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HomeMy WebLinkAboutDERR-2025-003433 Stantec Consulting Services Inc. 2890 East Cottonwood Parkway Suite 300 Salt Lake City UT 84121-7283 April 29, 2025 Project/File: 203724520 Liberty Coe Utah Department of Environmental Quality Division of Environmental Response and Remediation 195 North 1950 West, First Floor Salt Lake City, Utah 84116 Reference: Work Plan and Budget NGN-17: Corrective Action Plan Execution 7-Eleven Store No. 35508 712 South State Street, Clearfield, Utah Facility ID 3000334, Release Site NGN Dear Ms. Coe, On behalf of 7-Eleven, Inc. (7-Eleven), Stantec Consulting Services Inc. (Stantec) has prepared the following work plan and budget (WP&B) to perform remedial excavation and groundwater removal as the Corrective Action Plan (CAP) at 7-Eleven Store No. 35508 (the Site), located at 712 South State Street, Clearfield, Utah (Figure 1). The Utah Department of Environmental Quality (UDEQ), Division of Environmental Response and Remediation (DERR) refers to the Site as Facility ID 3000334 and Release Site NGN. The Site is eligible for reimbursement under the Utah Petroleum Storage Tank Trust Fund. The scope of work proposed herein would be designated as WP&B NGN-17. WP&B NGN-17 presents a summary of the public notification process and the remedial alternatives evaluation authorized under WP&B NGN-16 and a technical approach and cost estimate for the following WP&B NGN-17 scope of work.  Remedial excavation and off-site disposal of petroleum impacted soils and addition of agricultural gypsum soil amendment  Groundwater removal, on-site treatment, and discharge via the North Davis Sewer District (NDSD)  Reporting  Reimbursement services Public Notification Summary DERR provided approval of the public notice document prepared by Stantec via email on April 8, 2025. On April 9, Stantec distributed hard copies of the public notice (with the CAP meeting summary letter as an attachment) to the following adjacent businesses.  Kyle Long at Caliber Collison located at 520 East 700 South  Kathy Hamm at Utah Title Loans located at 710 South State Street No one was present at Westbridge Auto on April 9. On April 10, Stantec emailed a copy of the public notice and CAP meeting summary letter to Aaron Olsen of Westbridge Auto. Stantec has not received any public comments regarding the CAP to date. April 29, 2025 Page 2 of 7 Reference: Work Plan and Budget NGN-17: Corrective Action Plan Execution 7-Eleven Store No. 35508 712 South State Street, Clearfield, Utah Facility ID 3000334, Release Site NGN Remedial Alternatives Evaluation Stantec conducted a remedial alternatives evaluation to compare potential remedial alternatives to mitigate soil and groundwater impacts at the Site following underground storage tank removal. Potential remedial alternatives included excavation and off-site disposal of source area soils, off-site disposal of groundwater or on-site treatment with on-site discharge to the NDSD, and application of a soil amendment to address soil and groundwater impacts that may not be mitigated by soil excavation and disposal and treatment of pumped groundwater. Soil Excavation and Disposal Soil excavation was chosen as part of the CAP because it was anticipated that petroleum impacted soil (PIS) would be exposed during UST closure activities. Off-site disposal of PIS is feasible because of the relative proximity of the Site to the ET Technologies Soil Regeneration Site (SRS). Groundwater Based on an anticipated total excavation depth of 15 feet below ground surface and historical data indicating a relatively fast groundwater recharge rate (a 30-day CalClean dual phase extraction event in 2017 and numerous