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REP01084
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Last modified
8/24/2016 11:30:55 PM
Creation date
11/26/2007 9:52:10 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1981019
IBM Index Class Name
Report
Doc Date
3/29/2002
Doc Name
2001 AHR & ARR Exhibit 13, Appendix 1 to Exhibit 15
From
Colowyo Coal Company
To
DMG
Annual Report Year
2001
Permit Index Doc Type
Hydrology Report
Media Type
D
Archive
No
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rx <br />5 <br />SHRUB ESTABLISHMENT STUDY: <br />Technical Progress Report <br />Prepared by: <br />M. W.Paschke <br />Rangeland Ecosystem Science Department <br />Colorado State University <br />Fort Collins, CO 80523 <br />December 13, 2001 <br />The shrub establishment study is being funded by the Colorado Division of Minerals and <br />Geology (CDMG) and conducted by Colorado State University. The study was initiated in the <br />fall of 2000 at three coalmines in northwest Colorado: Colowyo, Seneca II, and Trapper. The <br />purpose of this report is to document progress since our last report in June 2001. <br />Between June and December 2001 there were two major activities completed on this <br />project. The first was vegetation data collection at each mine from July 23 to July 25, 2001. The <br />second major activity was data entry, validation and analysis, which were completed in <br />December 2001. <br />During the July vegetation sampling, each demonstration plot was sampled for vegetative <br />cover by species, bare ground, rock and litter. Apoint-intercept method was used to estimate <br />cover. Within each plot at Colowyo-and Trapper (Figures 1 and 2), five 100-m transects were <br />randomly located. One of the five transects in each plot at Trapper mine was stratified in <br />mycorrhizae inoculation strips in order to document baseline conditions in these subplots. Cover <br />data was collected every one meter along each transects (500 cover points per plot). At the <br />Seneca II mine, where plots are considerably smaller (Figure 3), we used three 30-m transects <br />and collected cover data every one meter (90 cover points per plot). Some plots at the Seneca II <br />mine were divided into subplots by a fence. During the 7uly 2001 vegetation sampling we <br />sampled both subplots (fenced and unfenced). Plots at the Colowyo mine were also subdivided <br />by a fence treatment, but the fence was not constructed until after our sampling, therefore we did <br />not stratify our sampling by fence treatment. Fence construction at Trapper mine should be <br />completed prior to the 2002 vegetation sampling. <br />In addition to cover sampling along these transects, we estimated shrub establishment and <br />shrub height in each demonstration plot within small quadrants along each transect. At Colowyo <br />and Trapper, the quadrants were 0.25mZ and were located every 20 m along the transect for a <br />total of 6.25 mZ per plot. In the smaller plots at Seneca II mine, we used 0.5m quadrants located <br />every 10 m along each transect for a total sampling azea of 4.5 m2 per demonstration plot. <br />Within each of these quadrants all shrubs were identified to species and heights of individuals <br />were recorded. <br />At the Seneca II mine shrub tubelings were planted in September of 2000 in select <br />demonstration plots. To evaluate the success of this operation, survival of transplants was <br />quantified during the vegetation sampling. Shrub survival within each demonstration plot was <br />estimated by following rows of transplants and scoring seedlings as either alive or dead. A <br />minimum of 25% of the transplant rows within each plot was surveyed as such. <br />CF 8.5.5 2002 results 1 <br />
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