Listed below are common problems identified during audits of QC activities and
the appropriate methodologies to be used during corrective actions at leaking
underground storage tank releases.
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ISSUE: The Notice to Impacted
Parties of Corrective Action, form
EQP3852,
and the Notice of Migration of Contamination, form EQP4482 (PDF,
Word),
are not being submitted to the STD along with proofs of receipt, for
facilities with contamination that has migrated off-site (or that is at the
property lines) above the Tier I unrestricted residential land use Risk-Based
Screening Levels (RBSLs).
RESOLUTION: STD Operational
Memorandum No. 12 states, "When a corrective action plan prepared as a result
of a release from an underground storage tank indicates impacted property
owned or operated by another person and the concentration of contamination
exceeds the Tier I unrestricted residential RBSLs, the owner or operator, or a
consultant retained by the owner or operator shall notify those persons so
impacted pursuant to subsection 21309a(3) of Part 213. Send the notice to the
impacted parties before submitting a corrective action plan with the FAR, or
before submitting the Closure Report if the FAR was not required."
The Notice of Migration of Contamination must be submitted to the appropriate
RRD district office when contamination has migrated off-site or is located at
the property boundaries. Submitting this notification is part of the property
owner's due care obligations under Section 20107a of Part 201, Environmental
Remediation, of Act 451.
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ISSUE: Reports are being
submitted with inaccurate, incomplete, or missing cover sheets. The
instructions for the report table of contents are not being followed. The QCs
are not using the most current versions of the report forms and/or are not
consecutively numbering the report pages. The QCs are marking sections of the
report as "N/A" without providing an explanation of why the sections are not
applicable.
RESOLUTION: The QC should check the DEQ web site
to verify that they have the
most current versions of the report forms. Copies of the report forms can also
be obtained by calling the RRD at 517-373-9837. During the report review
process, the QC project manager and/or the CP should verify that the report
was completed following the instructions on the report form. If the QC has any
questions concerning completing the report forms, they should contact the RRD
project manager for their facility.
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ISSUE: Closure Reports are being
submitted without attaching the applicable sections of the Initial Assessment
Report (IAR) and FAR for sites where the QC proceeds directly to site closure
without submitting an IAR or FAR.
RESOLUTION: When a facility is proceeding to closure without submitting an IAR
and/or FAR, the QC should attach the sections of the IAR and/or FAR that are
not covered in the Closure Report.
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ISSUE: The QCs are not
submitting performance monitoring (O&M) groundwater sample data until they
submit the Closure Report.
RESOLUTION: The Corrective Action Plan (CAP) should include, as part of the
performance monitoring plan, a schedule for submitting the performance
monitoring data to the RRD. The QC should submit this data to the RRD after it
has been received and reviewed. Audits of the performance monitoring data by
the RRD project managers may identify problems that can be corrected before
the RRD performs a post-closure audit.
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ISSUE: The QCs are submitting
Closure Reports based on groundwater verification samples that are two or more
years old.
RESOLUTION: When the QC project manager determines that the most recent
groundwater samples are two or more years old, the QC should resample the
appropriate monitor wells and follow the groundwater verification sampling
guidance in STD
Operational Memorandum No. 9.
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ISSUE: Models are being
submitted without the information used for the modeling calculations.
Inadequate models (e.g., groundwater fate and transport models that do not
predict the future leaching of contaminants into the groundwater from the
soils) are being submitted.
RESOLUTION: The model(s) used by the QC should be adequate to evaluate all of
the relevant contaminant migration and exposure pathways. The models should
account for any remaining source areas (e.g., UST systems, free product,
leaching from contaminated soils in the vadose zone). The QC must provide all
supporting documentation necessary for DEQ staff to evaluate the model's
predictions. Please refer to RRD
Operational Memorandum 4:
Site Characterization and Remediation Verification
(5/2/06) and its Attachment 7:
Groundwater Modeling.
Questions regarding models should be addressed to Richard Mandle, RRD at
mandler@michigan.gov
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ISSUE: The QCs performing Phase
1 site assessments routinely call the DEQ project managers asking for
information on sites and groundwater flow directions in order to avoid making
appointments to review the applicable site files under the Freedom of
Information Act, 1976 PA 442, as amended (FOIA). This may lead to
misinformation regarding the site based on the type of questions asked.
RESOLUTION: The QCs should make FOIA appointments with the appropriate DEQ
district offices to review the facility files. The QC can then contact the DEQ
project manager if he/she still has questions.
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ISSUE: The QC is not on-site at
the day or time indicated in the Notice of On-Site Work, and the project
manager is not being notified of the change in schedule.
RESOLUTION: The QC should provide at least a 48-hour notice prior to any field
activities, unless prior arrangements are made with the DEQ project manager.
The QC should provide as much advance notice as possible when fieldwork is
cancelled or postponed.
