My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
1999-04-12_GENERAL DOCUMENTS - M1974052
DRMS
>
Day Forward
>
General Documents
>
Minerals
>
M1974052
>
1999-04-12_GENERAL DOCUMENTS - M1974052
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
4/12/2023 5:51:47 PM
Creation date
11/23/2007 6:51:20 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1974052
IBM Index Class Name
General Documents
Doc Date
4/12/1999
Doc Name
WORK PLAN VARRA COAL ASH BURIAL PROJECT WELD CNTY COLO CGRS 1-135-2755
Media Type
D
Archive
No
Tags
DRMS Re-OCR
Description:
Signifies Re-OCR Process Performed
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
69
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
CGRS, Inc. <br /> ' closely approximating natural ground water than for the TCLP test. The results of the SGLP are <br /> directly comparable to the TCLP test. <br /> ' Groundwater obtained from the study area was used for the test. The full suite of chemical <br /> compounds (see list for SELP test) were analyzed during the SGLP test. The groundwater used in <br /> ' the SGLP test as the leaching fluid was analyzed for full suite of chemical compounds. The <br /> difference in the before and after chemical concentrations in the ground water used in the SGLP <br /> test represents the concentration of the chemical contaminants leached from the ash. <br /> ' 2.3.4 "Synthetic Groundwater Column Leaching Procedure" (SGCLP) <br /> The purpose of the "Synthetic Groundwater Column Leaching Procedure" (SGCLP) test was to <br /> ' determine the rate as a function of pore volume at which the chemical contaminant will be leached <br /> from the buried ash. The SGCLP test used synthetic groundwater with varying pH levels as the <br /> ' leaching fluid(s). With the SGCLP test, a specified weight (e.g. one kilogram) of the ash was <br /> placed in a column. Once the column was saturated, the testing period began. One pore volume of <br /> ' water was passed through the column and the concentration of the various contaminants measured <br /> in the outflow water. The SGCLP test was then repeated for several sequential pore volumes of <br /> twater. The hydraulic head on the column was adjusted so that one pore volume of water was <br /> passed through the sample in about 12 hours. Water samples were obtained for analyses at 2, 4 <br /> and 8 pore volumes of water flow through ! " <br /> r <br /> ' The SGCLP test was repeated for synthetic ground water with varying pH values to represent a <br /> range of possible site conditions. Synthetic ground water(s) with pH values of 5, 7 and 8.5 were <br /> ' used as the leaching fluid(s). For the fly ash, which has a very low hydraulic conductivity, the <br /> SGCLP test was conducted for 1, 2 and 4 pore volumes._ For the bottom ash, the recycled concrete <br /> ' and the recycled asphalt, which have high hydraulic conductivity, water samples were analyzed at <br /> 2, 4 and 8 pore volumes. <br /> The chemical analyses for the first extraction of the SELP test was used to determine the suite of <br /> ' chemical compounds of interest in the SGCLP test. Chemical compounds, which were either non- <br /> detect or detected at very low,&re eliminated from further testing. The SELP test is a highly <br /> ' 6 <br />
The URL can be used to link to this page
Your browser does not support the video tag.