HomeMy WebLinkAboutDSHW-2018-012119 - 0901a06880957dbbATK Launch Systems Inc. – Promontory July 2, 2018 Post Closure Permit UTD009081357
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MODULE IV - GROUNDWATER MONITORING
IV.A. POST-CLOSURE GROUNDWATER MONITORING
IV.A.1. Hazardous constituents have been released from the M-136 LTTAs, the M-508
Photographic Waste Discharge Site and other waste management sites at the facility.
The Permittee shall monitor groundwater in the impacted aquifers as described in this Module and Attachment 3. The Permittee shall maintain compliance with R315-264-90 Groundwater Protection during the post-closure care period as defined
in Condition IV.A.6.
IV.A.2. The Permittee shall maintain a groundwater monitoring system. The monitoring
well system consists of all wells dedicated to monitoring the release of hazardous constituents from M-136, M-508 and other waste management sites at the facility. The monitoring well system shall consist of the wells, piezometers and springs
specified in Table 4-A of Attachment 4. The monitoring well, piezometer and
spring locations are also presented in Attachment 4, Plates 1A and 1B.
IV.A.3. The Area of Compliance is defined as all monitoring wells, piezometers and springs located within impacted aquifers and displaying concentrations that exceed the Groundwater Protection Standard as defined in section IV.C. of this Permit module.
IV.A.4. The Permittee shall implement the corrective action program, as described in
Module V, upon exceedance of the Groundwater Protection Standard within the
Area of Compliance.
IV.A.5. Solid waste management units (SWMUs) may be subject to certain provisions of
this Module. The Director shall determine which SWMUs may be subject to
some or all of the provisions of this Module.
IV.A.6. The Permittee shall monitor the groundwater throughout the post-closure care period. If any of the Groundwater Protection Standards, or approved Alternate
Concentration Limits, are still exceeded after thirty (30) years, the Permittee shall
continue corrective action as specified in Condition V.F.
IV.A.7. The Permittee shall maintain a searchable data base so that a complete record of the
chemical and well specific groundwater monitoring data, collected in accordance with this Module, is available.
IV.B. REQUIRED PROGRAM
IV.B.1. The Permittee shall monitor groundwater, in accordance with Section IV.B., for the
hazardous constituents listed below in Table IV-1.
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IV.B.1.a. The groundwater quality assessment, completed by the Permittee, determined the
hazardous constituents listed in Table IV-1 below were released at the site, entered the impacted aquifer, and have been detected beyond the compliance point. Some constituents have been detected beyond the facility boundary. The Permittee shall
monitor the groundwater for the constituents listed in Table IV-1 as specified in the
Sampling and Analysis Plan, Attachment 3.
TABLE IV-1 CONSTITUENTS AND GROUNDWATER PROTECTION STANDARD
Constituent GWPS (ug/L) Constituent GWPS (ug/L)
1,1-Dichloroethene 7.0 1 Trans-1,2-dichloroethene 100 1
1,1-Dichloroethane 2.82 Trichloroethene 5.0 1
1,2-Dichloroethane 5.0 1 Trichlorofluoromethane 5,200 2
1,1,1-Trichloroethane 200 1 Vinyl Chloride 2.0 1
1,1,2-Trichloroethane 5.0 1 Xylene 10,000 1
Acetone 14,000 2 Arsenic 10 1
Benzene 5.0 1 Barium 2,000 1
Carbon Tetrachloride 5.0 1 Beryllium 4.0 1
Chlorobenzene 100 1 Chromium (total) 1001
Chloroform 802,3 Chromium VI 0.0352
Cis-1,2-Dichloroethene 70 1 Cobalt 62
Methyl Ethyl Ketone
(2-Butanone) 5,6002 Molybdenum 1002
Methylene Chloride 5 1 Perchlorate 142
Tetrachloroethene 5.0 1 Nitrate 10,000 1
Toluene 1,000 1 RDX 0.72
HMX 1,0002
1 Maximum Contaminant Levels (MCLs), EPA, 2017
2 EPA Regional Screening Levels (RSLs) for Tapwater, June 2017
3 The MCL for chloroform applies to the Total Trihalomethanes, which also include
bromodichloromethane, bromoform, and dibromochloromethane
IV.B.2. The Permittee shall collect and analyze samples from the groundwater monitoring system at least annually as described below:
IV.B.2.a. Thirty (30) days prior to the collection of samples, the Permittee shall submit an
annual Groundwater Monitoring Plan to the Director for approval. The monitoring
plan shall include a list of monitoring wells and springs proposed for sampling, the
constituents that will be sampled for in each well, a map highlighting the well locations, and the rationale for the proposed well selections and constituents.
