Table 6-4. Estimated Cost for OU 12 Vadose <strong>Zone</strong> Investigation Using SVE/DSITMSTask Duration Quantity Unit Unit Cost Total Cost Assumptions(days)Project PlansDraft Work Plan 40 1 ls $20,000 $20,000 Assume standard cost and preparation time for project plans (WP, HASP, and SAP).USAF Review 30 --- --- --- --- Assume standard 30-day review cycle.Final Work Plan 21 1 ls $5,000 $5,000 Assume standard time and cost to respond to comments and modify project plans.Subtotal $25,000SVE InvestigationCoordination and Planning 5 40 hr $65 $2,600 Includes subcontractor coordinate, site preparation, utilities clearance, cleanup, and IDW disposal.Vapor Probe Well Installation 1- mobilization/demobilization --- 1.5 hr $110 $165 Assume local mobilization/demobilization cost.- DPT rig with operator --- 10 hr $140 $1,400 Assume seven 0.75-inch diameter vapor extraction wells installed from approx. 30 to 50 ft bgs.- field geologist --- 10 hr $65 $650 Assume 10 hrs for field geologist oversight.- materials --- 7 ea $250 $1,750 Assume $250 per well based on actual costs.SVE Process System Setup 4- field engineer --- 40 hr $85 $3,400 Assume 10 hrs per day for 4 days to construct skid-mounted SVE process system.- field geologist --- 40 hr $65 $2,600 Assume 10 hrs per day for 4 days to construct skid-mounted SVE process system.- materials --- 1 ls $1,000 $1,000 Includes 0.75-inch PVC piping, rotometers, and vacuum guages.SVE Operations 5- field engineer --- 60 hr $85 $5,100 Assumes 12 hrs per day for 5 days to conducted step tests at 7 locations.- field geologist --- 60 hr $65 $3,900 Assumes 12 hrs per day for 5 days to conducted step tests at 7 locations.- field generator and diesel --- 5 day $125 $625 Includes generator and diesel cost to operator blower 12 hrs per day for 5 days.- on-site laboratory analysis --- 5 day $3,500 $17,500 Analyses for TCE, PCE, DCE, and vinyl chloride; assumes no off-site confirmation analyses.- data evaluation --- 24 hr $115 $2,760 Assumes 24 hrs for engineer to evaluate SVE data and make recommendations for soil sampling.Subtotal $43,450Limited Soil InvestigationCoordination and Planning --- 8 hr $65 $520 Assumes addition 8 hrs of labor for coordination to transition from SVE to soil sampling.Sample Collection 3- mobilization/demobilization --- 1.5 hr $110 $165 Assume local mobilization/demobilization cost.- DPT rig with operator --- 36 hr $140 $5,040 Drill 6 locations to 60 ft bgs with sample collection every 2 ft starting at 20 ft bgs for a total of 20- drillers assistant --- 36 hr $45 $1,620 samples per location. Assume 2 locations per day = 3 days x 12 hr/day = 36 hrs.- field geologist --- 36 hr $65 $2,340 Assume 3 days x 12 hr/day = 36 hrs for field geologist to log cores and collect samples.- bentonite grout --- 12 bag $25 $300 Assume 2 bags of bentonite grout per location; 6 total locations.- on-site laboratory analysis --- 3 day $3,500 $10,500 Analyses for TCE, PCE, DCE, and vinyl chloride; assumes no off-site confirmation analyses.Subtotal $20,485Remedial Investion (RI) <strong>Report</strong>Update of CSM 10 48 hr $90 $4,320 Assume an average rate of $65/hr for geologist and $115/hr for hydrogeologist/engineer.Draft RI <strong>Report</strong> 30 120 hr $90 $10,800 Assume an average rate of $65/hr for geologist and $115/hr for hydrogeologist/engineer.USAF Review 30 --- --- --- --- Assume standard 30-day review cycle.Final RI <strong>Report</strong> 21 40 hr $90 $3,600 Assume an average rate of $65/hr for geologist and $115/hr for hydrogeologist/engineer.ERPIMS Data Package --- 48 hr $70 $3,360 No ERPIMS-formatted electronic data package from field lab but abbreviated analyte list.Subtotal $22,080IDW Disposal (Soil)Drum and Hazardous Waste Tranportation --- 1 ls $250 $250 Assume 40 gallons of TCE-contaminated soil generated during sampling.Hazardous Waste Disposal (Incineration) --- 525 lb $0.29 $152 Assume 525 lb TCE-contaminated soil per location using 2-inch diameter DPT rod, 40 ft totalRCRA State Tipping Fee --- 1 ton $28 $28 depth per location, and bulk soil density of 100 lb/cubic foot; 6 total locationsSubtotal $430Travel 35 hr $65 $2,275 Assume 1.5 hr/day for 13 days for field geologist and 10 days for field engineer.Subtotal 200 --- --- --- $113,720Project Management --- --- --- --- $11,372 Assume 10% of project subtotal cost for project management.Total $125,092March 2003 6-8OU 12 <strong>Demonstration</strong> <strong>Report</strong>Final
