My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
2021-12-22_PERMIT FILE - C1981019A
DRMS
>
Day Forward
>
Permit File
>
Coal
>
C1981019
>
2021-12-22_PERMIT FILE - C1981019A
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
5/18/2022 8:52:47 AM
Creation date
5/17/2022 7:25:16 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1981019A
IBM Index Class Name
Permit File
Doc Date
12/22/2021
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.
/
90
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 />established" South Taylor Sagebrush Reference Area (ST -SRA) for eight reasons as follows. <br />First, the C -SRA is readily accessible (located near the Administration Building) and should remain <br />accessible during the life -of -mining. The ST -SRA is located high in the rugged terrain south of the <br />Lower Wilson project area where access may be intermittently or permanently interrupted by mine - <br />related activity. <br />Second, the C -SRA has been measured more frequently over the past several years and therefore, presents <br />a more extensive historic data -base. C -SRA data indicated for the third point below come from the 2005 <br />sampling effort from the C -SRA and new tables providing these data have been provided as Tables <br />2.04.10-28 through 2.04.10-32. <br />Third, an analysis of data indicates that the C -SRA more closely resembles the South Taylor Study Area <br />than the ST -SRA with respect to dominant species and lifeform composition. Big sagebrush (Artemisia <br />tridentata) comprises 28% and 27% of the C -SRA and South Taylor Study Area's vegetation <br />composition, respectively, while comprising only 13% (less than half) of the ST -SRA vegetation. To the <br />contrary, deciduous shrubs comprise twice (29%) of the ST -SRA vegetative composition but only 17% <br />and 5% of the Study Area and C-SRA's composition. And finally, perennial grasses comprise only 24% <br />of the ST -SRA vegetative composition while comprising 32% and 40% of the Study Area and C-SRA's <br />composition. In this regard, the C -SRA would be considered a better ecological target for reclamation <br />attempting to re-establish sage and grassland communities. <br />Fourth, (and of elevated significance) it appears the ST -SRA is located in an ecotone between the more <br />mesic mountain shrub community type and the mesic sagebrush community type based on composition <br />data, narrative descriptions, and photographs presented by Harrier in his 1984 report. Harrier describes <br />this area as the sagebrush-snowberry phase, which exhibits deeper more productive soils than the <br />sagebrush - wheatgrass phase more typical of most Colowyo disturbances. The ST -SRA is surrounded <br />and being invaded by mesic mountain shrub that will most likely continue to expand into, and replace, the <br />sagebrush community as succession progresses. This observation is also verified by review of 2005 aerial <br />imagery of the communities within and adjacent to the ST -SRA. Over the 21 years since the original <br />mapping, the area that could be segregated as sagebrush has substantially diminished in areal extent. To <br />the contrary, the C -SRA is located in a large expanse of the sagebrush — wheatgrass phase with occasional <br />patches of the mountain shrub community in draws and depressions and the more shallow -soiled juniper <br />scrub community in rock outcrop areas. Very few compositional changes in the dominant taxa are <br />expected in this area as succession progresses. Furthermore, this sagebrush-wheatgrass phase of the sage <br />community is a more appropriate ecological comparator given the similarity of this area's underlying soil <br />profile with the constructed growth media profile of Colowyo's reclaimed land. <br />Fifth, based on statistical testing per current Division guidelines, the ST -SRA is not comparable to the <br />South Taylor Study Area for either cover or production (see Table 2.04.10-27) but is eligible as a <br />reference area only because values are higher than those found in the study area. The sampling adequacy <br />and equivalency procedures used by Harrier in 1984 were more liberal for such evaluations. <br />Sixth, a review of data presented on Figures 2.04.10 — 7 and 8 indicated that Harrier's 1984 data for the <br />ST -SRA is substantially elevated over all other comparable sagebrush data sets from the area, but most <br />importantly, the values are 25% and 50% higher than the surrounding South Taylor Study Area during the <br />same year for cover and production, respectively. Some of this difference with data sets from other years <br />can be explained by an analysis of precipitation. However, the strong differences between the ST -SRA <br />and the study area reduce the defensibility of this reference area as an appropriate comparator. <br />Seventh, the sagebrush -grassland ecotype is the main ecological community that will be targeted by <br />South Taylor/Lower Wilson — Rule 2, Page 57 Revision Date: 4/7/17 <br />Revision No.: RN -07 <br />
The URL can be used to link to this page
Your browser does not support the video tag.