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IV.B.2.b. The Permittee shall collect and analyze samples from Shotgun and Pipe Springs
semiannually, once in the Spring and once in the Fall. The Permittee shall submit the analytical results for spring samples collected in the Fall with the Annual Groundwater Monitoring Report (Condition IV.E.2). The results for the spring
samples collected in the Spring shall be submitted to the Director in writing by the
Permittee within ninety (90) days of collecting the samples.
IV.B.3. The Permittee shall not implement the proposed Groundwater Monitoring Plan without Director written approval. The Director may, upon written notification to the Permittee, require any or all of the monitoring wells, springs or piezometers
listed in Table 1 of Attachment 4 be sampled for any or all of the constituents listed
in Table IV-1.
IV.C. GROUNDWATER PROTECTION STANDARD IV.C.1. The concentrations listed for each hazardous waste constituent in Table
IV-1 shall comprise the groundwater protection standard. The Permittee shall
sample and analyze the groundwater monitoring system for these constituents, as
described in Condition IV.B.
IV.C.2. The Permittee may apply for Alternate Concentration Limits (ACL). A petition may be submitted if:
IV.C.2.a. The approved corrective measures, as described in Modules V and VI, fail to meet
the groundwater protection standard defined by Condition IV.C.1., (Table IV-1) and
the Permittee has demonstrated that all other technically feasible methods have been
used to meet the concentration limits, or IV.C.2.b. A risk assessment, conducted in accordance with R315-101, concludes that a
contaminant concentration greater than the groundwater protection standard poses
no unacceptable risk to human health or the environment.
IV.C.3. If submitted, the Director shall determine, the appropriateness of any ACL petition, and either accept, or reject, the proposed concentration level. If the Director determines that the level is appropriate, the Permittee shall initiate a modification to
the permit in accordance with Condition I.E.2.
IV.C.4. The Permittee may request to have one or more constituents removed from the
groundwater monitoring constituent list (Table IV-1). The Director shall determine if it is appropriate to remove constituent(s), based on the rationale provided by the Permittee and monitoring results. If the Director determines that it is appropriate to
remove constituents as requested, the Permittee shall initiate a modification to the
permit in accordance with Condition I.E.2.
IV.C.5. The Permittee shall use the SW-846 test methods and detection limits listed in
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Table 1 of Attachment 3 to analyze groundwater samples. If an alternate test
method is proposed, the Permittee shall request a permit modification in accordance with Condition I.E.2. If, at any time during the duration of this permit, the Director determines that the test methods specified in Attachment 3 are not sensitive enough
to produce the required results, the Director may require the Permittee to use
alternate test methods. If the Director requires a change to the test method(s), the
Permittee shall modify the permit.
IV.D. GROUNDWATER MONITORING REQUIREMENTS
IV.D.1 The Permittee shall comply with the following general requirements for
groundwater monitoring:
IV.D.1.a. The groundwater monitoring system shall consist of the wells, piezometers and springs specified in Table 1 of Attachment 4.
IV.D.1.b. Existing monitoring wells shall be maintained in a fully operational condition for
the duration of this permit. The Permittee shall notify the Director within seven
days when a well is no longer properly functioning (including the presence of sandy
or silty materials that impacts the well function and cracked or broken casings). The
Director must approve in writing the conditions for replacement or correction of improperly operating well(s).
IV.D.1.c. The Permittee shall measure the total depth of all groundwater monitoring wells
that are completed in unconsolidated sediments (listed in Table 2, Attachment 3)
every five years. Total well depth measurements shall be compared to the original
total depths for each well and submitted to the Director with the Annual Groundwater Monitoring Report in the year following total well depth measurements. If a problem is observed, the Permittee shall follow the procedures
described above in Condition IV.D.1.b. regarding notification and corrective
procedures.
IV.D.1.d. The permanent removal of any wells in the groundwater monitoring system (Table 1, Attachment 4) shall be approved by the Director in writing. A request for the removal of wells shall constitute a permit modification.
IV.D.1.e. The Permittee shall install additional groundwater monitoring wells to maintain
compliance with this Module if subsurface conditions significantly change after
permit issuance. Such changes may include, but are not limited to, water level elevation or apparent flow direction changes, or detection of one of the hazardous constituents in a monitoring well. If hazardous waste constituents exceed the
groundwater protection standard concentration limits, as defined in Section IV.C.
of this Module, in the furthest most hydraulically down-gradient monitoring
well(s), the Permittee shall install additional groundwater monitoring wells further
down-gradient.
