03.04.2013 Views

Final Remedial Action Completion Report for the ... - Rvaap.org

Final Remedial Action Completion Report for the ... - Rvaap.org

Final Remedial Action Completion Report for the ... - Rvaap.org

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

<strong>Remedial</strong> <strong>Action</strong> <strong>Completion</strong> <strong>Report</strong><br />

June 2008<br />

1.2.1 Load Lines 1 - 4<br />

Remediation of Soils and Dry Sediments at RVAAP 08-11 (LLs 1-4)<br />

Page 1-5<br />

Industrial operations at <strong>the</strong> RVAAP primarily consisted of 12 munitions assembly facilities<br />

referred to as “load lines.” LLs 1-4 were used between 1941 and 1971 to melt and load<br />

trinitrotoluene (TNT) and Composition B, a mixture of TNT and cyclotrimethylenetrinitramine<br />

(cyclonite or RDX), into large-caliber shells. The operations of <strong>the</strong> primary load lines produced<br />

explosive dust, spills and vapors that collected on <strong>the</strong> floors and walls of various process<br />

buildings. Periodically, <strong>the</strong> floors and walls would be cleaned with water and steam. The<br />

resulting liquid contained TNT and Composition B and was known as “pink water” <strong>for</strong> its<br />

characteristic color.<br />

Various industrial operations associated with <strong>the</strong> munitions loading process and munitions<br />

rehabilitation activities were also conducted during <strong>the</strong> operation of LLs 1-4. As a result of <strong>the</strong>se<br />

operational activities, soils, sediments, and o<strong>the</strong>r media became contaminated with explosives.<br />

In 1951, soils contaminated with accumulated explosives were removed from LL 1 and replaced<br />

with clean fill. No o<strong>the</strong>r remedial actions, except salvage and building demolition activities,<br />

have been conducted at LLs 1-4.<br />

The RVAAP has been inactive since 1992. The only activity still being carried out from <strong>the</strong><br />

wartime era is <strong>the</strong> infrequent demolition of munitions and explosives of concern (MEC) found at<br />

<strong>the</strong> RVAAP. The Army has completed <strong>the</strong> salvage activities and demolition at LLs 2-4, with <strong>the</strong><br />

exception of floor slabs and foundations which are contracted to be removed by o<strong>the</strong>rs in 2008.<br />

1.3 NATURE AND EXTENT OF CONTAMINATION<br />

The summary of <strong>the</strong> nature and extent of contaminated shallow soils and dry sediment <strong>for</strong> which<br />

<strong>the</strong> remedial action was per<strong>for</strong>med is based on <strong>the</strong> Phase I and II remedial investigations (RIs)<br />

<strong>for</strong> LLs 1-4 (SAIC 2003; Shaw 2004b, 2004c, 2004d). Evaluation and data collected <strong>for</strong> LLs 1-4<br />

during <strong>the</strong> Phase I and II RIs show that historical operations resulted in contamination of shallow<br />

soils and dry sediment primarily in <strong>the</strong> vicinity of <strong>for</strong>mer production buildings and in various<br />

settling tanks and drainage ditches near those buildings. The wash water from <strong>the</strong> floors and<br />

walls that contained contaminants infiltrated into <strong>the</strong> soils around <strong>the</strong> buildings, drained into <strong>the</strong><br />

network of storm sewers, or was directed by surface flow through channels to surface water. The<br />

chemicals of concern (COCs) included metals, explosives, polychlorinated biphenyls (PCBs) and<br />

semi-volatile <strong>org</strong>anic compounds (SVOCs). Based on evaluations conducted during <strong>the</strong> RIs,<br />

explosives were mobile in water and had <strong>the</strong> potential to leach from <strong>the</strong> soils. In<strong>org</strong>anics, PCBs<br />

and polynuclear aromatic hydrocarbons (PAHs) were not expected to readily leach from soils.<br />

Contamination varied considerably within each load line by type and frequency of contaminant<br />

detected, concentration, and depth. Based on <strong>the</strong> RI data, LL 1 was <strong>the</strong> most contaminated (i.e.,<br />

widest variety of contaminants detected, highest frequency of COC detection, and highest COC<br />

concentrations) and LL 4 was <strong>the</strong> least contaminated of <strong>the</strong> four load lines.<br />

The soil and sediment contamination detected at LLs 1-4 was generally surficial in nature,<br />

between ground surface and 3 feet below ground surface (bgs). As mentioned previously, <strong>the</strong><br />

likelihood of migration was minimal <strong>for</strong> in<strong>org</strong>anics, PCBs and SVOCs identified as <strong>the</strong> COCs;<br />

however, explosive constituents may have leached from soils via infiltration. Based on <strong>the</strong><br />

available data, <strong>the</strong> estimated quantity of soils and dry sediments to be removed was 15,000 cubic<br />

*** FINAL***

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!