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REP50946
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Entry Properties
Last modified
8/25/2016 12:55:48 AM
Creation date
11/27/2007 12:58:35 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1980005
IBM Index Class Name
Report
Doc Date
3/29/2004
Doc Name
2003 Annual Reclamation Report
From
SCC
To
DMG
Permit Index Doc Type
Annual Reclamation Report
Media Type
D
Archive
No
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U <br />SHRUB ESTABLISHMENT STUDY: <br />Technical Progress Report <br />Prepazed by: <br />M. W. Paschke <br />Department of Forest, Rangeland and Watershed Stewardship <br />Colorado State University <br />Fort Collins, CO 80523-1478 <br />December 8, 2003 <br />s <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 March 2003. More detailed <br />analyses of 2003 data will be provided in the Annual Progress Report. <br />Between April and December 2003 there were two major activities completed on this <br />project. The first was vegetation data collection at each mine from August 12 to August 14, <br />2003. The second major activity was data entry, validation and preliminary analysis, which were <br />completed in December 2003. <br />During the August vegetation sampling, each demonstration plot was sampled for <br />vegetative cover by species, bare ground, rock and litter using the same methods employed in <br />2001 and 2002. As in 2002, sampling was stratified in the fenced and non-fenced areas in order <br />to examine the effects of game exclusion. Apoint-intercept method was used to estimate cover. <br />Within each fenced (five plots) and unfenced (five plots) plot at Colowyo and Trapper (Figures 1 <br />and 2), five 50-m transects were randomly located. One of the five transects in each plot at <br />Trapper mine was stratified in mycorrhizae inoculation strips in order to test for a treatment <br />response. Cover data was collected every one meter along each transects (250 cover points per <br />plot). At the Seneca II mine, where plots are considerably smaller (Figure 3), we used three 30- <br />m transects and collected cover data every one meter (90 cover points per plot). Only three plots <br />at the Seneca R mine were divided into subplots by a fence. <br />In addition to cover sampling along these transects, we estimated shrub establishment and <br />shrub height in each demonstration plot within O.SmZ quadrants along each transect. At Colowyo <br />and Trapper, the quadrants were located every 10 m along the transect, for a total of 6.0 mZ per <br />plot. In the smaller plots at Seneca II mine quadrants were located every 10 m along each 30-m <br />transect for a total sampling area of 4.5 m2 per demonstration plot. Within each of these <br />quadrants all shrubs were identified to species and heights of individuals 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 />During the vegetation sampling, voucher specimens of plant taxa were collected for <br />positive identification and for azchival in the Restoration Ecology Lab Herbarium. Permanent <br />
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