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IV.D.1.f. Upon notification by the Director in writing, or as a result of an enforcement action, the Permittee may be required to install and sample additional wells at any time during the post-closure or compliance periods if new information or unforeseen
circumstances reveal a need for additional monitoring to protect human health and
the environment.
IV.D.1.g. The Permittee shall not add or remove any groundwater monitoring wells without prior written approval of the Director. The Permittee shall submit to the Director an application for a permit modification (for Attachment 4) within ninety (90) days of
when new wells are added to or removed from the groundwater monitoring system.
IV.D.2. The Permittee shall locate, install, construct, and maintain new groundwater
monitoring wells as specified below: IV.D.2.a. Well construction shall follow the techniques described in the Technical
Enforcement Guidance Document (TEGD), OSWER-9950.1, November 1992, or
most current, approved edition. All monitoring wells shall be cased in a manner that
maintains the integrity of the monitoring well bore hole. This casing shall be
screened or perforated, and packed with gravel or sand, depending on the formation, to enable collection of groundwater samples. The annular space, the space between the bore hole and well casing above the sampling depth, shall be sealed with bentonite grout to prevent contamination of samples and the groundwater.
IV.D.2.b. The Permittee shall construct and maintain new monitoring wells and piezometers
in accordance with plans and specifications to be submitted to the Director for
approval. The Director will approve in writing the following: number, location, depth, and design of all new wells and piezometers prior to installation.
IV.D.2.c. The Permittee shall submit monitoring well completion reports within ninety (90)
days after completion of any new wells installed. These reports shall, at a
minimum, consist of the following components: a boring log that documents well
drilling and associated sampling; a well construction log and well construction diagram (“as built”); well survey information for locations and elevations of the newly completed wells, the results of pump tests or slug tests, and a summary that
discusses how the groundwater flow model shall be updated based on the data
obtained from the installation of the new wells. The detailed information that shall
be included for each of the four components is outlined in Attachment 5.
IV.D.2.d. The Permittee shall properly dispose all contaminated groundwater generated during groundwater monitoring well sampling and during the development of new
monitoring wells.
IV.D.2.e. The Permittee shall permanently remove wells from the monitoring well system in
accordance with the plugging and abandonment procedures described in the
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Technical Enforcement Guidance Document (TEGD), OSWER-9950.1, November
1992, and subsequent addenda and as specified in Condition IV.D.1.d. above. IV.D.3. The Permittee shall include and maintain sampling and analysis procedures in the
groundwater monitoring program that are designed to ensure reliable monitoring
results. As required by R315-264-97(d), the program shall include procedures and
techniques for:
IV.D.3.a. sample collection;
IV.D.3.b. sample preservation and shipment;
IV.D.3.c. analytical procedures;
IV.D.3.d. chain-of-custody control; and
IV.D.3.e. quality assurance and quality control.
IV.D.4. The sampling and analytical methods must be appropriate for groundwater sampling
and accurately measure hazardous waste constituents in groundwater samples, as
required by R315-264-97(e). IV.D.5. The Permittee shall use the following techniques and procedures when obtaining
samples and analyzing samples from the groundwater monitoring wells, piezometers
and springs:
IV.D.5.a. The Permittee shall collect, preserve, and transport all samples from monitoring wells, piezometers and springs in accordance with the procedures specified in the Sampling and Quality Assurance Project Plans, presented in Attachment 3;
IV.D.5.b. Changes to the sampling or analysis procedures specified in Attachment 3, Module
IV, or Module V, shall require a permit modification;
IV.D.5.c. The Permittee shall ensure all samples will be analyzed according to the test methods shown in Table 1 of the Groundwater Sampling and Analysis Plan,
Attachment 3, or an equivalent EPA-approved method that has been pre-approved,
by the Director in writing as per Condition I.G.13. In addition:
IV.D.5.c.i. All major analytical peaks greater than 25% of the peak height of the closest internal standard shall be identified using the most current National Bureau of Standards (NBS) Library. The quantity of these compounds shall be estimated and reported
based upon the closest internal standard;
IV.D.5.c.ii. Any major analytical peak found during the analysis may become a target parameter
for that constituent.
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IV.D.5.c.iii. All data shall be collected and validated as outlined in the Sampling and Quality Assurance Project Plans contained in Attachment 3. The Permittee shall resample all wells from which data is rejected.
IV.D.5.c.iv. The Director may request at any time all laboratory QA/QC documentation and
supporting data on any sampling episode in the previous 5 years. The raw organics
information for required sampling and analysis, including organics gas chromatographic printouts, mass spectral analyses, and QA/QC surrogate and spiking results shall be retained by the Permittee at the Promontory facility and
made available within fifteen (15) working days of request throughout the post-
closure care period.