single-day dual phase extraction events via vacuum truck) Stantec anticipated that excavation dewatering will be necessary to maintain excavation wall stability. As groundwater pumped from the excavation will be impacted with petroleum hydrocarbons, off-site disposal or treatment prior to on-site discharge will be a necessary component of the CAP. Through communication with Jonas Reeder (the Industrial Pretreatment Coordinator for the NDSD) Stantec learned that there is no fee associated with discharge of pretreated industrial process water into the NDSD. Charges may be imposed if industrial discharges cause process disruptions at the NSDS. Some cost will be associated with monitoring the volume of groundwater discharged to the NDSD and laboratory analysis of effluent samples. Off-site disposal of groundwater was not evaluated further due to the relatively low costs of discharge to the NDSD. Two on-site groundwater treatment techniques were evaluated for the pumped groundwater: granular activated carbon (GAC) treatment and air sparging (AS) in an open top frac tank. AS treatment of the pumped groundwater was found to be advantageous over GAC treatment for two main reasons. The AS treatment timeframe can be shorter than typical gravity fed GAC treatment systems. Also, relatively high petroleum hydrocarbon concentrations are expected which could saturate the GAC and cause concentration break through. Soil Amendment Stantec evaluated two soil amendments to address soil and groundwater impacts that may remain after and groundwater pumping and treatment: BOS 200® and agricultural gypsum. Agricultural gypsum was chosen based on its lower cost and better applicability as a soil amendment coupled with impacted soil excavation. April 29, 2025 Page 3 of 7 Reference: Work Plan and Budget NGN-17: Corrective Action Plan Execution 7-Eleven Store No. 35508 712 South State Street, Clearfield, Utah Facility ID 3000334, Release Site NGN The recommended dosage rate of both BOS 200® and agricultural gypsum is one percent by weight of the backfill material. Stantec’s estimated delivered price of BOS 200® is $12,000 per ton, whereas the estimated delivered price of agricultural gypsum is $550 per ton. Due to the significant relative cost of BOS 200® it was not evaluated further as a soil amendment. Stantec conducted monitored natural attenuation (MNA) parameters sampling on April 16 through 18, 2025. Samples were submitted for analysis of nitrate and sulfate by United States Environmental Protection Agency (EPA) Method 9056A, dissolved iron by EPA Method 6020B, and dissolved methane by the RKS-175 Method. Samples were submitted for 4-day rush turnaround to Pace Analytical National of Mount Juliet, Tennessee. The MNA parameters analytical results (presented in Table 1) indicated that concentrations of known electron acceptors utilized in anaerobic biological degradation were lower in impacted groundwater monitoring wells compared to non-impacted wells. Impacted wells also exhibited higher concentrations of dissolved methane compared to non-impacted wells indicating methanogenesis is occurring. Methanogenesis degrades petroleum hydrocarbons more slowly than other anaerobic biological degradation processes that utilize other electron acceptors. Agricultural gypsum was selected as a soil amendment to be mixed with backfill material to provide sulfate as an electron acceptor to promote further anaerobic biological degradation for the following reasons.  Gypsum soil amendment is a relatively low-cost addition to the existing soil excavation and disposal and groundwater treatment and discharge scope of work.  