Barrier Wall Performance 2009 Data

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Barrier Wall Performance 2009 Data July 2010 Progress Meeting McCormick & Baxter Superfund Site Portland, Oregon

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Barrier Wall Performance 2009 Data. July 2010 Progress Meeting McCormick & Baxter Superfund Site Portland, Oregon. Barrier Wall Performance. NAPL Recovery Where and how much NAPL Thicknesses Tracking thicknesses inside and outside wall Groundwater and River Elevations - PowerPoint PPT Presentation

Transcript of Barrier Wall Performance 2009 Data

Page 1: Barrier Wall Performance 2009 Data

Barrier Wall Performance

2009 Data

July 2010 Progress Meeting

McCormick & Baxter Superfund Site

Portland, Oregon

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Barrier Wall Performance

• NAPL Recovery– Where and how much

• NAPL Thicknesses– Tracking thicknesses inside and outside wall

• Groundwater and River Elevations– Shallow contour maps– Hydrographs– Gradients

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NAPL Recovery

• ROD RA Objectives: contain NAPL, prevent ongoing discharges of NAPL to Willamette River, and minimize further contamination of intermediate and deep aquifers

• Tasks:– Weekly recovery from wells outside barrier wall that

have sufficient NAPL• MW-Ds, MW-Gs, MW-20i (DNAPL only)• EW-1s (inside barrier wall)

– Quarterly gauging for NAPL in remaining wells

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Total NAPL Recovery1989-2010 ~6373gallons

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Wells with NAPL

Outside Barrier WallMW-20i MW-Gs MW-Ds MW-10s

Inside Barrier WallEW-8s MW-56sEW-18s MW-10rEW-1s EW-15sEW-23s

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MW-Ds (outside, FWDA)

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MW-Gs (outside, FWDA)

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MW-20i (outside, FWDA)

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MW-23s (inside, FWDA)

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EW-15s (inside, FWDA)

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MW-56 (inside, FWDA)

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EW-18s (inside, TFA)

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NAPL Recovery SummaryOutside Barrier Wall• 2008: 57 gallons of DNAPL from 3 wells (primarily MW-20i);

no LNAPL • 2009: 92 gallons DNAPL (MW-20i, MW-Gs, MW-Ds); no

LNAPL • 2010: 66 gallons DNAPL to date (including EW-1)• NAPL levels remain stable

Inside Barrier Wall – • monitored for NAPL quarterly; • Stable thicknesses • 2009: 21 gallons of DNAPL from EW-1s

Automated NAPL Recovery System - 2011

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Groundwater Flow

• Shallow Zone Contour Maps (4 quarters)

• Hydrographs from transducer data (historic and annual)

• Vertical Gradients (using 2008 transducer data)

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March 2009

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June 2009

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September 2009

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December 2009 (with Triangle Park)

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MW-36s/MW-37sinside/outside

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2009 Data MW36/MW37

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MW-40/MW-41Inside/Outside

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MW44s/MW45sinside/outside

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2009 Data MW44/MW45

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MW-52s/MW53sinside/outside

Historically, MW-52s gw elevation was ~18.5 NAVD88 (May 2003). The level has gradually dropped since installation of the barrier wall. Rate of decline increased with installation of the impermeable soil cap. Approaching equilibrium with the River

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Vertical Gradients

Monitoring WellShallow to

intermediateIntermediate to

deepShallow to

deep

MW-36 (inside) -0.0434 -0.0020 -0.191

MW-37 (outside) -0.0070 0.0022 -0.0015

MW-44 (inside) -0.0841 0.0165 -0.029

MW-45 (outside) -0.0066 0.0017 -0.0018

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Main Points• Shallow groundwater within Barrier Wall will equilibrate with the River

(dropped 5 feet – 1-2 more)

• Shallow groundwater outside and inside the barrier wall are not hydraulically connected (i.e., barrier wall is performing as expected)

• GW inside barrier wall is hydraulically connected to the river from the “drain” in corner at base of wall

• Intermediate and deep zones inside and outside the barrier wall continue to mimic river with very low vertical gradients (primarily downward)

• Gradients low and primarily downward: conditions are not conducive to NAPL migrating from inside barrier wall or from MW-20i to River

Barrier wall is performing as designed to prevent NAPL (from within the wall) from migrating to the River; also, significantly reduces the flux of contaminated groundwater to river