[Federal Register Volume 74, Number 128 (Tuesday, July 7, 2009)]
[Rules and Regulations]
[Pages 32084-32088]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: E9-15801]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 300
[EPA-HQ-SFUND-2009-0146; FRL-8926-1]
National Oil and Hazardous Substances Pollution Contingency Plan;
National Priorities List
AGENCY: Environmental Protection Agency (EPA).
ACTION: Direct Final Notice of Deletion of the Wilson Farm Superfund
Site (Site) from the National Priorities List.
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SUMMARY: EPA, Region 2, is publishing a direct final notice of deletion
of the Site, located in Plumsted Township, Ocean County, New Jersey,
from the National Priorities List (NPL). The NPL, promulgated pursuant
to section 105 of the Comprehensive Environmental Response,
Compensation, and Liability Act (CERCLA) of 1980, as amended, is an
appendix of the National Oil and Hazardous Substances Pollution
Contingency Plan (NCP). This direct final Notice of Deletion is being
published by EPA with the concurrence of the State of New Jersey,
through the Department of Environmental Protection (NJDEP). EPA and
NJDEP have determined that all appropriate remedial actions under
CERCLA, including operation and maintenance, have been implemented.
DATES: This direct final deletion will be effective September 8, 2009
unless EPA receives significant adverse comments by August 6, 2009. If
significant adverse comments are received, EPA will publish a timely
withdrawal of this 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-2009-0146, by one of the following methods:
Web Site: http://www.regulations.gov. Follow the on-line
instructions for submitting comments.
E-mail: [email protected].
Fax: To the attention of Michael Zeolla at (212) 637-4393.
Mail: To the attention of Michael Zeolla, Remedial Project Manager,
Emergency and Remedial Response Division, U.S. Environmental Protection
Agency, Region 2, 290 Broadway, 19th Floor, New York, New York 10007-
1866.
Hand Delivery: Superfund Records Center, 290 Broadway, 18th Floor,
New York, NY 10007-1866 (telephone: 212-637-4308). Such deliveries are
only accepted during the Docket's normal hours of operation (Monday to
Friday from 9 a.m. to 5 p.m.). Special arrangements should be made for
deliveries of boxed information.
Instructions: Direct your comments to Docket ID no. EPA-HQ-SFUND-
2009-0146; EPA' policy is that all comments received will be included
in the Docket without change and may be made available online at http://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 CBI
or otherwise protected through http://www.regulations.gov or via e-
mail. The http://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 comments. If you
send comments to EPA via e-mail, your e-mail address will be included
as part of the comment that is placed in the Docket and made available
on the Web Site. If you submit electronic comments, EPA recommends that
you include your name and other contact information in the body of your
comment and with any disk or CD-ROM that 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 comments.
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 http://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 can be available either
electronically in http://www.regulations.gov or in hard copy at:
[[Page 32085]]
U.S. Environmental Protection Agency, Region 2, Superfund Records
Center, 290 Broadway, 18th Floor, New York, NY 10007-1866, Phone: (212)
637-4308, Hours: Monday to Friday from 9 a.m. to 5 p.m., and
New Jersey Department of Environmental Protection, 401 East State
Street, Trenton, New Jersey 08625-0410, Phone: 609-777-3373.
FOR FURTHER INFORMATION CONTACT: Michael Zeolla, Remedial Project
Manager, Emergency and Remedial Response Division, U.S. Environmental
Protection Agency, Region 2, 290 Broadway, 19th Floor, New York, New
York 10007-1866, telephone at (212) 637-4376; fax at (212) 637-4393; or
e-mail at: [email protected].
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Introduction
II. NPL Deletion Criteria
III. Deletion Procedures
IV. Basis for Intended Site Deletion
V. Deletion Action
I. Introduction
EPA Region 2 is publishing this direct final notice of deletion of
the Wilson Farm Superfund Site (Site) from the National Priorities List
(NPL). The NPL constitutes Appendix B of 40 CFR part 300, which is the
Oil and Hazardous Substances Pollution Contingency Plan (NCP), which
EPA promulgated pursuant to section 105 of the Comprehensive
Environmental Response, Compensation and Liability Act (CERCLA) of
1980, as amended. EPA maintains the NPL as the list of sites that
appear to present a significant risk to public health, welfare, or the
environment. Sites on the NPL may be the subject of remedial actions
financed by the Hazardous Substance Superfund (Fund). As described in
300.425(e)(3) of the NCP, a site deleted from the NPL remains eligible
for remedial actions if conditions at the site warrant such action.
