National Oil and Hazardous Substance Pollution Contingency Plan; National Priorities List, 41625-41629 [05-14067]

Agencies

• ENVIRONMENTAL PROTECTION AGENCY

[Federal Register Volume 70, Number 138 (Wednesday, July 20, 2005)]
[Rules and Regulations]
[Pages 41625-41629]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 05-14067]


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ENVIRONMENTAL PROTECTION AGENCY

40 CFR Part 300

[FRL-7939-7]


National Oil and Hazardous Substance Pollution Contingency Plan; 
National Priorities List

AGENCY: Environmental Protection Agency.

ACTION: Direct Final Notice of Deletion of the Mallard Bay Landing Bulk 
Plant Superfund Site from the National Priorities List.

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SUMMARY: The Environmental Protection Agency (EPA) Region 6 is 
publishing a Direct Final Notice of Deletion of the Mallard Bay Landing 
Bulk Plant Superfund Site (Site), located northeast of Grand Chenier in 
Cameron Parish, Louisiana, 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 appendix B of 40 CFR part 300, which is 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 Louisiana, through the Louisiana Department 
of Environmental Quality (LDEQ), because EPA has determined that all 
appropriate response actions under CERCLA have been completed and, 
therefore, further remedial action pursuant to CERCLA is not 
appropriate.

DATES: This Direct Final Notice of Deletion will be effective September 
19, 2005, unless EPA receives adverse comments by August 19, 2005. 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: Comments may be mailed to: Beverly Negri, Community 
Involvement Coordinator, U.S. EPA Region 6 (6SF-LP), 1445 Ross Avenue, 
Dallas, TX 75202-2733, (214) 665-8157 or 1-800-533-3508 
(negri.beverly@epa.gov).
    Information Repositories: Comprehensive information about the Site 
is available for viewing and copying at the Site information 
repositories located at: U.S. EPA Region 6 Library, 12th Floor, 1445 
Ross Avenue, Suite 12D13, Dallas, Texas 75202-2733, (214) 665-6427, 
Monday through Friday 7:30 a.m. to 4:30 p.m.; Vermilion Parish Library, 
605 McMurtry Street, Gueydan, Louisiana 70542-4140, (337) 536-6781, 
Monday through Friday 10 a.m. to 5 p.m., Saturday 9 a.m. to 12 p.m.; 
Louisiana Department of Environmental Quality, Public Records Center, 
602 North Fifth Street, Baton Rouge, LA 70802, (225) 219-3168, Monday 
through Friday 8 a.m. to 4:30 p.m.

FOR FURTHER INFORMATION CONTACT: Michael A. Hebert, Remedial Project 
Manager (RPM), U.S. EPA Region 6 (6SF-LP), 1445 Ross Avenue, Dallas, TX 
75202-2733, (214) 665-8315 or 1-800-533-3508 (hebert.michael@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

    The EPA Region 6 office is publishing this Direct Final Notice of 
Deletion of the Mallard Bay Landing Bulk Plant Superfund Site from the 
NPL.
    The EPA identifies sites that appear to present a significant risk 
to public health or the environment and maintains the NPL as the list 
of those sites. As described in section 300.425(e)(3) of the NCP, sites 
deleted from the NPL remain eligible for remedial actions if conditions 
at a deleted site warrant such action.
    Because EPA considers this action to be noncontroversial and 
routine, EPA is taking it without prior publication of a notice of 
intent to delete. This action will be effective September 19, 2005, 
unless EPA receives adverse comments by August 19, 2005, on this 
document. If adverse comments are received within the 30-day public 
comment period on this document, 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. The 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.

[[Page 41626]]

    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 Mallard Bay Landing Bulk 
Plant Superfund 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

    Section 300.425(e) of the NCP provides that releases may be deleted 
from the NPL where no further response is appropriate. In making a 
determination to delete a release from the NPL, EPA shall 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 (Hazardous Substance Superfund 
Response Trust Fund) 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.
    Even if a site is deleted from the NPL, where hazardous substances, 
pollutants, or contaminants remain at the deleted site above levels 
that allow for unlimited use and unrestricted exposure, CERCLA section 
121(c), 42 U.S.C. 9621(c) requires that a subsequent review of the site 
be conducted at least every five years after the initiation of the 
remedial action at the deleted site to ensure that the action remains 
protective of public health and the environment. If new information 
becomes available which indicates a need for further action, EPA may 
initiate remedial actions. Whenever there is a significant release from 
a site deleted from the NPL, the deleted site may be restored to the 
NPL without application of the hazard ranking system. Deletion of a 
site from the NPL does not preclude eligibility for subsequent Fund-
financed or responsible party actions. If future conditions warrant, 
Section 300.425(e)(3) of the NCP provides that Fund-financed remedial 
actions may be taken at sites deleted from the NPL.