IV.D.5.c.v. All samples shall be tracked and controlled using the chain-of-custody procedures specified in the Sampling and Quality Assurance Project Plans contained in Attachment 3.
IV.D.5.c.vi. In case of loss of sample integrity (e.g. breakage, loss), resampling shall take place
within seven days of the loss of sample integrity.
IV.D.6. The Permittee shall determine the groundwater surface elevation in all monitoring wells listed in Table 4-A, Attachment 4 annually. The Permittee shall determine the groundwater surface elevation in the piezometers listed in Table 4-A, Attachment 4,
on an as needed basis as determined by the Director.
IV.D.7. The Permittee shall maintain a record of the piezometer locations and mark the
locations of piezometers in the field so that they may be found as needed. IV.D.8. The Permittee shall, on an annual basis, construct maps of the potentiometric
surface, based on the groundwater surface elevation data collected as described in
Condition IV.D.6. If, based on annual monitoring, the Director determines that
additional potentiometric data is needed, the Permittee shall install additional
monitoring wells or piezometers. IV.D.9. The Permittee shall determine the groundwater flow rate and direction in the
impacted aquifers based on groundwater surface elevation measurements. An
updated potentiometric map shall be submitted to the Director on an annual basis as
specified in Condition IV.E.2.
IV.D.10. If the Director receives information indicating that the surveyed well casing elevations of the wells in the groundwater monitoring system, as specified in
Condition IV.A.2., exceed 0.01 feet from a fixed datum the Permittee shall resurvey
any or all of these well casing elevations.
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IV.D.11. The Permittee shall submit plume maps, as specified in Section IV.E. to show the
concentration of hazardous constituents detected in impacted aquifers. Plume maps shall be submitted for the following constituents: trichloroethene, 1,1,1-trichloroethane, 1,1-dichloroethene, 1,1-dichloroethane, cis-1,2-dichloroethene,
chloroform and perchlorate.
IV.E. REPORTING AND RECORD KEEPING IV.E.1. The Permittee shall keep a record of all monitoring, testing and analytical data obtained pursuant to the groundwater monitoring requirements contained in this
Module. This data shall be managed as part of the Operating Record until closure
of the facility in accordance with R315-264-73(b)(6).
IV.E.2. The Permittee shall submit to the Director, for approval, annual Groundwater Monitoring Reports compiling the results of groundwater monitoring and assessing the effectiveness of the corrective action program. These reports shall be submitted
no later than March 15 of each year and shall contain the following information:
IV.E.2.a. An Introduction and list of wells describing the monitoring that was conducted, a
summary of the analytical results and a description of the QA/QC results;
IV.E.2.b. Results of sample analysis including the concentration of hazardous constituents, units of measurement, well or spring sampled, date sample was collected, the EQL
and MDL;
IV.E.2.c. Results of sample analysis for samples collected in the Fall from Pipe and Shotgun
Springs; IV.E.2.d. QA/QC information including Case Narratives from the laboratory and Data
Validation Reports as described in Section D2 of the QAPP (Attachment 3);
IV.E.2.e. Measurements of static water levels as directed by Condition IV.D.6.;
IV.E.2.f. Potentiometric surface maps of the impacted aquifer(s). This map shall indicate the rate and direction of groundwater flow, as indicated by Conditions IV.D.8. and
IV.D.9.
IV.E.2.g. Groundwater Monitoring Well Inspection Checklist (Attachment 2);
IV.E.2.h. Total monitoring well depth data in the year following total well depth measurements for wells listed in Table 2, Attachment 3, as directed by Condition
IV.D.1.c.
IV.E.2.i. Plume maps showing contaminant concentrations of the impacted aquifers, as
directed by Condition IV.D.11.;
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IV.E.2.j. Results of annual model recalibration and a summary analysis of annual model results, as directed by Conditions V.E.2. and IV.E.3.;
IV.E.2.k. Identification of potential “hot spots”meriting attention for further evaluation
(subsequent report will identify trends if any anomalies persist and propose
corrective action or modification to the system).
IV.E.3. If new groundwater surface or contaminant data does not show any discernable differences from the previous groundwater model calibration, and if the previous
groundwater model calibration was deemed satisfactory by the Director, the
Permittee may petition the Director to postpone the groundwater model
recalibration for one year.
IV.E.4. The annual groundwater monitoring reports identified in Conditions IV.E.2. through IV.E.2.k. shall also be submitted electronically. Data submitted
electronically shall be in a format approved by the Director.