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_REVISION - M1977208 (3)
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_REVISION - M1977208 (3)
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Entry Properties
Last modified
6/18/2021 6:14:51 AM
Creation date
11/22/2007 12:30:36 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1977208
IBM Index Class Name
Revision
Doc Name
RESULTS OF SOUTHDOWN INC LYONS PLANT INVESTIGATION INTO ON SITE STORAGE OF CEMENT KILN DUST
Type & Sequence
TR1
Media Type
D
Archive
No
Tags
DRMS Re-OCR
Description:
Signifies Re-OCR Process Performed
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DG°~Q~'~ <br />seepage in response to rainfall or snowmelt, or from ditch seepage. The <br />direction of groundwater flow in the sedimentary strata is to the east, primarily <br />along bedding planes. <br />The western highwall of C-Pit was dry this year, before the water began to flow in <br />/ the Boulder Feeder Canal. About 3 days after the Canal started flowing, <br />seepage appeared in the C-Pit highwall. This fact indicates that groundwater is <br />not the source of these observed seeps. Figures 2A, 2B and 2C show a <br />sequence of photographs of the western highwall of C-Pit before and after the <br />Canal started flowing. <br />The alluvial aquifer of St. Vrain Creek is in contact with the sedimentary strata <br />east of C-Pit but not in contact with C-Pit itself. Groundwater in the alluvial <br />aquifer is typically 5-8 feet below ground surface and flows east-southeast, <br />generally towards St. Vrain Creek. There is no apparent hydraulic connection <br />between C-Pit and the alluvial aquifer. <br />6.0 Surrounding Wells and Local Aquifers <br />There are two aauifers in the area that are typically used for water supply. They <br />are the al~vial aaoi_ifPr_of St. Vrain Creek and the Dakota sandstone. Both of <br />these aquifers are isolated from C-Pit by 800-1000 fegt of relatively imaermeablE <br />sedimentary rocks. <br />Figure 3 shows a plot of wells in the area based on data from the Colorado <br />Division of Water Resources (permitted wells database). The list of wells from <br />the Colorado Division of Water Resources is included in Appendix B. Wells are <br />shown by quarter -quarter section. It should be noted that many of the wells are <br />piezometers and monitoring wells installed by Western Mobile in their sand and <br />gravel property. <br />Recent water quality data is available from wells in both the Dakota sandstone <br />and in the alluvial aquifer. Water quality in both aquifers is generally good with <br />no indication of any impact from CKD disposal. <br />A well completed in the Dakota sandstone (located in the extreme southeast <br />corner of section 28) was sampled in April, 1 ersonnel from Grant <br />Environmental, Inc. The laboratory results (Table 6.1) 'ndicate that the water <br />quality is in compliance with almost all app' ndards. Results of water <br />quality analysis in A-Pit Reservoir are also shown in Table 6.1. <br />The pH (which would serve as a key indicator of impacts due to CKD disposal) of <br />Dakota Well water is 8.28, within the natural, expected range. Table 6.1 shows <br />the measured water quality in this well compared to the groundwater standards <br />suggested by the DMG. <br />13 <br />
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