III. Deletion Procedures

    The following procedures apply to deletion of the Site:
    (1) The EPA consulted with LDEQ on the deletion of the Site from 
the NPL prior to developing this Direct Final Notice of Deletion.
    (2) LDEQ concurred with 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 published today in the ``Proposed Rules'' section of 
the Federal Register is being published in a major local newspaper of 
general circulation at or near the Site and is being distributed to 
appropriate federal, state, and local government officials and other 
interested parties; the newspaper notice announces the 30-day public 
comment period concerning the notice of intent to delete the Site from 
the NPL.
    (4) The EPA placed copies of documents supporting the deletion in 
the Site information repositories identified above.
    (5) If adverse comments are received within the 30-day public 
comment period on this document, 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 Location

    The Mallard Bay Landing Bulk Plant (MBLBP) Site is located 23 miles 
northeast of Grand Chenier in Cameron Parish, Louisiana; about 8 miles 
southwest of Gueydan in Vermillion Parish, Louisiana; and about 15 
miles south of Jennings in Jefferson Davis Parish, Louisiana. The 
geographic center of the Site is at latitude 29[deg]56'27'' north and 
longitude 92[deg]39'21'' west and the address is 2240 South Talen's 
Landing Road in Cameron Parish.

Site History

    In early 1980 through 1983, the MBLBP facility operated as a crude 
oil refinery. Mixed crude oil was refined to produce naphtha, diesel 
fuel, and No. 6 fuel oil. In August 1985, under new ownership, the 
facility resumed crude oil refining operations and continued operations 
until early 1987, when the owners filed for bankruptcy and the facility 
was closed. In 1987, the LDEQ-Hazardous Waste Division conducted a site 
inspection, in response to the bankruptcy proceedings. LDEQ noted that 
the facility had allegedly accepted hazardous waste fuels for which it 
was not permitted and had also received and attempted to process 
styrene, a compound commonly used to produce plastics.
    The facility was actively monitored by the Louisiana Department of 
Natural Resources (LDNR) and LDEQ during its operational years. Based 
on information obtained during a 1993 site inspection, LDEQ referred 
the site to EPA in June 1993. On July 30, 1996, EPA organized and 
conducted a removal assessment, which included the sampling and 
analysis of above-ground storage tanks (ASTs) and drums located on-
site, as well as an evaluation of appropriate treatment and disposal 
options. From January to March 1999, EPA oversaw the removal and off-
site disposal of approximately 866,304 gallons of oil/waste material 
from on-site ASTs. An additional 152,392 gallons of thick, sludge-like 
oil/waste material could not be removed from some ASTs due to its 
viscous consistency. Chemical analyses of this remaining tank waste 
revealed elevated concentrations of styrene, benzene, toluene, 
ethylbenzene, xylenes, 2-methylnaphthalene, naphthalene, arsenic, 
barium, chromium, copper, lead, manganese, mercury, nickel, vanadium, 
and zinc. Sediment samples collected from the wetlands adjacent to the 
area containing the tank waste revealed elevated levels of arsenic, 
barium, copper, manganese, mercury, nickel, vanadium, and zinc.
    On July 27, 2000, EPA formally announced that it was adding the 
MBLBP site to the National Priorities List (NPL), making it eligible 
for funding under EPA's Superfund program.

Remedial Investigation and Feasibility Study (RI/FS)

    From late 2000 to early 2002, EPA conducted field sampling and 
investigation activities at the MBLBP Site including collection and 
analyses of soil, sediment, surface water, ground water, waste 
materials, and asbestos-containing materials to determine if

[[Page 41627]]

significant pollutant concentrations were present. The Remedial 
Investigation (RI) and Feasability Study (FS) identified the types, 
quantities, and locations of contaminants found in these samples. The 
sample results generally indicated that the Site had been impacted by 
volatile, semi-volatile, and metal constituents commonly found at oil 
refinery facilities.