and the three-dimensional numerical modeling of soil contamination generated during the investigation,data gaps are identified prior to demobilizing from the site. Based on the experience from the OU 12<strong>Source</strong> <strong>Zone</strong> <strong>Delineation</strong> <strong>Demonstration</strong>, it is feasible to update/refine the soil contamination model withthe analytical data obtained from the most recent boring prior to mobilizing the CPT rig to the nextsampling location. In addition, the WS/DSITMS investigation eliminates the data evaluation andreporting task typically required during a conventional investigation.The total cost for a single phase of fieldwork and sample analyses in the WS/DSITMS investigation is$90,620, compared with $120,790 and $111,750 for two phases in the HSA investigation and DPTinvestigation, respectively. An additional cost of $14,760 is incurred during the conventionalinvestigative approaches for data evaluation and reporting following the first phase of fieldwork. Thedata evaluation and reporting task is required to identify data gaps associated with the initial phase ofsampling and develop a sampling and analysis plan to fill those gaps in order to adequate characterize thesuspected source zone. By eliminating the need for a second phase of field investigation, the overalltimeframe for making subsequent decisions is reduced. This results in a shorter timeframe by which tomake investigative and/or remediation decisions and ultimately can reduce the lifecycle costs associatewith a site.Although the WS/DSITMS investigation does not require a separate data evaluation and reporting taskbetween field sampling events, it does require the development of a site model to guide sample collection.For the WS/DSITMS investigation, it is assumed that $3,680 (32 hours of a seniorhydrogeologist/engineer) is required to refine the site model from the work plan prior to the start offieldwork. During field activities, it is assume that an additional $4,140 (4 hours per day for 9 days of asenior hydrogeologist/engineer) is required to continuously update/refine the site model with the mostrecently collected site data. Because the site model is built and continuously updated in the field, lesstime is required during the RI reporting stage to generate the final version of the CSM, thus reducing theoverall cost of the RI report. In addition to a reduction in cost, one of the main advantages of theWS/DSITMS investigative approach is data density and the consequent improvement in the model ofVOC contamination in the vadose zone. The nominal vertical spacing between soil samples is 1 foot forthe WS/DSITMS investigation, compared to 2 feet for the conventional investigative techniques.Ultimately, the higher data density achieved in the WS/DSITMS investigation results in a very detailedmodel of vadose zone contamination. Decreasing the spacing to 1 foot during the conventionalinvestigations doubles the analytical expense, significantly increasing total project costs.In spite of its advantages, the WS/DSITMS investigation has some limitations. Flexibility in selecting asoil sample is lost, because a sample can only be collected from either end of the 1-inch diameter and 1-foot long stainless steel sampling tube. A related drawback is the inability to continuously log soilstratigraphy. At best, a one-foot composite soil type can be identified, based on the material removedfrom the sampling tube when it is cleaned. Moreover, none of the traditional CPT logging data iscollected with the Wireline CPT sampler, precluding the inference of soil stratigraphy from CPT logs.The method is also constrained by the ability of the CPT rig to push, making the method difficult to applyin gravelly and cobbly soils, and also limiting the method to relatively shallow (
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FinalSource Zone Delineation Demons
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EXECUTIVE SUMMARYThis report docume
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The SVE demonstration conducted in
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TABLE OF CONTENTSEXECUTIVE SUMMARY
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LIST OF FIGURESFigure ES-1 Iso-Conc
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Figure 5-38 Horizontal slices at fi
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LIST OF ACRONYMS AND ABBREVIATIONSA
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Hill Air Force BaseUtahRIVERDALEWeb
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Co-Team LeaderCo-Team LeaderURS Pro
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1.4 Report OrganizationThe remainin
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Davis-Weber CanalDetail AreaHillAir
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ANorthSouthU5-18864,580CROSS SECTIO
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Approx. LocationOf BarrelsInitial S
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Figure 3-2. Wireline locking and re
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3.3 DSITMS Soil AnalyticsDirect sam
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4.0 SOIL VAPOR EXTRACTION DEMONSTRA
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The equilibrium four-phase distribu
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3520 ft. from well, 3.5 cfmTCE in E
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The SVE system included piping from
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SVE Process System and On-Site DSIT
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Table 4-3. Summary of OU 12 SVE Ste
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3,000U12-VP1 Calibration Curve2,500