Impacted groundwater monitoring wells show lower concentrations of known anaerobic biological degradation electron acceptors and higher concentrations of dissolved methane than non-impacted wells.  Gypsum will provide sulfate as an alternative electron acceptor allowing for enhanced anaerobic biological degradation of petroleum hydrocarbons through sulfate reduction instead of relatively slower degradation through methanogenesis. Scope of Work Task 1.1 – Remedial Excavation The UST system removal is scheduled to begin on Monday, May 5, 2025. Spackman Enterprises (Spackman) has been selected as the tank removal contractor. The UST system removal and closure sampling will be completed prior to beginning any portion of the remedial excavation scope of work. It is estimated that the UST system removal and closure sampling will be completed by May 7, and remedial excavation will be able to begin on May 7. Costs for the portion of the excavation necessary to remove the UST system will be the responsibility of 7-Eleven, and reimbursement will not be requested for those costs. The proposed maximum lateral extent of the remedial excavation is shown in Figure 1; the actual extent of the excavation (both laterally and vertically) will be determined based on field screening observations (soil staining and photoionization detector [PID] readings) coupled with soil sample laboratory analytical results. April 29, 2025 Page 4 of 7 Reference: Work Plan and Budget NGN-17: Corrective Action Plan Execution 7-Eleven Store No. 35508 712 South State Street, Clearfield, Utah Facility ID 3000334, Release Site NGN Stantec will oversee soil potholing by Spackman on Monday, May 5, 2025. Potholing will provide soil samples for waste characterization analytical data requirements and begin to provide soil analytical data to correlate with field screening observations. Potholing samples will be submitted for 24-hour rush turn around. UST closure soil samples will also be submitted for 24-hour rush turn around. If it is determined that soil analytical results correlate well with field screening observations, 24-hour rush turn around may not be necessary for remedial excavation confirmation samples. The excavation extents may also be limited by Site infrastructure. Shoring will not be used; therefore, Spackman will use excavation sloping to provide stability to the excavation walls and protect existing infrastructure. This may limit the lateral and vertical extents of the excavation. The proposed maximum excavation extents were assumed based on a history of measurable light non- aqueous phase liquid (LNAPL) being present in monitoring wells MW-2 and MW-2R, historical soil and groundwater analytical data, and the age of the release. Table 2 shows historical soil analytical results. In addition to a history of measurable LNAPL at MW-2 and MW-2R, soil samples collected from the soil borings for MW-2 and MW-2R showed concentrations above UDEQ DERR Petroleum Storage Tank (PST) Branch Initial Screening Levels (ISLs). Measurable LNAPL was also detected at MW-5/5R in March and June 2017. Historical dissolved petroleum hydrocarbon concentrations at MW-5/5R have consistently remained above ISLs and Tier 1 Screening Levels. Monitoring wells MW-2 and MW-2R will likely be destroyed during remedial excavation activities. MW-5R maybe be destroyed as well. It is Stantec’s intention to maintain monitoring wells MW-1 and MW-3. Following CAP execution, Stantec will prepare a WP&B for follow-up groundwater monitoring and sampling; that WP&B will also include replacement of any monitoring wells destroyed during remedial excavation. Using the anticipated area of the remedial excavation and a planned total excavation depth of 15 feet below the original ground surface, Stantec estimates that