Results

     Metals and semi-volatile contamination was found in soils 
at the site and generally confined to the top 1 foot of soil.
     Ground water contamination was very intermittent across 
the site in the first water bearing zone.
     The only organics detected above screening levels were in 
the sediments within the west tank battery.
     No organics were detected in surface waters above 
screening levels.
     Metals were detected in surface water samples from the 
tank battery and treatment ponds on the west side of the Site.
     Waste materials and two above ground storage tanks 
contained high concentrations (relative to screening levels) of metals 
and organics.
     Asbestos-containing material was identified on some above 
ground piping and other process units.

Characterization of Risk

    As part of the RI/FS, EPA conducted a human health risk assessment 
(HHRA) and an ecological risk assessment (ERA). The assessments 
estimated the probability and magnitude of potential adverse human 
health and environmental effects from exposure to contaminants 
associated with the Site assuming no remedial action was taken. They 
provided the basis for taking action and identified the contaminants 
and exposure pathways that need to be addressed by the remedial action. 
A review of the analytical data obtained during the field investigation 
revealed constituents in the process sludge contained in onsite tanks, 
at hazardous concentrations. Because the hazardous sludges were thus 
established as a risk, they were excluded from the HHRA and ERA to 
prevent bias in the risk assessment of the remaining media at the Site.
    The MBLBP Site is an industrial facility in a rural area of Cameron 
Parish with predominantly undeveloped properties and other industrial 
facilities surrounding the Site. Therefore, the reasonably anticipated 
future land use for the offsite and onsite areas is industrial. 
However, to evaluate risks, should future residential development occur 
onsite, a hypothetical future residential use evaluation was also 
conducted. Based on the future residential scenario, adult and child 
residents were identified as potential receptors, and for the 
industrial scenario, adult workers were identified as potential 
receptors.
    The risk assessment indicated that hypothetical future exposures to 
ground water were predicted to result in cancer risk probabilities and 
noncancer hazards above acceptable risk levels. In addition to ground 
water exposures, hypothetical future exposures to a small area of the 
surface soil at the site were predicted to result in non-cancer hazards 
exceeding acceptable risk levels.
    The ERA focused on the on-site terrestrial habitat and the aquatic 
habitat provided by onsite holding ponds and drainage pathways leading 
offsite. No risks to aquatic receptors were identified in the 
assessment. Edible parts (fruits and leaves) of the plants as well as 
soils were determined to not be toxic to soil invertebrates, mammals, 
and birds. Therefore, there were no significant ecological risks 
identified in the ERA.

Remedial Action Objectives

    Based upon the HHRA and the ERA, the following remedial action 
objectives were developed for the site:
     Treat process sludge contained within vessels and piping 
so that it may be safely removed and properly disposed offsite, to no 
longer pose a threat to human health and the environment as a 
characteristically hazardous waste,
     Properly remove and dispose of asbestos containing 
materials,
     Isolate and remove shallow contaminated soils,
     Demolish, dispose of, or otherwise prohibit access to all 
existing buildings, piping, and tanks.

Record of Decision Findings

    The EPA signed a Record of Decision (ROD) on March 12, 2003, with 
the remedial action addressing the Site as one operable unit. The ROD 
addressed the wastes left on-site after the previous removal action as 
well as any contaminated media. The ROD selected solidification/
stabilization and off-site disposal of tank sludge and hot spot soils; 
removal and off-site disposal of asbestos-containing material; 
demolition, decontamination, and off-site disposal or recycling of 
existing on-site buildings, tanks, and piping; and removal and off-site 
disposal of stockpile wastes and drums remaining from previous 
investigations. Ground water would be monitored during remedial 
activities to assess the need for institutional controls.
    EPA determined during the design preparations of the selected 
remedy that the treatment method for sludge wastes at the Site was not 
sufficient to meet appropriate waste disposal regulations. On May 30, 
2003, TetraTech EM Inc. completed a Supplemental Feasibility Report 
describing alternative remediation disposal methods for the sludge 
wastes. A Revised Proposed Plan was issued by EPA on June 6, 2003, for 
a 30 day public comment period which provided a detailed summary and 
discussion of various remedial alternatives to address the sludge 
wastes at the Site. No members of the public were in attendance at the 
public meeting held of June 17, 2003, nor were any comments received by 
EPA from the public concerning the revised proposed plan. The LDEQ did 
submit comments related to the proposed plan and concurred with the 
preferred alternative. A ROD Amendment was signed on July 10, 2003, 
which selected excavation/extraction and off-site energy recovery/
thermal destruction as the remedial alternative to address the sludge 
wastes at the Site.