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5.0 RESULTS OF SOIL SAMPLING AND SV
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0U12-1802100U12-1803100U12-18051020
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0102030405060700U12-1804U12-1807102
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Figure 5-4. Soil samples collected
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298400298360Northing (ft)2983202982
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298400298360Northing (ft)2983202982
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The final TCE soil contamination mo
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298400298360Northing (ft)2983202982
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Figure 5-12. Isometric view, lookin
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An isometric view of the upscaled a
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March 2003 5-21 OU 12 Demonstration
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4620WE460045804560454045204500Verti
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4620WE460045804560Elevation (ft)454
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Volumetric calculations yield an es
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The position of the water table in
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5.2 OU 12 SVE EvaluationThe OU 12 S
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Vapor Probe #1Vapor Probe #2Vapor P
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Thus, the in situ air permeability
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0.0000-0.0010U12-VP1 ResponsePressu
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0.000020.00000U12-VP1 ResponsePress
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Table 5-5. Estimated In Situ Air Pe
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- Page 94 and 95: 200.018180.016TCE Concentration (pp
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- Page 102 and 103: permeability layer. Final adjustmen
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- Page 106 and 107: Table 5-8. continuedFile Name Extra
- Page 108 and 109: U12-1802U12-VP3U12-1812U12-1803U12-
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- Page 118 and 119: 5 10 15 20 25 30 35 40 455 10 15 20
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- Page 150 and 151: 8.0 REFERENCESBear, J. 1979. Hydrau
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- Page 170 and 171: APPENDIX BSimulated TCE Vapor-Phase
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- Page 174 and 175: U12-PV1Source Area #2TCE Concentrat
- Page 176 and 177: U12-PV1Source Area #2250VP1 i=24, j
- Page 178 and 179: U12-PV1Source Area #3TCE Concentrat
- Page 180 and 181: U12-PV1Source Area #4TCE Concentrat
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U12-PV1Source Area #7TCE Concentrat
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TCE Concentration (ppmv1,7301,7201,
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TCE Concentration (ppmv6,0005,0004,
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U12-PV1Source Area #8TCE Concentrat
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U12-PV1Source Area #9500450VP1 i=24
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TCE Concentration (ppmTCE Concentra
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700600U12-PV1Source Area #9VP1 i=24
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U12-PV2Source Area #1TCE Concentrat
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U12-PV2Source Area #3TCE Concentrat
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U12-PV2Source Area #7TCE Concentrat
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U12-PV2Source Area #7TCE Concentrat
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TCE Concentration (ppmv1,4001,2001,
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U12-PV2Source Area #7TCE Concentrat
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U12-PV2Source Area #7TCE Concentrat
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U12-PV2Source Area #8TCE Concentrat
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U12-PV2Source Area #8TCE Concentrat
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U12-PV2Source Area #10250VP2 i=23,
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U12-PV3Source Area #9TCE Concentrat
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U12-PV4Source Area #7TCE Concentrat
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U12-PV4Source Area #9TCE Concentrat
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TCE Concentration (ppm1.00.90.80.70
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U12-PV6Source Area #7TCE Concentrat
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U12-PV6Source Area #8TCE Concentrat
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U12-PV6Source Area #101816VP6 i=33,
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TCE Concentration (ppm6050403020100