approximately 2,700 tons of soil will be excavated (in addition to the volume of soil excavated to remove the UST system). It is anticipated that the 2,700 ton total excavation soil volume may include up to 1,300 tons of PIS. Excavated soils will be screened for visual staining and using a PID and segregated into PIS and non-impacted stockpiles. Non-impacted soil that is deemed suitable for use as backfill will be stockpiled on site for later use. Stantec will coordinate disposal of PIS at the ET Technologies SRS. Stantec anticipates the collection of up to 13 soil confirmation samples (in addition to the required UST closure soil samples) from the excavation bottom and sidewalls; proposed confirmation soil sample locations are shown on Figure 1. Samples will be collected by a PST Branch certified soil and groundwater sampler. Samples will be collected from the excavator bucket; neither Stantec nor Spackman personnel will enter the excavation to collect samples. Samples will be collected into laboratory supplied containers, labeled with the sample identification, collection date, and time, and placed into an ice chilled cooler for delivery to the project laboratory under chain-of-custody (COC) documentation. April 29, 2025 Page 5 of 7 Reference: Work Plan and Budget NGN-17: Corrective Action Plan Execution 7-Eleven Store No. 35508 712 South State Street, Clearfield, Utah Facility ID 3000334, Release Site NGN Samples will be submitted for analysis of methyl tertiary-butyl ether, benzene, toluene, ethylbenzene, total xylenes, and naphthalene (MBTEXN) by EPA Method 8260 and gasoline range total petroleum hydrocarbons (TPH-GRO) and diesel range TPH (TPH-DRO) by EPA Method 8015. Samples will be submitted to Chemtech-Ford Analytical Laboratories (Chemtech-Ford) of Sandy, Utah. Spackman will provide additional backfill material as needed to account for excavated soil that is removed from the site. Backfill material and labor costs resulting from excavation of PIS will be submitted for reimbursement; however, costs associated with the UST closure backfilling will be accounted for separately and will not be submitted for reimbursement. Agricultural gypsum will be mixed with backfill material as a sulfate amendment to promote continued anaerobic biological degradation within the dissolved plume. Gypsum will be mixed with backfill material via the excavator bucket. Task 1.2 – Groundwater Removal It is anticipated that petroleum impacted groundwater will be encountered at a depth between11 and 12 feet below ground surface. Spackman will provide dewatering services in conjunction with the remedial excavation to maintain excavation stability. Groundwater will be pumped into an open top, 17,000-gallon frac tank on site and treated via AS prior to discharge into the NDSD. For the purposes of this work plan, Stantec estimates that a total of approximately 19,000 gallons of groundwater will be removed from the excavation. To the extant practical, in an effort to minimize the amount of groundwater produced by dewatering, excavation will be conducted in approximate north to south cross sections and proceed to the southwest. Should groundwater production exceed estimates, Spackman has the capability to bring an additional frac tank on site within the same day. Stantec has submitted a NDSD industrial discharge permit application to discharge the treated groundwater. The discharge permit will require Stantec to collect three effluent samples: one each at the beginning, middle, and end of the project. Samples will be collected into laboratory containers, labeled with the sample identification, collection date, and time, and placed into an ice chilled cooler for delivery to the project