Design Criteria

    On February 21, 2003, EPA issued a work assignment to TetraTech EM 
Inc. to perform the Remedial Design (RD). The Fund-lead RD was 
completed on May 5, 2003. The project was also a Fund-lead 
construction.
    Between March 2003 and June 2003, EPA and the State (i.e., LDEQ) 
negotiated a State Superfund Contract (SSC). The SSC was reviewed 
before a final contract was signed on June 10, 2003. The first 
amendment to the SSC was signed on July 17, 2003, with a second and 
final amendment being signed on August 14, 2003. The SSC provided that 
the State pay 10% of the remedial action costs.
    The Remedial Design included the following components:
     Approximately 152,400 gallons of hazardous tank sludge 
located in aboveground storage tanks (ASTs) will be extracted and 
stabilized by adding and mixing a chemical reagent. Once the on-site 
contaminated material is stabilized and sampled to ensure Toxicity 
Characteristic Leaching Procedure (TCLP) performance standards are met, 
the mixture will be transported to an off-site landfill.
     Approximately 220 cubic yards of soil will be excavated 
from hot spot location WE04, as well as about 857 cubic yards from 
underneath the ASTs. This material will be stabilized by adding and 
mixing a chemical reagent.

[[Page 41628]]

Once the consolidated contaminated material is stabilized and sampled 
to ensure TCLP performance standards are met, the mixture will be 
transported to an off-site landfill.
     About 12,000 linear feet of aboveground and underground 
piping will be cleaned/removed/recycled off-site or cleaned and 
abandoned in-place.
     About 5,000 square feet of aboveground building structures 
will be dismantled and demolished and properly disposed or recycled 
off-site.
     All waste materials in stockpiles and drums that were left 
from previous investigations will be removed and properly disposed off-
site.
     About 1,044 tons of on-site tanks will be demolished, de-
contaminated and stored in a temporary storage area until transported 
to a scrap yard for recycling or off-site disposal.
     Approximately 210 linear feet of asbestos-containing 
material (ACM) contained on the piping and additional ACM located in 
the small heater area of the East Facility will be abated prior to the 
demolition of the facility and disposed off-site.
     Surface water located in treatment ponds on the West 
Facility will be discharged into an adjacent drainage ditch. All on-
site ponds will be partially filled with concrete stockpile recovered 
from the Site, then backfilled with soil from the earthen berms 
presently surrounding them.
     The Site will be graded and seeded with indigenous grasses 
to prevent water accumulation.
     During remedial action, efforts will be made to control 
dust to limit the amount of materials that may migrate off-site.
     Ground water will be monitored during remedial activities 
to assess the need for institutional controls.
    The RD was modified concerning the disposition of the 152,400 
gallons of hazardous tank sludge. Immediately prior to the initiation 
of the Remedial Action (RA) at the Site, it was determined that the 
sludge stabilization treatment method was not sufficient to meet 
appropriate waste disposal regulations. The revised sludge treatment 
alternative of utilizing the sludge as a supplemental fuel source at an 
off-site thermal destruction facility was the subject of the Revised 
Proposed Plan of June 6, 2003, and the ROD Amendment of July 10, 2003.