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ISSUE: The QC is not determining
the groundwater flow direction.
RESOLUTION: Whenever possible, given the hydrogeologic conditions at the
facility, the QC should determine the groundwater flow direction. Direct-push
samplers (e.g., Geoprobe) can install temporary monitor wells that can be
surveyed and used to collect static water level elevation data. If the
hydrogeologic conditions prevent determining the groundwater flow direction,
the QC should include an explanation of why the groundwater flow direction was
not determined in the IAR, FAR, and Closure Report.
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ISSUE: The QC is not estimating
the depth to groundwater for sites where the soil contamination does not
extend to the groundwater. Section 10.2.2 (page 49) in the
General Guidance for Evaluating and
Characterizing Petroleum Releases
was amended to address this
issue. In permeable soils, petroleum can migrate vertically down to the
groundwater without leaving residual soil contamination in the vadose zone
above the Tier I soil leaching to groundwater exposure pathway RBSLs.
RESOLUTION: When permeable soils underlie the source of the release, the QC
should investigate the vertical extent of the soil contamination until an
unimpacted confining layer or groundwater is encountered. Monitor well logs
from nearby sites of environmental contamination or nearby water supply well
logs can be used as supplemental documentation of the depth to groundwater.
The QC should justify any decision not to investigate down to the groundwater
in the IAR, FAR, and Closure Report. The QC should address any questions
concerning determining the vertical extent of the contamination to the DEQ
project manager or geologist.
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ISSUE: The QC is not following
Operational Memorandum No. 13
and/or is not providing an
adequate justification of the use of natural attenuation as a corrective
action.
RESOLUTION: The FAR should include a Risk-Based Corrective Action (RBCA)
assessment and feasibility study that justifies the selection of natural
attenuation as the corrective action. When the RRD project manager audits the
FAR, he/she needs to determine if natural attenuation will be effective and
whether there will be any unacceptable exposures before natural attenuation
addresses the contamination. The CAP should include a performance monitoring
plan, including a contingency plan if natural attenuation is ineffective, that
follows the guidelines in
Operational Memorandum No. 13.
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ISSUE: The QC is not
aggressively recovering free product at facilities with extensive free
product.
RESOLUTION: The QC needs to promptly determine the horizontal extent of the
free product, the apparent free product thickness in the monitor wells, the
volume of free product recovered from the monitor wells, and the recharge rate
for the free product into the monitor wells. The QC will use this information
to design an appropriate free product recovery system. When there is an
extensive volume of free product entering the monitor wells, the QC needs to
design and implement an aggressive free product recovery system. Hand bailing
and passive recovery devices will not be adequate. The QC should evaluate the
need for a continuous recovery system to maximize the free product recovery.
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ISSUE: The QC is not conducting
adequate hydrogeological investigations, especially at facilities with complex
hydrogeologies.
RESOLUTION: An adequate site characterization is critical to making a RBCA
assessment, and for designing and implementing effective corrective actions.
This includes determining the horizontal and vertical extent of the
contamination, including off-site properties. Sites with complex hydrogeology
will require more thorough characterization to identify all of the contaminant
migration and exposure pathways. The hydrogeology may affect which corrective
action alternatives are selected.
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ISSUE: The QCs are incorrectly
classifying facilities as Class 3 or 4 sites when they are Class 1 or 2 sites.
The QCs are reclassifying Class 1 sites without documenting that free product
has not been present for at least six months.
RESOLUTION: The QC needs to assess all relevant exposure pathways in
classifying sites. The QC should follow the guidelines in
RRD Operational Memorandum No. 1 and
RRD Operational Memorandum 3:
Part 213 Site Classification. The
QC cannot reclassify a Class 1 site that formerly had free product until six
consecutive monthly inspections document the absence of free product.
Questions regarding the site classification should be addressed to the RRD
project manager.
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ISSUE: The text in the Closure
Report does not explain which exposure pathways are relevant and which cleanup
criteria are being used. The Closure Report does not explain why more
restrictive exposure pathways are eliminated.
RESOLUTION: The Closure Report text should clearly explain which exposure
pathways are relevant and which cleanup criteria are being used. The QC should
justify the elimination of exposure pathways and cleanup criteria that are not
relevant.
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ISSUE: The QCs are using the
indoor air inhalation RBSLs when the site conditions do not fit the generic
assumptions that were used to calculate the RBSLs. Examples of this are
facilities with shallow groundwater, free product, and/or soils that exceed
the soil saturation (CSAT) exposure pathway RBSLs.
RESOLUTION: The assumptions used to develop the indoor air inhalation exposure
pathway RBSLs do not apply when there is a shallow water table, free product
is present, or the soil contamination exceeds the CSAT exposure
pathway RBSLs or site-specific target levels. Please refer to Addendum
to STD Op Memo 4 Attach 8: Acceptable Indoor Air Concentrations
for further guidance.