveal any chemicals of concern above the MCLs or Part 201 criteria.
In summary, EPA has determined that no further remedial action is
necessary for the Holland Lagoons Site. Previous responses at the Site
eliminated the need for a further remedial action. Contaminated soil
from on-site disposal pits was excavated and disposed of off-site. No
further five-year reviews are required because contamination has been
remediated to allow for unlimited use and unrestricted exposure.
Community Involvement
Public participation activities have been satisfied as required in
CERCLA Section 113(k), 42 U.S.C. 9613(k), and CERCLA Section 117, 42
U.S.C. 9617. Documents in the deletion docket, which EPA relied on for
recommendation of the deletion of this Site from the NPL, are available
to the public in the information repositories and at
www.regulations.gov.
Determination That the Site Meets the Criteria for Deletion in the NCP
The NCP (40 CFR 300.425(e)) states that a site may be deleted from
the NPL when no further response action is appropriate. EPA, in
consultation with the State of Michigan, has determined that the
responsible parties have implemented all response actions required, and
no further response action by responsible parties is appropriate.
V. Deletion Action
EPA, with concurrence from State of Michigan through the MDEQ, has
determined that all appropriate response actions under CERCLA have been
completed. EPA received concurrence from the State of Michigan on April
5, 2012. Therefore, EPA is deleting this Site from the NPL.
Because EPA considers this action to be noncontroversial and
routine, EPA is taking it without prior publication. This action will
be effective January 14, 2013 unless EPA receives adverse comments by
December 14, 2012. If adverse comments are received within the 30-day
public comment period, EPA will publish a timely withdrawal of this
direct final Notice of Deletion before the effective date of the
deletion, and it will not take effect. EPA will prepare a response to
comments and continue with the deletion process on the basis of the
notice of intent to delete and the comments already received. There
will be no additional opportunity to comment.
List of Subjects in 40 CFR Part 300
Environmental protection, Air pollution control, Chemicals,
Hazardous waste, Hazardous substances, Intergovernmental relations,
Penalties, Reporting and recordkeeping requirements, Superfund, Water
pollution control, and Water supply.
Dated: October 31, 2012.
Susan Hedman,
Regional Administrator, Region 5.
For the reasons set out in this document, 40 CFR part 300 is
amended as follows:
PART 300--[AMENDED]
0
1. The authority citation for part 300 continues to read as follows:
Authority: 33 U.S.C. 1321(c)(2); 42 U.S.C. 9601-9657; E.O.
12777, 56 FR 54757, 3 CFR, 1991 Comp., p. 351; E.O. 12580, 52 FR
2923; 3 CFR, 1987 Comp., p. 193.
Appendix B to Part 300 [Amended]
0
2. Table 1 of Appendix B to part 300 is amended by removing, the entry
for ``MI, Waste Management of Michigan (Holland), Holland''.
[FR Doc. 2012-27706 Filed 11-13-12; 8:45 am]
BILLING CODE P