My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
2020-03-24_PERMIT FILE - C1981019A (2)
DRMS
>
Day Forward
>
Permit File
>
Coal
>
C1981019
>
2020-03-24_PERMIT FILE - C1981019A (2)
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
5/11/2020 5:24:59 PM
Creation date
5/9/2020 2:50:43 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1981019A
IBM Index Class Name
Permit File
Doc Date
3/24/2020
Type & Sequence
TR135
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.
/
92
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 />species are designated noxious weeds (`B" List taxa on the Colorado State List) with several others (e.g., <br />cheatgrass) classified as invasive weed species. Identified noxious weeds include musk thistle (Carduus <br />nutans), Canada thistle (Cirsium arvense), and houndstongue (Cynoglossum ofcinale). <br />Specific - Detailed vegetation mapping and quantitative data collection occurred by performing baseline <br />vegetation surveys (or supplemental surveys) within the study area of the Lower Wilson Mine Area. <br />Emphasis was placed on the disturbed area for quantitative efforts. Six native vegetation communities <br />and two land use types were identified from this area as follows: <br />Mountain Shrub <br />Sagebrush <br />Aspen Woodland <br />Grassland <br />Juniper Scrub <br />Bottomland <br />Cropland (land use) <br />Stock tank (land use) <br />As previously discussed, only the grassland community was completely sampled with baseline surveys <br />(ground cover, production, and woody plant density) while the remaining communities received <br />supplemental ground cover sampling. In this regard, grassland was the only vegetation type requiring <br />establishment of a reference area to facilitate development of performance criteria. Rationale for this <br />strategy was that existing data and reference areas for Mountain Shrub, Sagebrush, and Aspen <br />communities would be sufficient for this permit revision effort (see existing Colowyo permit and Table <br />2.04.10-10). <br />As previously indicated, the juxtaposition / distribution of Study Area vegetation communities, sample <br />collection locations, and reference areas are presented on Map 4B. A summary of the average ground <br />cover based on 2005 data is presented on Table 2.04.10-11 and Figure 2.04.10-3. Similarly, a summary <br />of the relative cover (composition) based on 2005 data is presented on Table 2.04.10-12 and Figure <br />2.04.10-4. Raw ground cover and production data for the grassland community and reference areas are <br />presented on Tables 2.04.10-13 through 2.04.10-18 with a summary of production data presented on <br />Table 2.04.10-19 and Figure 2.04.10-5. The raw data for grassland woody plant density are presented on <br />Table 2.04.10-20 and Figure 2.04.10-6. The principal parameters for the t-test of the means utilized to <br />validate the grassland reference areas are presented on Table 2.04.10-21. Finally, the raw ground cover <br />data collected as supplementary information for the five non -grassland communities are presented on <br />Tables 2.04.10-22 through 2.04.10-26. <br />Grassland - As indicated on Map 413, the grassland community within the Study Area occupies 16.97 <br />acres and occurs in six locations. The two grassland reference sites are located against the west Study <br />Area boundary (1.23 acres) and on the ridgeline (1.01 acres). <br />A total of 31 species were observed within the grassland community while the lower and upper reference <br />areas exhibited 29 and 42 taxa, respectively. Average ground cover of vegetation within the study area <br />was 69.93% with 0% rock, 21.07% litter, and 9.0% bare ground exposure. Dominant species included: <br />bluegrass (Poa agasizensis), thickspike wheatgrass (Agropyron dasystachyum), Western wheatgrass <br />(Agropyron smithii), tailcup lupine (Lupinus caudatus), slender wheatgrass (Agropyron trachycaulum), <br />groundsmoke (Gayophytum ramosissimum), and mountain big sagebrush (Artemisia tridentata ssp. <br />vaseyana). The number of perennial herbaceous species exhibiting between 3% and 50% relative cover <br />(composition) was determined to be 4 grasses and 1 forb. Current annual herbaceous production within <br />the Study Area's grassland community was determined to be 1,754 pounds per acre with 83% due to <br />perennial grasses and 15% due to perennial forbs. The remaining 2% was due to annual species. Woody <br />plant density based on the total count of plants within a 0.46 -acre macroplot was 509 plants per acre with <br />dominance by mountain big sagebrush and rubber rabbitbrush (Chrysothamnus nauseosus). <br />South Taylor/Lower Wilson — Rule 2, Page 52 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.