Because EPA considers this action to be noncontroversial and
routine, this action will be effective September 8, 2009 unless EPA
receives significant adverse comments by August 6, 2009. Along with
this direct final Notice of Deletion, EPA is co-publishing the Notice
of Intent to Delete in the ``Proposed Rule'' section of today's 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 Site and demonstrates how it
meets the deletion criteria. Section V discusses EPA's action to delete
the Site from the NPL unless significant 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 parties have implemented all
appropriate response actions required;
ii. All appropriate Fund-financed responses under CERCLA have been
implemented, and no further 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,
implementing remedial measures is not appropriate.
III. Deletion Procedures
The following procedures apply to deletion of this Site.
(1) EPA consulted with the State of New Jersey 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 of New Jersey thirty (30) working
days for review of this notice and the parallel Notice of Intent to
Delete prior to their publication today, and the State of New Jersey,
through the NJDEP, 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
Ocean County Observer. 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. If appropriate,
EPA may then continue with the deletion process based on 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 summary provides the Agency's rationale for the
proposal to delete this Site from the NPL.
Site Background and History
The Site consists of 10 acres within a 218-acre property and is
located one-quarter mile southwest from the intersection of State
Highway Route 528 (New Egypt-Lakewood Road) and Hawkin Road (State
Highway Route 640) in Plumsted Township, Ocean County, New Jersey. The
Site is situated in a predominantly rural area with some residential
homes to the south. The 10-acre site, bordered on the north side by
cultivated land which is part of the Wilson Farm property, is wooded
and unoccupied. A dirt road runs through the center of the Site, which
allows access into the property from Hawkin Road. The Site has a number
of unimproved roadways in and around it and is used mainly for hunting.
Colliers Mills Wildlife Management Area is east of the Site and
consists of forested undeveloped property that runs north and south
along Hawkin Road. Borden Run Creek runs west and south of the site and
flows into Colliers Mills Lake. At the northern edge of the Site
towards New Egypt/Lakewood Road is an active farm field and beyond that
a small residential neighborhood. The Site is
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located within the boundaries of a national reserve known as the
``Pinelands.'' The Pinelands reserve is separated into ``Management
Areas.''
The Wilson Farm property was one of seven sites used to dispose of
liquid and drummed chemical waste from the Thiokol Corporation facility
during the 1960's and early 1970's. The property on which the Site is
located is privately owned and has been posted with ``No Trespassing
Signs.''
The Site was inspected by the Ocean County Health Department and
New Jersey Department of Environmental Protection (NJDEP) in February
1980, which led to the implementation of an Immediate Removal Action in
September 1980. Approximately 620 cubic yards of mixed chemical waste
material and soils were removed from the Site. Prior to the Immediate
Removal Action, NJDEP had installed and sampled six groundwater
monitoring wells in July 1980. Groundwater from these monitoring wells
was found to contain chemical contamination.
In December 1982, the NJDEP scored the Site utilizing the Hazard
Ranking System. Based on this ranking, the Site was added to the NPL on
September 21, 1984 (FRL-2646-2).
In 1986, the NJDEP established a Well Restriction Area (WRA) on the
Site and surrounding properties in order to protect any new drinking
water wells which might be installed near the Site. The WRA required
that all new wells within approximately a 2,000-foot radius of the Site
be installed to a depth of at least 150 feet. The purpose of this
action was to ensure that new wells were not impacted by contamination
in the shallow aquifer.
Remedial Investigation and Feasibility Study (RI/FS)
In July 1986, the NJDEP directed Morton Thiokol Inc. (Thiokol
merged with Morton Norwich Corporation) to make payments to the NJDEP
for the cost of conducting a Remedial Investigation and Feasibility
Study (RI/FS) at the Site. On December 3, 1987, the NJDEP and Morton
Thiokol Inc. (MTI) entered into an Administrative Consent Order (ACO)
in which MTI agreed to comply with this Directive (Directive No. 1).
In January 1987, Acres International Corporation (Acres) was
contracted by the NJDEP to perform the RI/FS. After initial site
investigations were performed, NJDEP determined that further remedial
studies were necessary. In January 1990, the NJDEP directed Morton
International Incorporated (MII) and the Thiokol Corporation (after
Directive No. 1 was issued, MTI split into MII and Thiokol) to pay for
the additional studies. MII complied and the RI/FS was completed by
Acres in March 1992.