laboratory under chain-of-custody (COC) documentation. Samples will be submitted for 24-hour rush analysis of (MBTEXN) by EPA Method 8260 and TPH-GRO) and TPH-DR) by EPA Method 8015. Samples will be submitted to Chemtech-Ford. The UDEQ Division of Air Quality (DAQ) New Source Review Section requires submission of their Form 16 to document the estimated emissions from soil and groundwater hydrocarbon remediation projects. Stantec has completed the required emissions estimates for the processes of excavating PIS and air sparging hydrocarbon impacted groundwater within a frac tank. The estimated emissions are well below the annual small source exemption criteria listed in Utah Administration Code R301-401-9 of less than five tons of volatile organic compounds, 500 pounds of any hazardous air pollutant (HAP), and less than one ton of combined HAPs. Stantec will submit DAQ New Source Review Section Form 16 and associated emissions estimates prior to the project start date. April 29, 2025 Page 6 of 7 Reference: Work Plan and Budget NGN-17: Corrective Action Plan Execution 7-Eleven Store No. 35508 712 South State Street, Clearfield, Utah Facility ID 3000334, Release Site NGN Precautions will be taken to allow groundwater to drain from excavated soils throughout the excavation and loading process. Loaded trucks will not leave the Site until groundwater has been removed in order to avoid the loss of impacted material while in transit to the ET Technologies SRS. Task 2 – Reporting Upon the completion of field activities and the receipt of all analytical results, Stantec will prepare a report documenting UST removal and remedial activities. The report will include a summary of field activities, actual volumes of materials removed and placed (backfill to accommodate excavated PIS volumes and agricultural gypsum), soil and other material disposal documentation, confirmation sample results, and laboratory reports. Task 3 – Reimbursement Services Stantec’s services will include preparation of reimbursement claims on behalf of 7-Eleven. This task includes assembling invoices paid by 7-Eleven, invoices for subcontracted services, details of charges, Stantec invoices, proof of payment documentation, the DERR Standardized Invoice Form, and the DERR Request for Payment Voucher Summary Worksheet. Estimated Costs The estimated costs for the scope of work described in this work plan are presented in Table 3. Non- reimbursable costs, such as subcontractor markup, have been omitted from the cost breakdown. Spackman’s subcontracted cost estimate is provided as Attachment A. The costs presented in Table 3 represent Stantec’s estimate of likely charges to be incurred during the implementation of the scope of work described above. Actual charges to the tasks and activities included in the scope may vary from those presented in the estimate as activities and tasks require either more or less effort than estimated. Stantec will contact the DERR project manager if there is significant diversion from the estimated cost breakdown, or if additional authorization above the total estimated cost of this work plan is required. April 29, 2025 Page 7 of 7 Reference: Work Plan and Budget NGN-17: Corrective Action Plan Execution 7-Eleven Store No. 35508 712 South State Street, Clearfield, Utah Facility ID 3000334, Release Site NGN Should you have any questions or require any additional information, please contact Anna Skinner at (801) 743-4815. Sincerely, STANTEC CONSULTING SERVICES INC. Anna Skinner Project Manager Certified Consultant #0271 Phone: (801) 743-4815 anna.skinner@stantec.com Ally Auffermann PE Environmental Engineer Phone: (801) 617-3211 ally.auffermann@stantec.com Attachments: Figure 1 – Site Plan Table 1 – MNA Analytical Results Table 2 – Soil Analytical Results Table 3 – Estimated Costs for WP&B NGN-16 Attachment 1 – Spackman Cost Estimate Figure T T T T T T T T T XXXXXXXXXXXXXXXXX X X X X X X X X X X X X X X XXXXXX X X X X X X X X X X X X X X X X X X X X X X X X X 7-ELEVEN STORE NO. 35508 G G G G G G G G G G G G G G T T T T T T T T T T T T T T T T G G G G G G G G G G E E E E E E E E E E E E E E E E E E E E E E E E STORE E E E E MW-8 MW-2 MW-4R MW-3R MW-5R MW-2R MW-6R 7 0 0 S O U T H S T R E E T UTAH TITLE LOANS S T A T E S T R E E T PEDESTAL SIGN WATER METER CANOPY DISPENSERS PRODUCT PIPING LIGHT POLE TRANSFORMERTRASH ENCLOSURE TRANSFORMER MW-7R TRANSFORMER SSVMP-1 MW-9 MW-10 MW-12 MW-11 AB R A A U T O B O D Y S H O P 1SITE PLANSTORE NO. 35508 712 SOUTH STATE STREET CLEARFIELD, UTAH FOR: JOB NUMBER:DRAWN BY:CHECKED BY:APPROVED BY:DATE: FIGURE: No warranty is made by Stantec Consulting Services Inc. as to the accuracy, reliability, or completeness of these data. Original data were compiled from various sources. This information may not meet National Map Accuracy Standards. This product was developed electronically, and may be updated without notification. Any reproduction may result in a loss of scale and or information. N 0 40 80 APPROXIMATE SCALE IN FEET ELEVEN PHONE: 2890 E COTTONWOOD PKWY, STE 300 SALT LAKE CITY, UTAH (801) 261-0090 E MW-1R GW-1 SS-2 GW-2 SS-4 SS-5 SS-6 SS-7 SS-1/ USC-1 SS-3/ USC-2 SS-10/ USC-3 SS-9 SS-8 No warranty is made by Stantec Consulting Services Inc. as to the accuracy, reliability, or completeness of these data. Original data were LEGEND TELEPHONE LINE ELECTRIC LINE X X X X X G G T T E E MW-1 STORM DRAINSDSD CS-1 SS-1 UST CLOSURE SAMPLE LOCATION MONITORING WELL LOCATION CONFIRMATION SAMPLE LOCATION APPROXIMATE PROPERTY BOUNDARY FENCE LINE GAS LINE APPROXIMATE UST RESURFACING BOUNDARY APPROXIMATE EXCAVATION BOUNDARY Tables Sample Location Date Sulfate Iron Methane MW-1R 4/16/2025 7.15 T8 63.2 <0.100 <0.0100 MW-2R 4/17/2025 1.84 T8 31.1 6.84 0.544 MW-3R 4/17/2025 3.09 T8 46 <0.100 <0.0100 MW-4R 4/18/2025 2.47 45.2 0.111 0.0106 MW-5R 4/17/2025 <0.100 T8 <5.00 17.3 0.417 MW-6R 4/16/2025 5.76 65.9 0.359 <0.0100 MW-7R 4/17/2025 3.02 T8 47.4 <0.100 <0.0100 MW-8 4/17/2025 0.364 T8 18.8 0.237 0.0847 MW-9 4/18/2025 0.241 29.1 4.35 1.10 MW-10 4/16/2025 3.58 T8 44.4 <0.100 <0.0100 MW-11 4/17/2025 4.14 T8 45.9 <0.100 <0.0100 MW-12 4/16/2025 8.8 T8 62 <0.100 <0.0100 Notes: All concentrations are in milligrams per liter (mg/L). T8 = Sample(s) received too close to holding time expiration. Table 1 MNA Analytical Results 7-Eleven Store No. 35508 712 South State Street, Clearfield, Utah Nitrate Page 1 of 1 Stantec Consulting Services Inc. MW-1 7.0 08/03/15 <0.00189 0.00524 0.0130 0.00279 0.0168 <0.00473 0.280 <4.90 MW-1 14.0 08/03/15 <0.00188 0.00502 0.0117 <0.00188 0.0104 <0.00470 0.224 <4.87 MW-1R 17.5 10/05/16 <0.00189 0.00218 0.00308 <0.00189 <0.00567 <0.00473 <0.0945 <4.84 MW-2 11.0 08/03/15 <0.0975 0.678 4.99 1.33 10.9 <0.244 80.0 <4.87 MW-2 12.0 08/03/15 <0.0990 0.307 2.41 0.795 7.96 <0.248 52.1 <4.93 MW-2R 17.5 10/05/16 <0.00180 0.292 1.49 0.0659 0.564 <0.00450 3.65 <4.85 MW-2R 20.0 10/05/16 <0.00193 0.0172 0.129 0.0110 0.0922 <0.00484 0.503 <4.90 MW-3 12.5 08/03/15 <0.00188 0.0553 0.200 0.00338 0.192 <0.00469 0.638 <4.81 MW-3 14.0 08/03/15 <0.00195 0.0561 0.242 0.0213 0.200 <0.00486 1.06 <4.90 MW-3R 20.0 10/05/16 <0.00185 0.00285 0.00535 <0.00185 <0.00554 <0.00461 <0.0923 <4.98 MW-4 13.0 08/03/15 <0.00173 0.00533 0.0128 0.00199 0.0118 <0.00433 33.0 <4.96 MW-4 14.0 08/03/15 <0.00188 0.00655 0.0154 0.00367 0.0153 <0.00470 46.7 <4.71 MW-4R 19.0 10/05/16 <0.00196 0.00322 0.00524 <0.00196 <0.00588 <0.00490 <0.0980 <4.92 