DISTRIBUTION AND FATE OF ENERGETICS AT THE MMR IMPACT AREA AND - - PowerPoint PPT Presentation

distribution and fate of energetics at the mmr impact
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DISTRIBUTION AND FATE OF ENERGETICS AT THE MMR IMPACT AREA AND - - PowerPoint PPT Presentation

DISTRIBUTION AND FATE OF ENERGETICS AT THE MMR IMPACT AREA AND TRAINING RANGES Jay Clausen Senior Hydrogeologist/ Geochemist (AMEC) Marc Grant (AMEC) Ben Gregson (IAGWSP) Presented at SERDP and ESTCP Symposium. November 27-29, 2001.


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SLIDE 1

DISTRIBUTION AND FATE OF ENERGETICS AT THE MMR IMPACT AREA AND TRAINING RANGES

Jay Clausen Senior Hydrogeologist/ Geochemist (AMEC) Marc Grant (AMEC) Ben Gregson (IAGWSP)

Presented at SERDP and ESTCP Symposium. November 27-29, 2001. Washington, DC (IAGWSP Contact Ben Gregson 508-968-5821).

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SLIDE 2

Introduction

  • Military training ranges under scrutiny

– Potential impacts to ecology and environment – Complex issues and problems

  • Major ranges receiving attention

– Massachusetts Military Reservation (MMR) - ARNG – NoMan Island – Vieques, Puerto Rico - U.S. Navy

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SLIDE 3

Camp Edwards - Site History

  • Training and Impact Areas used since 1911
  • Designed to house 30,000 troops during

WWII

  • USEPA banned training

in 1997 through an administrative order

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SLIDE 4

Site Lithology

Legend

VC Sand & Gravel F Sand & Silt Till Bedrock Water Table Well Screen

ELEVATION IN FEET (MSL)

  • 100
  • 50

50 100 150 200

Sea Level

Aquifer Unsaturated Zone

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SLIDE 5

Hydrogeologic Model

  • Groundwater flow is

radial with the mound to the southeast of the Impact Area in the J Range Area

  • Groundwater flow is

approximately one foot per day

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SLIDE 6

Areas of Investigation

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SLIDE 7

Surface Soil Findings

TNT 6.3% RDX 37.0% HMX 20.3% 2,4-DNT 1.3% aDNTs 32.3% Other 2.7%

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SLIDE 8

Soil Results (explosives)

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SLIDE 9

Soil Results at Artillery Target 42

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SLIDE 10

Groundwater Findings (explosives)

RDX 65.7% HMX 21.9% aDNTs 12.4%

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SLIDE 11

Plan View of RDX Detections in the Impact Area

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SLIDE 12

Inner Groundwater Transect within the Impact Area

210 160 110 60 10

  • 40
  • 90
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SLIDE 13

Longitudinal Cross-Section through the Impact Area

210 160 110 60 10

  • 40
  • 90
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SLIDE 14

Location of Perchlorate In Groundwater at MMR

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SLIDE 15

Potential Source Area

  • High-order

detonations

  • Low-order

detonations

  • UXO
  • EOD activities

at the J Range

  • Disposal/Burial

sites

  • Washout
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SLIDE 16

Explosive Fate-and-Transport Conceptual Model

  • Deposition of particulates to ground surface
  • Slow dissolution of particulates
  • Rapid movement of dissolved explosives through

unsaturated zone, leaving little residual contamination (RDX and HMX)

  • Introduction to groundwater results in rapid transport

away from source

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SLIDE 17

Conclusions

  • RDX and HMX present in surface soil adjacent to

artillery and mortar targets

  • RDX and HMX present in groundwater downgradient
  • f primary target area (i.e. Tank Alley) within the

Impact Area

  • TNT which is a component of the munitions appears

to be degraded before reaching groundwater

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SLIDE 18

Conclusions (cont.)

  • Training using HE artillery and mortar rounds (UXO,

detonation, or both) appears to have resulted in an explosive impact to groundwater at MMR

  • Some metals, PAHs, and pesticides/herbicides present

in surface soil but no evidence of impacts to groundwater

  • PCNs may be an issue for soil and perchlorate may be

an issue for groundwater

  • MMR findings are potentially applicable to other bombing

ranges and battlefields

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SLIDE 19

Lessons Learned

  • Compositing explosive soil samples is necessary
  • Modifications to explosive analytical methods may be

needed – expanded analyte list – changes to sample preparation – lower detection limits

  • Perchlorate (OB/OD) and PCNs for ranges may be

issues

  • Maintain strong technical focus
  • OB/OD is worse case (concentration)