The RI/FS identified that approximately six to twelve cubic yards
of industrial waste, including a black rubbery tar-like substance and
miscellaneous laboratory glassware, to a depth of six inches, still
remained at the Site. No buried waste was encountered. The RI/FS found
that this waste did not present a risk to human health or the
environment.
On August 23, 1991, the NJDEP and MII entered into a second ACO for
the removal of the remaining contaminated surface waste materials at
the Site. MII prepared and submitted an Interim Removal Action Plan to
the NJDEP and EPA in October 1991. The final removal activities were
agreed to between NJDEP and MII in May 1992.
The surficial waste removal activities were conducted at the Site
between June and July 1992. Approximately 645 cubic yards of waste/soil
material was removed and transported for treatment and disposal to a
federally permitted hazardous waste landfill. A comparison of the post-
excavation soil sample analytical results to the NJDEP proposed cleanup
goals for residential surface soils confirmed the effectiveness of the
removal work. In October 1993, MII restored all areas disturbed by the
removal activities through back-filling and grading soils and re-
vegetating. A final surficial waste removal report was submitted by MII
in February 1994.
After completing the Interim Removal Action, EPA conducted a
baseline risk assessment to evaluate the potential risks to human
health and the environment for residual contaminants in the soil,
groundwater, surface water and sediments. EPA issued the final Risk
Assessment Report on May 3, 1993.
Selected Remedy
Based on this Risk Assessment Report, EPA concurred on a ``No
Further Action'' Record of Decision (ROD) which was issued by NJDEP on
August 2, 1993. The selected remedy included implementing a
groundwater, surface water and sediment monitoring program for five
years to ensure that any residual contamination remained below levels
of concern and confirmed the no action determination. Visual inspection
of the Site during monitoring was also conducted to ensure that no
further waste materials were present. Lastly, the ROD called for
continuation of the WRA for a minimum of five years to ensure the
protection of area drinking water supplies.
Response Action
Pursuant to the remedy selected in the ROD, MII and the NJDEP
entered into a Memorandum of Agreement (MOA) on August 25, 1994, to
perform post-remediation monitoring activities. A Post-Remediation
Monitoring Work Plan was submitted by MII in October 1994. A final
post-remediation monitoring work plan was approved in January 1995.
The five years of monitoring, as outlined in the ROD, began in May
1995 with the first quarterly sampling event and continued until
September 1999. The monitoring consisted of collecting samples at ten
monitoring wells and three surface water and sediment locations on a
quarterly basis in the first year and on an annual basis in 1996, 1997,
1998 and 1999. During each sample event, the Site was inspected for any
evidence of remaining surface waste material that would then be
removed.
After five years of monitoring, site contaminants remained below
Federal Maximum Contaminant Levels (MCLs). Since the Site is located in
New Jersey's Pinelands Protection Area, the aquifer is classified by
the NJDEP as Class I-PL under its Groundwater Quality Criteria
Standards (GWQS). Class I-PL standards are defined as the higher of the
Practical Quantitative Levels (PQLs) or background levels. NJDEP
requires groundwater sample results to indicate concentrations are
below the PQL. The GWQS establish anti-degradation policies that are
designed to protect the existing and designated uses of the State of
New Jersey ground waters and are not considered health-based Federal
MCLs.
A review of the post-remediation monitoring results revealed that
lead in MW-5S, and chloroform in MW-8S were present above the PQLs for
all sampling events. Lead concentrations were detected above the PQL of
10 ppb (5 ppb is now the current standard) in MW-5S and ranged from
14.5 ppb (2nd sample event) to 94.9 ppb (6th sample event). Chloroform
concentrations were detected above the PQL of 1 ppb and ranged from 1.2
ppb (7th sample event) to 6.2 ppb (2nd sample event). Due to these
groundwater concentrations above the PQL, NJDEP recommended that Rohm
and Haas (which acquired MII) conduct additional investigative
activities including soil and groundwater sampling around MW-5S and MW-
8S for lead and chloroform, respectively.
