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2003-06-12_REVISION - M1999034 (2)
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2003-06-12_REVISION - M1999034 (2)
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Last modified
6/15/2021 2:45:23 PM
Creation date
11/21/2007 11:56:29 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1999034
IBM Index Class Name
Revision
Doc Date
6/12/2003
Doc Name
Board Packet
From
DMG
To
Members of Board
Type & Sequence
AM1
Media Type
D
Archive
No
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mining operation! A copy of the CDPS Industrial General Permit issued to AI with an effective date <br />of October 1, 2002 is enclosed as Attachmem 3. This permit has two outfalls and does not require <br />any water quality monitoring even though numeric standards exist for the Upper South Platte River <br />Subbasin in this area. More important was the fact that the Water Quality Control Division did not <br />review the permit application for antidegradation criteria. <br />The mining site and my property are within the historical ground water contaminant plume <br />emanating from the Rocky Mountain Arsenal (RMA) located 2.5 miles to the southeast. Weapons <br />production and industrial manufacture of pesticides and herbicides contaminated soil, sediments, and <br />water at the RMA. From 1942 through 1969, the Army manufactured weapons including nerve <br />agents at the arsenal. Shell Chemical Company leased part of the site from the Army and produced <br />pesticides and herbicides from 1951 until 1982. Offpost ground water contamination was not <br />idernified until 1974. EPA added the arsenal to its National Priorities List (Superfund) in 198 7. <br />According to the Tri-County Health Department, the majority of offpost contamination is found in <br />the shallow, unwnfined aquifer (alluvial aquifer). In their overview of the RMA, enclosed as <br />Attachment 4, Tri-County Health Department states, "The main Arsenal-related contaminants in the <br />groundwater aze: volatile organic chemicals, such as Benezene, Chloroform, Toluene, and <br />Trichloroethylene (TCE); pesticides and other related chemicals, such as Aldrin, Atrazine, <br />Chlordane, Dibromochloropropane (DBCP), Dieldrin, Enfrin, and Isodrin; Army nerve agent by- <br />products like Diisopropylmethylphosphonate (DIlv1P); and heavy metals, including Arsenic, <br />Cadmium, Chromium, Lead, and Mercury. Table SA, also included in Attachment 4, from the <br />Public Health Assessment dated September 30, 1996 prepared by the Agency for Toxic Substances <br />and Disease Registry lists the maximum historical detection levels and range of detections for a <br />number of these contaminants. <br />For diswssion purposes, I will focus on Diisopropyl Methylphosphonate (DIIvIP) as it was the <br />subject of numerous investigations in this area. DIMP does not occur naturally and is created as a <br />by-product of the production of the chemical agent Sarin. Concerns regarding the toxicity to this <br />chemical prompted the Water Quality Control Commission to establish a statewide DIIvIP standard <br />of 8 µg/L for both surface water and ground water in Colorado. In 1990, the Colorado Department <br />of Health tested my drinking water well (Arapahoe aquifer) and found 27.9 µg2 D1MP. Additional <br />sampling by Tri-County Health in 1991 produced no detectable levels. 1985 sampling of my alluvial <br />irrigation well by Tri-County Health produced a DIIvvIP concentration of 5.2 µg2. As a result of <br />these investigations, the residence was provided with bottled water and continues to utilize that <br />source for drinking water. During the Pro-Hearing conference, I learned that AI has also tested for <br />DIIviP in this area and has reported concentrations above the detection limits. <br />My concern is ~ the contaminant concentrations in ground water today, rather the release of <br />adsorbed comaminants due to excavation mining operations. DI1vfP is a member of a class of semi- <br />volatileorganic compounds, though somewhat soluble, that tend to adsorb on soil particles. <br />Docwnentation of this characteristic is enclosed as Attachment. 5. Adsorption is the most common <br />way in which contaminants are removed from the ground water as it moves through a porous <br />medium (Tchobanoglous, 1987). Adsorption occurs when a dissolved ion or molecule becomes <br />attached to the surface solid particles, sedimentary grains. The amount of a contaminant subject to <br />adsorption in a ground water aquifer is dependent upon that chemical's distribution coefficient. The <br />forces that hold the molecule to the sedimentary grains are very weak. These adsocfied wntaminants <br />are not only within the current aquifer matrix but also the zone of historical water table fluctuation as <br />
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