Remedial Construction Activities

    The EPA issued Remedial Action (RA) work assignment to the Response 
Action Contract (RAC) contractor on June 2, 2003, with on-site RA 
construction beginning on June 8, 2003.
    The 2003 Remedial Action at the Site included the following:
     200,150 gallons of sludge were extracted from the Site and 
utilized as a supplemental fuel source at an off-site thermal 
destruction facility.
     895 tons of on-site tanks, piping, and vessels were 
demolished, removed, decontaminated, and recycled or disposed at an 
off-site facility.
     1120 cubic yards of contaminated soil were excavated and 
disposed in an appropriate off-site landfill.
     5875 feet of 10 inch, 6 inch, and 4 inch pipe were 
demolished, cleaned out (combined with sludge wastes), and removed.
     7785 feet of 10 inch, 6 inch, and 4 inch pipe were 
evacuated and abandoned in place.
     4000 square feet of above ground buildings were 
dismantled, demolished, and disposed or recycled off-site.
     21 cubic yards of asbestos-containing material were abated 
during demolition activities.
     Surface water from on-site ponds meeting State discharge 
standards was discharged into an adjacent drainage canal.
     Ground water met all Federal and State standards, so no 
further action was needed concerning ground water at the Site.
     The Site was graded to prevent water accumulation.
    The EPA and the State of Louisiana conducted the RA as planned, and 
completed a pre-final inspection on September 8, 2003. During the 
inspection, several minor punch list items were identified, however, 
the RA activities completed according to design specifications were:
     Site preparation activities:
     Excavation and disposal of on-site contaminated soil;
     Removal and disposal of remaining waste materials;
     Treatment and discharge of surface water;
     Removal and disposal of above ground/under ground tanks;
     Removal and disposal of above ground/under ground piping;
     Removal and disposal of above ground structures;
     Removal and disposal of asbestos-containing materials;
     Analysis of confirmation samples from all excavation 
areas;
     Sampling and evaluation of ground water.
    Activities identified in the pre-final inspection included 
decontamination and return of containers utilized for fuel blending of 
the sludge waste materials, general site grading and restoration 
activities, and plugging and abandonment of on-site ground water 
monitoring wells. These activities were scheduled to be completed by 
the end of September 2003. The EPA conducted a final inspection on 
October 2, 2003, at which time all RA field activities had been 
completed.
    On August 23, 2004, EPA signed a Remedial Action Report signifying 
successful completion of construction activities. No specified reuse of 
the property has been established at this time. While there has been 
some interest in purchase of the property by local individuals/
organizations, no purchase agreements have been developed nor 
finalized.
    The remedial actions set forth in the ROD and the ROD Amendment 
were consistent with, and complied with, the Superfund Amendments and 
Reauthorization Act (SARA) of 1986, Public Law 99-499, which 
substantially amended CERCLA, 42 U.S.C. 9601 et seq., and the National 
Contingency Plan (NCP). SARA codified many of the existing requirements 
under the then existing NCP (1985), as well as adding, among other 
things, a new section 121 to CERCLA, which provided direction for 
selection of remedial actions compliant with applicable or relevant and 
appropriate Federal, State, and local laws regulations and requirements 
(Applicable or Relevant and Appropriate Requirements) 42 U.S.C. 9621.

Five-Year Review

    Upon completion of this remedy, no hazardous substances remain at 
the Site above levels that prevent unlimited use and unrestricted 
exposure. Since no additional operation and maintenance activities are 
needed, the EPA does not need to conduct a five-year review pursuant to 
CERCLA Section 121(c) and as provided in the current guidance on Five 
Year Reviews: OSWER Directive 9355.7-03B-P, Comprehensive Five-Year 
Review Guidance (June 2001).

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 from the NPL are available to the public 
in the information repositories.

V. Deletion Action

    The EPA, with concurrence of the State of Louisiana, has determined 
that all appropriate responses under CERCLA have been completed, and 
that no further response actions, under

[[Page 41629]]

CERCLA, are necessary. Therefore, EPA is deleting the 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 September 19, 2005, unless EPA receives adverse comments 
by August 19, 2005. 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. The 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, Water supply.

    Dated: July 8, 2005.
Richard E. Greene,
Regional Administrator, Region 6.

0
For the reasons set out in this document, 40 CFR part 300 is amended as 
follows:

PART 300--[AMENDED]

0
1. The authority citation for part 300 continues to read as follows:


    Authority: 33 U.S.C. 1321(c)(2); 42 U.S.C. 9601-9657; E.O. 
12777, 56 FR 54757, 3 CFR, 1991 Comp., p.351; E.O. 12580, 52 FR 
2923, 3 CFR, 1987 Comp., p.193.

Appendix B--[Amended]

0
2. Table 1 of Appendix B to Part 300 is amended under Louisiana 
(``LA'') by removing the site name ``Mallard Bay Landing Bulk Plant''.

[FR Doc. 05-14067 Filed 7-19-05; 8:45 am]
BILLING CODE 6560-50-P