A Supplemental Groundwater Investigation (SGI) was conducted by
ENSR (on behalf of the Rohm and Hass Company which acquired MII) in
October 2004. The SGI consisted of
[[Page 32087]]
collecting sixteen subsurface soil samples around MW-5S and MW-8S, four
groundwater samples from temporary wells MW-5S-5, MW-5S-6, MW-8S-2 and
MW-8S-4, and four surface water and sediments samples in Borden Run
Creek. The results of sampling found non-detect levels of Site
contaminants in the surface water, sediments and soils. In a March 18,
2005 letter, NJDEP concluded that no further monitoring of the Site
surface water, sediments or soils was required but recommended that a
Classification Exemption Area (CEA) be proposed for the Site
groundwater. The SGI results are summarized as follows:
(1) Subsurface soil samples collected from the area around MW-5S
(for lead) and MW-8S (for chloroform) did not have lead or chloroform
detected above the New Jersey Residential Direct Contact, Non-
Residential Direct Contact or the Impact to Groundwater Soil Cleanup
Criteria. The data also found field screening results showing no
detectable concentrations of lead and chloroform are present in soils.
NJDEP concluded that the subsurface soil data for the area around MW-5S
and MW-8S indicate that the soils are not impacted and a no further
action for the soils is appropriate;
(2) Groundwater samples collected from MW-5S-5 and MW-5S-6 (for
total and dissolved lead analysis), and MW-8S-2 and MW-8S-4 (for
chloroform analysis) found no detectable levels of lead above the
method detection limit or chloroform above the GWQS of 6 ppb, and
neither above the Federal MCLs. Chloroform did, however, exceed the PQL
criteria of 1 ppb at three locations (MW-8S-2, MW-8S-4, and MW-8S-4D);
(3) Surface water samples collected found that chloroform, toluene,
lead and zinc did not exceed the NJDEP Surface Water Quality Standards
(SWQS) or EPA National Ambient Water Quality Criteria (NAWQC). However,
zinc concentrations were found slightly above the background levels;
and
(4) Sediment sample-analyses did not detect chloroform or toluene
above the analytical detection limits. However, the detection limits
were above the NJDEP Guidance for Sediment Quality Evaluations (SQE)
and EPA Region 5 Ecological Screening Levels (ESLs). NJDEP believes
that neither toluene nor chloroform is problematic in sediments. Lead
and zinc concentrations did not exceed the SQE and ESLs but were
detected above the background level at the two most down gradient
sediment locations.
NJDEP's review of the current and historical surface water and
sediment data concluded that additional sampling is not necessary and
no further action for this area of concern is appropriate.
In December 2005 and November 2006, ENSR re-sampled MW-5S and MW-
8S. The analytical results indicated that lead and chloroform
concentrations continued to be above the Class I-PL groundwater
standards (or PQL). Because of the historical concentrations of lead in
MW-5S and chloroform in MW-8S exceeding the PQL, NJDEP requested that
Rohm and Haas propose a CEA at the Site.
Institutional Controls
At the time of the ROD, a WRA was in place and recognized by the
ROD as a temporary measure along with continued monitoring for five
years. NJDEP indicates that the WRA is still in place. Since the
groundwater currently meets federal and state standards for public
consumption, it does not appear that the WRA provides any specific
purpose at the Site.
Although not required by the 1993 ROD remedy, the NJDEP required
the institution of a CEA at the Site due to limited groundwater
contaminant levels continuing to exceed PQLs. The CEA was submitted in
October 2006. As part of the CEA requirements, Rohm and Hass proposed
several actions to reduce the length of time the CEA would remain in
effect. Those actions included installing a replacement well that would
evaluate the possibility that the elevated lead concentrations were an
artifact of some unexpected problem at MW-5S and performing a one-day
high vacuum groundwater extraction in order to remove chloroform
impacted groundwater and soil vapors from MW-8S.
ENSR replaced MW-5S with MW-5R and performed the high vacuum
groundwater extraction at MW-8S on May 7, 2007. MW-5S was
decommissioned. Following these field activities, ENSR collected
groundwater samples from MW-5R and MW-8S on June 6 and September 5,
2007. The results indicate that lead concentrations in MW-5R were no
longer detected but the chloroform concentrations in MW-8S continue to
exceed the PQL but not the MCL. Based on these results, the NJDEP
issued a no further action for lead at MW-5R on April 13, 2008, and
requested that the CEA be revised for chloroform at MW-8S. Rohm and
Haas will continue to monitor MW-8S until chloroform is not detected at
concentrations above the PQL for two consecutive quarterly sampling
events.
NJDEP has accepted the Rohm and Hass proposal of no further action
with a CEA for chloroform at MW-8S, without the need of a WRA
designation. Rohm and Haas submitted the final revised CEA proposal in
January 2009. Once approved by the NJDEP, the CEA will continue until
chloroform is below the PQL for two consecutive quarterly sampling
events. The NJDEP will issue a no further action for chloroform at MW-
8S when two consecutive quarterly sampling events results in chloroform
detection below the PQL concentration.