MW-5 12.0 12/08/15 <0.00168 0.0162 0.0655 0.00521 0.0450 <0.00419 0.310 <4.98 MW-5 15.0 12/08/15 <0.00188 0.00821 0.0578 0.0112 0.107 0.00618 0.843 <4.94 MW-5R 20.0 10/05/16 <0.00180 0.0295 0.0789 0.0125 0.0405 <0.00449 0.320 <4.93 MW-6 15.0 12/08/15 <0.00167 0.00336 0.00841 0.00167 0.00672 <0.00417 <0.0835 <4.94 MW-6 20.0 12/08/15 <0.00188 0.00461 0.0106 0.00198 0.00738 <0.00469 <0.0938 <4.92 MW-6R 18.0 10/04/16 <0.00189 0.00255 0.00395 <0.00189 <0.00566 <0.00472 <0.0943 <4.84 MW-7 10.0 12/08/15 <0.00182 0.00267 0.00688 <0.00182 <0.00547 <0.00456 <0.0912 <4.87 MW-7 15.0 12/08/15 <0.00185 0.00327 0.00757 <0.00185 0.00655 <0.00463 <0.0926 <4.96 MW-7R 17.5 10/04/16 <0.00190 <0.00190 <0.00190 <0.00190 <0.00569 <0.00474 <0.0949 <4.91 MW-8 11.0 10/04/16 <0.00196 <0.00196 0.00257 <0.00196 <0.00587 <0.00489 <0.0978 <4.91 MW-8 14.0 10/04/16 <0.00189 0.00226 0.00323 <0.00189 <0.00568 <0.00473 0.174 <4.93 MW-8 18.5 10/04/16 <0.00188 0.00271 0.00418 <0.00188 <0.00565 <0.00471 <0.0942 <4.86 MW-9 5.5 - 6.5 11/14/17 <0.00192 <0.00192 <0.00192 <0.00192 <0.00576 <0.00480 <0.0960 <4.83 MW-9 9 - 10 11/14/17 <0.00189 <0.00189 0.00212 <0.00189 <0.00566 <0.00472 <0.0956 <4.96 MW-9 13.0 - 13.5 11/14/17 <0.00194 0.00266 0.00434 <0.00194 <0.00581 <0.00484 <0.0859 <4.90 MW-9 18.5 - 19.0 11/14/17 <0.00184 0.00267 0.00534 <0.00184 <0.00551 <0.00460 <0.0942 <4.93 MW-10 10.3 08/29/19 <0.0101 <0.00504 <0.00504 <0.00504 <0.00504 <0.00504 <0.504 1.19 MW-10 20.0 08/29/19 <0.00990 <0.00495 <0.00495 <0.00495 <0.00495 <0.00495 <0.495 <0.993 MW-11 8.0 08/29/19 <0.0101 <0.00503 <0.00503 <0.00503 <0.00503 <0.00503 <0.477 <1.01 MW-11 20.0 08/29/19 <0.00998 <0.00499 <0.00499 <0.00499 <0.00499 <0.00499 <0.499 <0.995 MW-12 10.5 08/29/19 <0.00984 <0.00492 <0.00492 <0.00492 <0.00492 <0.00492 <0.492 <0.993 MW-12 20.0 08/29/19 <0.00967 <0.00484 <0.00484 <0.00484 <0.00484 <0.00484 <0.479 0.983 0.3 0.2 9 5 142 51 150 500 0.3 0.9 25 23 142 51 1,500 5,000 bgs mg/Kg MBTEXN TPH-GRO TPH-DRO MTBE < -- UDEQ RBCA bold = analyte not detected above the specified reporting limit = not measured or analyzed = Utah Department of Environmental Quality = Risk-Based Corrective Action = analytical result exceeds the specified UDEQ Initial Screening Level = below ground surface = milligrams per kilogram = methyl tertiary butyl ether, benzene, toluene, ethylbenzene, total xylenes, and naphthalene by EPA Method 8260B = gasoline-range total petroleum hydrocarbons by EPA Method 8260B = diesel-range total petroleum hydrocarbons by EPA Method 8015D = methyl tertiary butyl ether Ethyl- benzene Total Xylenes Naphthalene UDEQ Initial Screening Level RBCA Tier 1 Screening Level Explanation of Abbreviations Sample Location Depth (feet bgs) Date Sampled MBTEXN Compounds TPH-GRO (mg/Kg) TPH-DRO (mg/Kg) (mg/Kg) MTBE Benzene Toluene Table 2 Soil Analytical Results 7-Eleven Store No. 35508 712 South State Street Clearfield, Utah Page 1 of 1 Stantec Consulting Services Inc. PE, subcontractor procurement P102 4 hours @ $157.00 = $628.00 PE, DAQ and NDSD permitting P102 4 hours @ $157.00 = $628.00 Senior PM, soil waste profile application P101 2 hours @ $163.00 = $326.00 Senior PM, on site P101 4 hours @ $163.00 = $652.00 Field Scientist, on site P104 45 hours @ $109.00 = $4,905.00 Field Scientist, travel P104 9 hours @ $109.00 = $981.00 Subcontractor Bid 1 bid @ $106,300.00 = $106,300.00 Agricultural Gypsum 14 tons @ $83.71 = $1,171.94 Soil Disposal 1300 tons @ $25.07 = $32,591.00 Health and Safety Plan 1 NTE @ $470.00 = $470.00 PID 1 week @ $285.00 = $285.00 Sampling Supplies 1 week @ $100.00 = $100.00 MNA Laboratory Analyses 12 sample @ $198.00 = $2,376.00 Soil Waste Profile Laboratory Analyses 2 sample @ $182.00 = $364.00 Soil MBTEXN/GRO/DRO