The following was prepared in response to questions from groundwater
professionals concerning over-excavations (OE) conducted to address groundwater
pathways and subsequent report submittal requirements.
High risk interim monitoring occurs before operation of a remediation system.
During system operation High Risk Remediation Monitoring is conducted following
the monitoring plan provided in the CADR (which may entail sampling the same MWs
as in the Tier 2 plan, in addition to measuring other parameters, and more
frequent sampling). Once OE is conducted, remediation monitoring and reporting
follows (minimum quarterly sampling and semi-annual reporting) and groundwater
sampling events are timed based on when corrective action is implemented (i.e.,
third quarter high risk interim monitoring is no longer applicable). For
example, if OE is completed in June, sample groundwater in December.
OE is not an 'active system'. It can be done as expedited corrective action
(particularly if soil contamination is the only issue) or 'regular' corrective
action. When OE is used to address a groundwater pathway (or both soil and
groundwater pathways), we would consider follow-up monitoring to be remediation
monitoring. Groundwater may be sampled as often as you like (monthly/quarterly),
but a six-month stabilization period is typically required before data could be
used in re-evaluating risk (i.e., ignore data collected within six months post-OE).
The recommended six-month stabilization period was established with the idea of
capturing seasonal variations. Groundwater data collected sooner than six months
may be used if stabilized conditions can be documented (i.e., more frequent data
collection / sample a variety of parameters to show conditions have
equilibrated). At least two groundwater monitoring events (post-OE / 6 months
apart) are needed before site reclassification can be requested. One exception
may be for the Groundwater Vapor to Enclosed Space pathway – after a six-month
stabilization period and the first groundwater sampling event, vapor sampling
may be conducted.
An OE report with an attached revised Tier 2 which incorporates the soil
data is to be submitted within 45 days of completion of the excavation
activities under the following conditions:
- For sites where only high risk soil pathways existed and OE successfully
removed soil contamination such that the site may be reclassified.
- For sites where OE is conducted to address high risk soil pathways, but it is
not successful (i.e., soil contamination > target levels remain). The certified
groundwater professional should also attach a cover letter indicating what
future corrective actions are planned. We will then establish a CADR due date.
For cases where OE is conducted to address groundwater pathways and
is also successful in removing contaminated soil (< T.L.s), submittal of the OE
report with attached revised Tier 2 may be delayed until after the first post-OE
groundwater sampling event. The intent of waiting is to incorporate groundwater
data and to avoid multiple and unnecessary re-runs of the Tier 2 model/ report
submittals/ reviews. Note, a second post-OE groundwater sampling event is
required before the department would consider a request for site
reclassification to NAR. Generally, the earliest a reclassification request can
be made, where groundwater pathways are involved, is one year post-OE. The
request should be made through submittal of an SMR. Generally, post-excavation
groundwater data should entered into the SMR module of the Tier 2 software,
unless groundwater concentrations increase. See 1/30/02 posting for guidance on
when to enter SMR groundwater data in the Tier 2 module of the software.
Oxygen Releasing Compounds in combination with OE
Generally, use of oxygen releasing compound is not an expedited corrective
action. However, we recognize it may be an opportunistic time to apply at OE,
particularly if it’s being used as a ‘polishing off’ method or a boost to soil
remediation. In these cases you may proceed with application of oxygen releasing
compound, without the usual pre - / post - oxygen releasing compound monitoring
requirements (see below).
If oxygen releasing compound application is being considered the primary
corrective action for groundwater, and particularly when sensitive receptors are
at risk (e.g., PWLs, DWWs), a CADR would have to be submitted before the
compound is applied. A report to the department should indicate: how the
compound will be applied (slurry, injection, grid layout, etc.), at what rates,
how rates were determined, a monitoring plan (pre and post-application) which
identifies parameters to be measured - at minimum, baseline DO, CO2 (outside
contaminated area), BTEX levels, etc. This is not meant to be an all-inclusive
list (see CADR guidance). Remediation monitoring of the oxygen releasing
compound treatment is to be done quarterly with semi-annual report submittal.
Additionally, if sensitive receptors are at risk, they need to be sampled and
evaluated in the semi-annual reports. As with post-OE monitoring, at least two
sample events separated by six months (post-oxygen releasing compound
application) are needed before reclassification would be considered.
The preceding discussion is general guidance - there may be site-specific
differences. Please discuss site-specific variances with the IDNR LUST site
project manager.
Questions regarding this posting may be directed to
Elaine Douskey at (515)281-8011 or
elaine.douskey@dnr.state.ia.us