My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
2009-08-13_PERMIT FILE - C1981019A (4)
DRMS
>
Day Forward
>
Permit File
>
Coal
>
C1981019A
>
2009-08-13_PERMIT FILE - C1981019A (4)
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
8/24/2016 3:49:45 PM
Creation date
2/23/2010 10:09:58 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1981019A
IBM Index Class Name
Permit File
Doc Date
8/13/2009
Section_Exhibit Name
Rule 2 Permits -ST
Media Type
D
Archive
Yes
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
129
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
RULE 2 PERMITS <br />The South Taylor Pit will likely have geochemical characteristics similar to the water quality in the <br />Streeter Well, the Streeter Pond, and other spoil pit aquifers (Williams and Clark, 1994), since the <br />lithology is relatively homogenous across the area. <br />The TDS in the Streeter Well is 3,750 milligrams per liter (mg/L), and TDS in pit spoil wells nearby <br />average 3,400 mg/L (Williams and Clazk, 1994). TDS concentrations in the Streeter Pond averaged 1,786 <br />mg/L in 2005 and TDS concentrations in aquifers immediately downgradient from neazby pit spoils <br />averaged 1,796 mg/L (Table 2.04.7-31). Wells located a half mile downgradient from pit spoil averaged <br />900 mg/L (Williams and Clark, 1994). <br />An estimate of TDS loading from backfilled spoils discharge into Good Spring Creek was developed <br />based on a simple mass balancing based on the projected increased TDS of the water contributing to <br />Good Spring Creek. Calwlated impacts of this groundwater into the alluvia] and surface water flow <br />regime at Good Spring Creek aze shown here. <br />A calculated spoil pit maximum dischazge estimate of 0.06 cfs enters Good Spring Creek during base <br />flow, and 0.6 cfs enters during peak flow. Therefore, a maximum of 7% of the base flow and 5% of the <br />peak flow to Good Spring Creek at the NUGSC sampling point would be contributed from the pit outflow <br />at steady state. (These percentages are approximately twice what the springs above NUGSC actually <br />contribute to the creek flows.) <br />To project the potential impact to Good Spring Creek, a weighted TDS loading between the historic low <br />flow at NUGSC (0.85 cfs and 1,050 mg/L TDS) (Table 2.04.7-34) and the projected spoils (0.06 cfs and <br />3,400 mg/L (worst case) and 1,796 mg/L (likely case) TDS; Table 2.04.7-31) was performed. <br />• Worst case (pit spoil aquifer TDS concentrations): <br />((0.85 cfs x 1050 mg/L) + (0.06 cfs x 3400 mg/L))/0.92 cfs = 1192 mg/L <br />Reasonable case (groundwater immediately downgradient from pit spoil): <br />((0.85 cfs x 1050 mg/L) + (0.06 cfs x 1796 mg/L))/0.92 cfs = 1087 mg/L <br />Thus, the base flow of Upper Good Spring Creek is calculated to have between 37 and 142 mg/L increase <br />in total dissolved solids, or an increase of between 3.5% and 13.5% caused by the projected contribution <br />from the pit springs. The increase in TDS in the base flow at Lower Good Spring Creek (with the base <br />flow of 1.8 cfs and TDS of 1187 mg/I placed into the above calculations) would be between 20 mg/L and <br />71 mg/L, or between 1.6% and 6% of TDS increase. Peak flow TDS increases would be less than these <br />values. <br />~~ <br />South Taylor/Lower Wilson -Rule 2, Page 119 Revision Date: 3/3 0/07 <br />Revision No.: PR-02 <br />
The URL can be used to link to this page
Your browser does not support the video tag.