Analyses 13 sample @ $85.00 = $1,105.00 -- 24-hour rush turnaround 13 sample @ $85.00 = $1,105.00 Water MBTEXN/GRO/DRO Analyses 3 sample @ $85.00 = $255.00 -- 24-hour rush turnaround 3 sample @ $85.00 = $255.00 Senior PM, review P101 1 hour @ $163.00 = $163.00 PE, review P102 2 hour @ $157.00 = $314.00 PM, preparation P103 20 hours @ $127.00 = $2,540.00 Field Scientist, preparation P104 10 hours @ $109.00 = $1,090.00 Drafter P107 8 hours @ $90.00 = $720.00 Clerical P109 1 hours @ $66.00 = $66.00 Senior PM, review P102 3 hours @ $157.00 = $471.00 PST Specialist, preparation P108 8 hours @ $84.00 = $672.00 Task 3 Subtotal $1,143.00 Table 3 Corrective Action Plan Execution 7-Eleven Store No. 35508 712 South State Street, Clearfield, Utah Facility ID 3000334, Release Site NGN Total Budget $160,533.94 Estimated Costs for WP&B NGN-17 Task 2 - Reporting Task 2 Subtotal $4,893.00 Task 1 - Remedial Excavation and Groundwater Treatment Task 1 Subtotal $154,497.94 Task 3 - Reimbursement • PST Fund Claim Preparation Page 1 of 1 Stantec Consulting Services Inc. Attachment E S T I M A T E Spackman Enterprises, L.C. PO Box 1276 Centervi ll e, UT 84014 tspackman@spackmanenterprises.c om +1 (801) 589-1707 65-352 Stantec (7 Eleven Stores) Bill to Stantec C onsulting Corporation 2890 E Cottonwood Pa rkwa y Suite 300 SLC , UT 84121 Ship to Sta ntec Consulting Corp ora tion 3995 South 700 Ea st Suite 300 U tah Murra y, UT 84107 Estimate details Estim ate no.: 1125 Estim ate date: 02/28/2025 Job Site: 7-11 Clearfi eld Rem ediation #Product or service Descrip tion Qty Rate Am ount 1.Excavation Cutting and Removal of up to 2500 sq feet of asphalt 1 $1,750.00 $1,750.00 2.Excavation Excavatio n and Transpo rtation Only of 1300 tons of impacted soil 1300 $19.00 $24,700.00 3.Excavation Excavatio n and o nsite staging o f up to 1400 to ns or 933 CY o f clean overburden. 1 $6,300.00 $6,300.00 4.Excavation Backfill and compact with clean o verburden up to 1400 tons or 933 CY, excludes any testing due to material inconsistency 1 $6,300.00 $6,300.00 5.Excavation Unit co st for dispo sal o f unusable overburden, 20.00 per to n if it is accepted by co nro ck recycling as clean fill. 1 $0.00 $0.00 6.Excavation Additio nal backfill and compaction to replace impacted so il volume 1300 tons. 1300 $35.00 $45,500.00 7.Excavation Additio nal asphalt resurfacing 3"thick up to 2500 sq feet 2500 $3.50 $8,750.00 8.Excavation Dug in dewatering sump at time of excavatio n 1 $1,000.00 $1,000.00 9.Excavation Daily dewatering pump rate for a manned 2" trash pump. **up to 8 hours daily** excludes weekend, overnight, o r overtime 4 $900.00 $3,600.00 pumping. **3 days to pump while digging, 1 day to discharge frac tank. 10.Excavation Price per Frac Tank to Mobe/Demobe/Clean and Sediment removal/disposal (if clean sediment, if co ntaminated will take it to ET like the o ther so il. ) 1 $3,200.00 $3,200.00 11.Excavation Frac Tank per day 14 $50.00 $700.00 12.Excavation Cost fo r one pot filter, two carbon drums, set up and take do wn. Assumes being gravity fed ** excludes any mo nitoring or testing o r additio nal carbo n o r drums if needed** $5,500.00 1 $0.00 $0.00 13.Excavation Air sparging with a blower o r compresso r would be 800.00 per 8 ho ur day. U nmonito red. Rate includes fueling generator or co mpresso r daily. 5 $800.00 $4,000.00 14.Excavation Additio nal 15 days of fence 1 $500.00 $500.00 15.Excavatio n should take 3 days, backfill 4 days, resurfacing 1 day. 16.** Excludes any shoring, utility repair, co ncrete repair, or remobilization. Priced based on being able to excavate as soo n as removal is complete and backfill as so o n as excavation is complete. Total $106,300.00 Accepted date A ccepted by