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Assessment and Remediation of PICATINNY ARSENAL (USARMY)
New Jersey, USA
History of Land Use and Source of Contamination
• Site Name : Picatinny Arsenal
– Area : 6,491 Acres
– City : Dover (County : Morris)
– Location : New Jersey, USA
– Land Used : Over 100 years
– Source of : Ammunition in wartime.
• Land Use : Research, development and pilot-plant production of weapons, constituent explosives
and propellants ,Testing and manufacturing explosives and propellants, Shell-burial areas. Surface
impoundments, landfills, drum-storage areas. Rocket-engine testing areas.
• Source of Contaminants : Discharge to sewer/surface water
: Explosive disposal/detonation
: Inadvertent spill
: Lagoon disposal and Landfill
: Manufacturing process
: Storage - drums/containers of waste
: Waste pile, tank - above and below ground
Dominant Contaminants on the Site
• Contaminants
– VOC in area D Groundwater consists of a large groundwater plume which
have originated from de-greasing activities at Building 24.
– TCE in Building 95 a maximum concentration of 15.7 mg/liter detected in
wells up gradient from the wastewater-treatment site in Ground water .
– PCBs were detected in surface soil, subsurface soil, and sediment samples
collected at Site 20/24. In the original RI investigation, PCBs exceeded the RG
of 2 mg/kg in five surface soil samples with max concentration of 296 mg/kg.
– LEAD was detected in six surface soil samples at 20/24 site, concentrations
were greater than its RG (580 mg/kg). Concentrations of lead ranged from 621
mg/kg to 2,000 mg/kg (2001 USEPA)
• Effect
– Ground water (drinking water);
– Surface water (drinking water, human food chain, sensitive environments);
– Soil exposure (resident population, nearby population, sensitive environments);
– Air pollution (population, sensitive environments).
Geological feature and characteristics of the site
• The arsenal is in the central part of the New Jersey Highlands .
• The Highlands are a northeast-southwest-trending system composed of folded and faulted
• Precambrian to Devonian rocks that form a sequence of broad level highlands separated by long narrow
valleys. At least 156 potentially-hazardous locations exist on the site.
Soil Profile Ground Water Flow
Areal map and Contaminated Areas
Proposed Remediation Approach reported in the ROD and
Expected Results
• Remediation Approaches
• Prevent exposure to contaminated media by human and biological receptors
• Air stripper for VOC
• Granular activated Carbon (GAC) for VOC remediation
• Discharge of Effluent via holding tank and piping to green pond brook
• Protect uncontaminated media for future use
• Minimize migration of contaminants to adjacent media
• Protect environmental receptors
• Installation of a Vegetated Soil Cover Mat Con Asphalt Cap and Continued Implementation of Land Use
and Access Restrictions
• Excavation of Soil with PCB, LEAD and detected contaminants
• Pre-treatment System of GW .
• Results
• The Selected Remedy will ensure that risks remain below
– The 1x10-6 cancer risk level
– Hazard Index of less than 1.0.
• This level falls at the lower end of the USEPA's target risk range of 10-4 to 10-6. There are no short-term
threats associated with the Selected Remedy that cannot be readily controlled. In addition, no adverse cross-
media impacts are expected from the Selected Remedy.

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Assessment and Remediation of Dominant Contaminants of Picatinny Arsenal, New Jersey, USA

  • 1. Assessment and Remediation of PICATINNY ARSENAL (USARMY) New Jersey, USA History of Land Use and Source of Contamination • Site Name : Picatinny Arsenal – Area : 6,491 Acres – City : Dover (County : Morris) – Location : New Jersey, USA – Land Used : Over 100 years – Source of : Ammunition in wartime. • Land Use : Research, development and pilot-plant production of weapons, constituent explosives and propellants ,Testing and manufacturing explosives and propellants, Shell-burial areas. Surface impoundments, landfills, drum-storage areas. Rocket-engine testing areas. • Source of Contaminants : Discharge to sewer/surface water : Explosive disposal/detonation : Inadvertent spill : Lagoon disposal and Landfill : Manufacturing process : Storage - drums/containers of waste : Waste pile, tank - above and below ground
  • 2. Dominant Contaminants on the Site • Contaminants – VOC in area D Groundwater consists of a large groundwater plume which have originated from de-greasing activities at Building 24. – TCE in Building 95 a maximum concentration of 15.7 mg/liter detected in wells up gradient from the wastewater-treatment site in Ground water . – PCBs were detected in surface soil, subsurface soil, and sediment samples collected at Site 20/24. In the original RI investigation, PCBs exceeded the RG of 2 mg/kg in five surface soil samples with max concentration of 296 mg/kg. – LEAD was detected in six surface soil samples at 20/24 site, concentrations were greater than its RG (580 mg/kg). Concentrations of lead ranged from 621 mg/kg to 2,000 mg/kg (2001 USEPA) • Effect – Ground water (drinking water); – Surface water (drinking water, human food chain, sensitive environments); – Soil exposure (resident population, nearby population, sensitive environments); – Air pollution (population, sensitive environments).
  • 3. Geological feature and characteristics of the site • The arsenal is in the central part of the New Jersey Highlands . • The Highlands are a northeast-southwest-trending system composed of folded and faulted • Precambrian to Devonian rocks that form a sequence of broad level highlands separated by long narrow valleys. At least 156 potentially-hazardous locations exist on the site. Soil Profile Ground Water Flow
  • 4. Areal map and Contaminated Areas
  • 5. Proposed Remediation Approach reported in the ROD and Expected Results • Remediation Approaches • Prevent exposure to contaminated media by human and biological receptors • Air stripper for VOC • Granular activated Carbon (GAC) for VOC remediation • Discharge of Effluent via holding tank and piping to green pond brook • Protect uncontaminated media for future use • Minimize migration of contaminants to adjacent media • Protect environmental receptors • Installation of a Vegetated Soil Cover Mat Con Asphalt Cap and Continued Implementation of Land Use and Access Restrictions • Excavation of Soil with PCB, LEAD and detected contaminants • Pre-treatment System of GW . • Results • The Selected Remedy will ensure that risks remain below – The 1x10-6 cancer risk level – Hazard Index of less than 1.0. • This level falls at the lower end of the USEPA's target risk range of 10-4 to 10-6. There are no short-term threats associated with the Selected Remedy that cannot be readily controlled. In addition, no adverse cross- media impacts are expected from the Selected Remedy.