CERCLA Remedial Action Site Closure Guidance
Figure 4. Type B: Typical Long Term Cleanups for
CERCLA
Groundwater Operable Units
Contents:
III-B. Type B: Long-Term Cleanup
Type B, ‘Long-Term Cleanups,’ usually addresses cleanups
associated with ground water remediation of CERCLA
operable units. The two types of groundwater treatment are in-situ
and ex-situ. In-situ treatments allow groundwater to be treated
without being brought to the surface, which can result in significant
cost savings. In-situ treatment, however generally requires longer
time periods and there is less certainty about the uniformity of
treatment. The variability of aquifer characteristics and the difficulty
of verifying the efficacy of the process are two drawbacks with
in-situ treatment.
In-situ treatments typically involve either biological or physical/chemical
technologies. Available in-situ physical/chemical treatment technologies
include air sparging, bioslurping, directional wells, dual phase
extraction, thermal treatment, hydrofracturing, in-well air stripping,
and passive/reactive treatment walls. For example, available in-situ
biological treatment technologies include enhanced biodegradation
(nitrate and oxygen enhancement with either air sparging or hydrogen
peroxide), monitored natural attenuation, and phytoremediation of
organics. However, monitored natural attenuation is not a “technology”
per se; rather it is an approach that relies on natural processes
and monitoring. The expectation is that natural subsurface processes
such as dilution, volatilization, biodegradation, adsorption, and
chemical reactions with subsurface materials will reduce contaminant
concentrations to acceptable levels.
By contrast, ex-situ treatments generally require shorter time
periods, and there is more certainty about the uniformity of treatment
because of the ability to monitor and continuously mix the groundwater.
However, ex-situ treatments require pumping of groundwater, leading
to potential increased costs and engineering for equipment, possible
permitting, and material handling. Like in-situ treatment, ex-situ
treatments typically involve either biological or physical/chemical
technologies. For example, available ex-situ biological treatment
technologies are bioreactors and constructed wetlands. Available
ex-situ physical/chemical treatment technologies include adsorption/absorption,
advanced oxidation processes, air stripping, granulated activated
carbon/liquid phase carbon adsorption, ion exchange, precipitation/coagulation/flocculation,
separation, and sprinkler irrigation.
Regardless of the type of groundwater treatment technology employed,
the required activities for completing groundwater remedies are
the same. Figure 4 depicts the standard remedial action completion
elements for groundwater treatments. To find out more about these
requirements, simply click on the section of the process that is
of interest to you.
B.1 Remedial Action [top]
The RA
is the implementation of the remedy selected in the Record of Decision
(ROD). The RA
start date is defined as the date the contractor has mobilized and
begun substantial and continuous physical on-site remedial action,
as documented by a memo or letter to EPA.
B.2 Operating Properly and Successfully (OP&S) [top]
OP&S
activities are conducted after the physical construction of the
treatment system is complete. The purpose of OP&S
is primarily to test the treatment system. This ‘testing period’
could last up to one year. OP&S
start and finish times should be documented with EPA and the State.
No OP&S
is necessary if no waste is left on-site (Clean Closure, Type-A). The
phrase "operating properly and successfully" involves
two separate concepts. A remedial action is operating "properly"
if the treatment system is operating as designed. That same system
is operating "successfully" if its operation will achieve
the cleanup levels or performance goals (removal of contaminant)
as described in the decision document. Additionally, in order to
be successful, that remedy must be protective of human health and
the environment. For instance, an ex-situ pump and treat system
may be operating properly according to its design for pumping and
extracting so many gallons of ground water per day, but not operating
successfully because the amount of contaminant removed does not
meet the requirements as described in the ROD.
B.3 Final Inspection [top]
With any RA
construction contract, normal construction industry practice is
to conduct contract pre-final and final inspections prior to closing
out the construction contract. These inspections are conducted to
determine whether the treatment system has been completed in accordance
with the contract design and specifications. The inspections are
generally held between the contracting party (DOE) and the construction
contractor, although others can be invited (e.g., EPA).
During the contract pre-final inspection, the contracting party’s
project manager and the construction contractor inspect all elements
of work to see if the work is complete and ready for acceptance
under the terms of the contract. Some minor defects may come to
light during the inspection. The construction manager develops a
“punch list” of all items that need correction or completion
before the work can be accepted. A pre-final inspection report is
prepared, including the punch list, completion dates for outstanding
items, and a date for a final inspection.
If punch list items are minor, the pre-final inspection may automatically
serve as the final inspection. Otherwise, a final inspection is
conducted later to determine that punch list items are corrected
and all work has been completed in accordance with the contract
plans and specifications. Federal Facility Agreements (FFAs) generally
require a set of inspections to determine that all aspects of the
remedy have been implemented in accordance with applicable enforcement
documents and the ROD.
Participants for the final inspection usually include: DOE, the
State, EPA, and the DOE oversight contractor. For long-term cleanups,
the treatment system(s) must meet the OP&S
criteria.