Since contaminant levels in all media are below risk based levels,
no institutional controls are required at this Site under CERCLA.
Cleanup Goals
Post-excavation sampling conducted as part of the removal actions
verifies that the Site soils were below the NJDEP cleanup standards for
residential properties. Groundwater CERCLA cleanup standards were
Federal Maximum Contaminant Level (MCL) and Maximum Contaminant Level
Goal (MCLG).
Operations and Maintenance
No operation and maintenance was required for the Site property,
where mixed surface waste and contaminated soils were removed for off-
site disposal, and post-excavation sampling confirmed that remediation
goals were achieved. Post-remediation groundwater monitoring was
conducted for five years and all contaminants are below MCLs.
Five-Year Review
There were two five-year reviews of the selected remedy for this
Site. The first review was issued on May 12, 2000. A second five-year
review was signed on June 3, 2005. The June 2005 Five-Year Review
Report found that the no further action remedy protects human health
and the environment at this Site. It indicates that no future five-year
reviews will be necessary if the Site is found to be suitable for
unlimited use without restriction and that finding is part of the
deletion process or is contained within an appropriate EPA decision
document. The deletion process has determined that the Site is suitable
for unlimited use without restriction. Therefore, no future five-year
reviews will be conducted at this Site.
Community Involvement
Public participation activities for this Site have been satisfied
as required in CERCLA sections 113(k) and 117, 42 U.S.C. 9613(k) and
9617. Throughout the removal and remedial process, EPA and the NJDEP
have kept the public informed of the activities being conducted at the
Site by way of public
[[Page 32088]]
meetings, progress fact sheets, and the announcement through local
newspaper advertisement on the availability of documents such as the
RI/FS, Risk Assessment, ROD, Proposed Plan and Five-Year Reviews.
Notices associated with these community relations activities were also
mailed out to the area residents and other concerned parties on the
mailing list for the Site.
Determination That the Site Meets the Criteria for Deletion From the
NCP
The NCP specifies that EPA may delete a site from the NPL if ``all
appropriate Fund-financed response under CERCLA has been implemented,
and no further response action by responsible parties is appropriate.''
40 CFR 300.425(e)(1)(ii). EPA, with the concurrence from the State of
New Jersey, through NJDEP, believes that this criterion for deletion
has been met and the Site is available for use without restriction.
Consequently, EPA is deleting this Site from the NPL. Documents
supporting this action are available in the Site files.
V. Deletion Action
EPA, with the concurrence of the State of New Jersey, has
determined that all appropriate Fund-financed responses under CERCLA
have been implemented, and no further action by responsible parties is
appropriate. Therefore, EPA is deleting the Site from the NPL.
Because EPA considers this action to be noncontroversial and
routine, EPA is deleting the Site without prior publication. This
action will be effective September 8, 2009 unless EPA receives adverse
comments by August 6, 2009. If adverse comments are received within the
30-day public comment period of this action, EPA will publish a timely
withdrawal of this Direct Final Deletion before the effective date of
the deletion and the deletion will not take effect. EPA will, if
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 received. In such a case, there will be no additional
opportunity to comment.
List of Subjects in 40 CFR Part 300
Environmental protection, Air pollution control, Chemicals,
Hazardous substances, Hazardous waste, Intergovernmental relations,
Penalties, Reporting and recordkeeping requirements, Superfund, Water
pollution control, Water supply.
Dated: June 25, 2009.
George Pavlou,
Acting Regional Administrator, Region 2.
0
For the reasons set out in the preamble Part 300 Title 40 of Chapter I
of the Code of Federal Regulations is amended as follows:
PART 300--[AMENDED]
0
1. The authority citation for Part 300 continues to read as follows:
Authority: 33 U.S.C. 1321(c)(2); 42 U.S.C. 9601-9657; E.O.
12777, 56 FR 54757, 3 CFR, 1991 Comp., p. 351; E.O. 12580, 52 FR
2923, 3 CFR, 1987 Comp., p. 193.
Appendix B--[Amended]
0
2. Table 1 of Appendix B to part 300 is amended by removing ``Wilson
Farm, Plumsted Township, NJ.''
[FR Doc. E9-15801 Filed 7-6-09; 8:45 am]
BILLING CODE 6560-50-P