My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
REP26151
DRMS
>
Back File Migration
>
Report
>
REP26151
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
8/24/2016 11:57:28 PM
Creation date
11/27/2007 4:25:21 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1981019
IBM Index Class Name
Report
Doc Date
3/25/2004
Doc Name
2003 AHR & ARR Section 9 Part 2
Permit Index Doc Type
Annual Reclamation Report
Media Type
D
Archive
No
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
73
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
2.6.4 Fire Areas <br />Three fire units (FA001, FA002, and FA003) were seeded in 2002 and sampled in 2003 after one <br />growing seasons. The three fire areas were accidentally bumed in the summer of 2002 and seeded in <br />the fall of 2002. Seedling emergence data revealed that there was a range from 1 to 1.53 perennial <br />seedlings per square foot. An average density range of 0.60 to 1.25 was attributed to perennial grasses, <br />while a 2nge of 0.10 to 0.27 seedlings per square foot were from perennial forts and 0.0 to 0.13 <br />seedlings were attributed to shrubs. Annual brumes exhibited a range of 0.8 to 11.50 plants per square <br />foot and annual forts, especially Russian thistle, ranged from 1 to 2.63 seedlings per square foot. Woody <br />plant density was determined from these "emergent" quadrats. Density ranged from zero shrubs per <br />acre in FA001 to over 5,660 shrub seedlings per acre in FA003. There is a reasonabh/ good take by the <br />seeded grasses in the fire areas and the bumed Gambel oak and serviceberry are resprouting well. <br />Dense patches of noxious weeds are oaasionally found where the fire areas meet the berms along the <br />haul roads, and these areas should receive treatment with herbicide to prevent a problematic infestation. <br />Annual brumes are dense in places within the fire areas (especially FA002). Widespread use of the <br />herbidde Oust or Plateau for contro4 is recommended in FA002 and spot use is recommended for FA001 <br />and FA003. <br />• 2.7 Summary by Year <br />2.7.1 1996 Revegetation <br />Charts 8 and 9 and Tables 10 and 11 exhibit the average cover and wmposition of vegetation found <br />on the five units (EP028, EP029, WP004, S16009, and 516010) that were seven years of age when <br />evaluated in 2003. All of these units have progressed well toward bond release criteria with the <br />exception of the woody plant density criterion. Perennial cover (43.0% to 58.6%) and production (725 to <br />2,900 pounds per acre) should readily pass comparisons with the reference areas, while the diversity <br />standard of 3 perennial grasses and 1 perennial fort with between 3% and SO% relative wver has been <br />met by all but one unit (S16009 presently, has insufficient perennial fort cover to achieve at least 3% <br />relative cover). Woody plant density in all of the 1996 revegetation units is low ranging from 20 to 265 <br />woody plants per acre, which is far below the present standard of 90% of 1,000 woody stems per acre. <br />See Appendix AA -Section 7.4 for a discussion on options and recommendations with regard to woody <br />plant density. Elevated levels of annual bromes are present in only one unit, EP028. The patches of <br />annual bromes in this unit should be monitored to gauge if they are expanding or shrinking. If <br />monitoring reveals they are expanding, use of the herbidde Oust or Plateau is recommended. Dominant <br />taxa found in 1996 revegetation are intermediate wheatgrass, thickspike wheatgrass, smooth brome, <br />xenrcecott Energy Co. ~ C°lowyo Anne Page 76 Revegetatlon Monitoring -2003 <br />
The URL can be used to link to this page
Your browser does not support the video tag.