B.4 Interim Remedial Action Report [top]
The interim report for a given operable unit is used only for remedial
actions that include ground or surface water restoration remedies,
including monitored natural attenuation. Interim reports are used
because of the long delay between construction of the treatment
facility (or ROD
signature for monitored natural attenuation) and attaining cleanup
goals as specified in the ROD.
This delay could last many years. The interim report is identical
in content to the final RA
report.
B.5 Preparing the Interim RA
Report [top]
DOE is the lead agency and as the lead agency DOE should prepare
the Interim Report in consultation with EPA and the State.
The Interim RA
Report, like the final RA
Report, usually contains ten sections and these sections should
be tailored to the site depending upon the type of remediation used.
Also, the final contract inspection for the Interim RA
Report must be completed before the report can be written and submitted
to the appropriate EPA Regional official. The sections in the Interim
Report are as follows:
B.6 Submitting the Interim RA
Report to EPA [top]
Following completion of the final contract inspection, submit the
Interim Report to the designated EPA Regional Official. The goal
is for DOE to submit the report for approval within 90 days of the
final inspection for OP&S.
When the report is received at the EPA Regional Office, EPA uses
the following criteria to approve the Interim RA
Report:
- The remedy includes ground water restoration with active treatment
(ex-situ) or monitored natural attenuation to reduce contaminant
concentrations to meet cleanup goals at some future date;
- For active treatment, all construction activities of the treatment
system are completed and the system is operating as intended (OP&S);
- For monitored natural attenuation, any necessary remedial action,
such as monitoring wells, has been constructed;
- A contract final inspection or equivalent has been conducted;
and
- The Interim RA
Report is consistent with the EPA guidance,
Close
Out Procedures for National Priorities List Sites.
B.7 Interim RA
Report Approval [top]
EPA will return the report with the signature (of the Branch Chief
or above) on the cover sheet or by letter to DOE. At the operable
unit level, EPA Headquarters does not have to review the report
or concur with the EPA Region.
Once the designated Regional EPA Official approves in writing the
Interim RA
Report, this CERCLA
milestone has been achieved. The Interim RA
Report can simply be amended (updated) to create the Final RA
Report. The Final RA
Report would include any additional information on activities since
the Interim RA
Report was completed.
B.8 Operation and Maintenance (O&M) [top]
O&M
are the activities required to maintain the effectiveness and integrity
of the remedy after OP&S.
In the case of groundwater remedies, O&M
involves operating and maintaining the groundwater containment and
restoration systems; monitoring to ensure that the remedy is performing
as expected and the environment is protected; and maintaining and
enforcing institutional controls and access restrictions.
O&M
completion is accomplished when the cleanup goals as specified in
the ROD
are achieved for groundwater restoration.
B.9 Final Remedial Action Report [top]
The Final RA
report documents the cleanup activities that took place at the operable
unit under remedial authority. In the case of long-term cleanups,
an Interim RA
Report has already been prepared; therefore, the Interim RA
Report can simply be amended to create the Final RA
Report. The amendment would add information on activities that occurred
after the Interim RA
Report was completed.
B.10 Submitting the Final RA
Report to EPA [top]
Following completion of the O&M
period, DOE submits the Final RA
Report to the designated EPA Regional Official. When the report
is received at the EPA Regional Office, EPA uses the following criteria
to approve the Report:
- All construction activities are complete, including site restoration;
- All cleanup goals as specified in the ROD
have been achieved;
- A contract final inspection or equivalent has been conducted;
and
- The RA
Report is consistent with the EPA guidance,
Close Out Procedures
for National Priorities List Sites.
B.11 Final RA
Report Approval [top]
EPA will return the report with the signature (of the Branch Chief
or above) on the cover sheet or by letter to DOE. At the operable
unit level, EPA Headquarters does not have to review the report
or concur with the EPA region.
Once the designated Regional EPA Official approves in writing the
RA
Report, this CERCLA
milestone has been accomplished.
B.12 Cleanup Goals Achieved [top]
Cleanup Goals Achieved is a milestone used for groundwater restoration,
including monitored natural attenuation remedies. These long-term
cleanup remedies have not yet achieved cleanup goals when the Interim
RA
Report is signed and the remedy transitions from the remedial action
phase into O&M.
The cleanup goals achieved milestone signals the completion of the
remedial action and is accomplished on the date the designated Regional
EPA Official approves in writing the Final RA
Report. This report should update information previously provided
in the Interim RA
Report.
B.13 Checklist For Type B – Long Term
Cleanups [top]
- Remedial Action
- Operating Properly and Successfully
- Pre-Final Inspection
- Interim RA
Report
- Preparing the Interim RA
Report
- Submitting the Interim RA
Report to EPA
- Interim RA
Report Approval
- Operation and Maintenance
- The Final RA
Report
- Submitting the Final RA
Report
- Approval of the Final RA
Report
- Cleanup Goals Achieved
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