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points per transect. Random even numbered intervals were sampled on the right-hand side of the <br />tape and odd -numbered intervals were sampled on the left-hand side of the tape. This process <br />yields a potential cover sampling area of approximately one -hundred meters in size. <br />Each time the rod was dropped, the plant species encountered by the rod was recorded. If no plant <br />cover was encountered, then the observation was recorded as to the presence of litter, rock, bare <br />ground, lichens or cryptograms. Plant material produced in the 2013 growing season which was <br />still attached to the plant was considered as living plant material and all plant material produced in <br />prior years and which was dead or which had fallen to the ground was considered to be litter. The <br />100 data points collected along each cover transect were summarized into a single datum for <br />purposes of statistical analysis. Absolute and relative plant cover, along with the plant life forms <br />were determined based upon the plant cover data collected. <br />As outlined in the discussion of the revegetation success standards for reclaimed plant cover in the <br />Southfield Permit, the weighted average cover of the three reference areas located at the <br />Southfield Mine were compared to the weighted average cover from the reclaimed areas. As <br />recommended by the CDRMS in their Bond Release Guideline, cover of all annual and biennial <br />plants were excluded from the "allowable plant cover" revegetation success standard. In addition, <br />EFCI's consultant was informed during pre -consultation meetings with the CDRMS, that no state <br />listed noxious weeds could be counted towards the "allowable plant cover " revegetation success <br />standard. Therefore, in this analysis, the "allowable plant cover" revegetation success standard, <br />consisted of only perennial plant cover, minus all state listed noxious weeds and all annuals and <br />biennials. <br />Forage Production. Forage production in this evaluation included only perennial herbaceous <br />species. A simple random sampling approach was used to collect forage production along <br />randomly located transects. In many instances the forage production transect was the plant cover <br />and shrub density transect. Along each production transect, three randomly located one-quarter <br />square meter circular plots were located along the transect tape and clipped at ground level. <br />As directed by the CDRMS relative to other final revegetation sampling efforts, the production <br />plots were clipped by life forms for perennial grasses and perennial forbs for the reference areas <br />and on the reclaimed areas. As recommended in the CDRMS Vegetation Guideline, Bond <br />Release Guideline and CDRMS Regulations, annuals, biennials, and noxious weeds identified in <br />Table 1, Southfield - Plant Species List, were not harvested in the forage production sampling. <br />For each area sampled, a minimum of 30 forage production transects were collected as required <br />by the CDRMS regulations pertaining to the final bond release sampling. Following clipping, the <br />harvested plant materials were dried in a drying oven at 105 degrees C until a constant dry weight <br />(+/- 0.1 gram) was obtained. In the discussion of results, these forage production data are <br />presented in to grams per quarter square meter and pounds per acre. <br />Species Diversity. The Southfield Mine Permit contains species diversity revegetation success <br />standards relating only to warm season grass species. In order to standardize the definition of <br />what species are warm season grasses, we followed the recommendation made by Ms. Janet Binns <br />and used the USDA Plants website site to identify warm season (C-4) grass species which are <br />identified in Table 1, Southfield - Plant Species List. <br />