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• Once the boundaries of the reclaimed area were identified, then using a specially prepazed <br />computer program which utilizes the random number generating capabilities of a Pentium II <br />computer, the potential transect locations were identified. These coordinates were then entered <br />into the GPS unit and the transect locations were marked in the field using either numbered <br />wooden lathe or with plastic wire pin flags. At each transect location, the direction was <br />determined by selecting a random direction based on the degrees of the compass. Once the <br />orientation of the transect was determined, then the 50-meter tape was laid out across the site. <br />Plant Cover. In this sampling effort, plant cover was evaluated by sampling a 50- meter <br />transect. Along the outstretched tape, a total often points located at five meter intervals were <br />utilized as the sample locations for the ten point frame. These points were then used as the <br />sample locations for collecting plant cover along the transect tape. At each designated sample <br />interval, an inclined metal ten-point frame, approximately one meter in height was positioned <br />perpendicular to the tape. Using a sharpened metal rod, the location was sampled at ten <br />centimeter intervals along the ten point frame. <br />Each observation was recorded as to the specific plant species encountered as the rod was <br />dropped. If no plant cover was encountered, then the observation was recorded as to the presence <br />of plant litter, rock, or whether baze ground was encountered. The 100 data points collected <br />along each transect tape were then sttmmarized into a single datum for purposes of statistical <br />evaluation. Absolute and relative plant cover, species diversity, and plant life forms were <br />determined based upon the observations collected in sampling the plant cover on each site <br />• sampled. <br />Species Diversity. The plant cover data collected along each sample transect yielded data in <br />absolute cover as determined by the percentage of hits. These cover data were then converted <br />into percent composition or relative plant cover by species based upon the total amount of plant <br />cover encountered in each sample transect. The relative importance values of plants growing on <br />the reclaimed areas as outlined in the Permit, contain standards as to the number of perennial <br />grass species which can be found growing on the reclaimed azeas to ensure that a monoculture of <br />a single plant or a few plants does not dominate the reclaimed azeas. <br />The species diversity standard in the Permit commits the Operator to establish a reclaimed plant <br />community composed of at least five perennial grasses possessing a relative importance value of <br />equal to or greater than 3 percent relative cover, with no single grass contributing greater than 40 <br />percent of the relative cover, and that these five perennial grasses cannot contribute more than 75 <br />percent of the total relative cover on the site. The permit also states that if there aze more than <br />six perennial grasses, each contributing more than three percent of the relative cover then this <br />species diversity standrsd is waived. <br />Shrub Density. Along each transect tape sampled in the Moffat Reclaimed Area shrub density <br />data was collected using a modified belt transect by sampling one meter along each side of the <br />transect tape. The right hand side of the transect tape was called Side A and the left hand side of <br />the tape was called Side B. Data collected from each side were added into a transect value which <br />• represents the number of shrubs sampled in the 100 squaze meter sample plot. These data were <br />