Site 28 Supplemental Investigation

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Former NAS Moffett Field Neil Hey, PG Shaw E & I, Inc. & Valerie Harris, PE Remedial Project Manager Navy BRAC PMO West RAB Meeting February 7, 2013 Site 28 Supplemental Investigation

description

Presentation to the February 7, 2013, Moffett Restoration Advisory Board meeting by Neil Hey of Shaw E&I and Valerie Harris of the Navy.

Transcript of Site 28 Supplemental Investigation

Page 1: Site 28 Supplemental Investigation

Former NAS Moffett Field

Neil Hey, PG

Shaw E & I, Inc.

&Valerie Harris, PE

Remedial Project Manager

Navy BRAC PMO West

RAB Meeting

February 7, 2013

Site 28 Supplemental Investigation

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Presentation Overview

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Project Objectives

Technical Approach

Preliminary Results

Remaining Work

Questions

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Supplemental investigation is needed to:

1) Further delineate PCE & daughter products (TCE,DCE, & VC) in A-aquifer within & around the FormerBuilding 88 & Traffic Island source areas

2) Confirm depth & lateral continuity of A/B-aquitard inTraffic Island Area

3) Verify depth to top of B2-aquifer in Traffic IslandArea

4) Confirm whether existing well W-88-1 is screened inB2-aquifer

5) Confirm whether B2-aquifer beneath Traffic IslandArea is impacted by COCs

Project Objectives

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Phase 1 – Semi-quantitative ScreeningSurvey

To further assess the distribution of CEs andsoil lithology in the areas of interest

Phase 2 – Monitoring Well Installations &Sampling

To fill in data gaps of the current groundwatermonitoring well network

Technical Approach

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Navy SCAPS Rig

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SCAPS Probe

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From:

U.S. Army Corps of Engineers, 2002,

Cost and Performance Report for Tri-Service

SCAPS MIP, January , ERDC/EL TR-02-1

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Membrane interface probe (MIP)/ Direct sample ion-trapmass spectrometer (DSITMS) detector System

Semi-quantitative COC concentration data(mg/L of calibration solution)

MIP data are only considered estimates(USACE, 2002)

<http://el.erdc.usace.army.mil/elpubs/pdf/trel02-1.pdf>

Results by MIP system are relative & should beverified by soil and groundwater samples(EPA, 2012)

<http://www.clu-in.org/characterization/technologies/mip.cfm>

MIP/DSITMS System

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SCAPS Test Results – Former Bldg 88

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Maximum MIP/DSITMSResponse & Groundwater

and Soil Results

PCE

~6 to 16 ft bgs(Fine-grained Sediment Interval)

GeneralGroundwaterFlow Direction

11.5 ft bgs830,000 µg/Lcs – MIP660 µg/L - GW8.8 mg/kg - Soil

11.1 ft bgs210,000 µg/Lcs – MIP440 µg/L - GW0.45 mg/kg - Soil

µg/Lcs denotes micrograms perliter of DSITMS calibration solution

Tier 2 SCAPS test location

Tier 1 SCAPS test location

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SCAPS Test Results – Former Bldg 88

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GeneralGroundwaterFlow Direction

18 ft bgs50,000 µg/Lcs – MIP78 µg/L - GW1.9 mg/kg - Soil

Maximum MIP/DSITMSResponse & Groundwater

and Soil Results

PCE

~16 to 27 ft bgs(Coarse-grained Sediment Interval)

µg/Lcs denotes micrograms perliter of DSITMS calibration solution

Tier 2 SCAPS test location

Tier 1 SCAPS test location

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SCAPS Test Results – Former Bldg 88

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GeneralGroundwaterFlow Direction Tier 2 SCAPS test location

Tier 1 SCAPS test location

Maximum MIP/DSITMSResponse & Groundwater

and Soil Results

PCE

~27 to 40 ft bgs(Fine-grained Sediment Interval)

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SCAPS Test Results – Former Bldg 88

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GeneralGroundwaterFlow Direction

Maximum MIP/DSITMSResponse & Groundwater

and Soil Results

PCE

~40 to 56 ft bgs(Coarse-grained Sediment Interval)

Tier 2 SCAPS test location

Tier 1 SCAPS test location

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SCAPS Test Results – Former Bldg 88

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GeneralGroundwaterFlow Direction

Maximum MIP/DSITMSResponse & Groundwater

and Soil Results

PCE

~56 to 70 ft bgs(Coarse & Fine-grained

Sediment)

Tier 2 SCAPS test location

Tier 1 SCAPS test location

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1) SCAPS results generally correlate well with historical data

2) MIP/DSITMS detections of PCE primarily in fine-grained sediments

3) Highest MIP/DSITMS detections of TCE & DCE primarily in fine-grained sediments

4) Vinyl chloride was not detected in any of the MIP/DSITMS samples

5) Fine-grained sediments acting as a continuing source of chemicals tothe groundwater

6) MIP/DSITMS responses are over 10-times higher than collocateddiscrete depth groundwater sample results

7) Discrete depth groundwater results are 10-times lower thanestimated effective solubility limits

8) Discrete depth soil results are over 10-times lower than estimatedsoil saturation concentrations

Preliminary Findings

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Potential Well LocationsFormer Bldg 88 Area

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GeneralGroundwaterFlow Direction

11.5 ft bgs830,000 µg/Lcs – MIP660 µg/L - GW8.8 mg/kg - Soil

11.1 ft bgs210,000 µg/Lcs – MIP440 µg/L - GW0.45 mg/kg - Soil

New Monitoring Well

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Planned SCAPS LocationsTraffic Island Area

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GeneralGroundwaterFlow Direction

0 to 23 ft bgs

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Planned SCAPS LocationsTraffic Island Area

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GeneralGroundwaterFlow Direction

23 to 46 ft bgs

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Planned SCAPS LocationsTraffic Island Area

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GeneralGroundwaterFlow Direction

46 to 65 ft bgs

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Planned Well LocationsTraffic Island Area

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Tier 2 SCAPS at Former Bldg 88 Area – Spring 2013

Tiers 1 & 2 SCAPS at Traffic Island Area – Spring 2013

Monitoring Well Installations – Summer 2013

Groundwater Sampling – Summer & Fall 2013

Field Work Timeline

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Questions?

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Point of Contact:

Scott Anderson

BRAC Environmental Coordinator

(619) 532-0938

[email protected]