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Summary of Sampling Design <br />Evaluation Parameter <br />Phase II BRB-2a <br />Phase II BRB-3 <br />Reference Areas <br />Min. 15 samples <br />Min. 15 samples (to <br />Min. 15 samples (to <br />Quantitative Cover Sampling <br />(to adequacy as <br />adequacy as <br />adequacy as necessary*) <br />necessary*) <br />necessary*) <br />Quantitative Production <br />NA** <br />NA** <br />NA** <br />Sampling <br />Woody Plant Density <br />NA*' <br />NA*' <br />NA** <br />Sampling <br />NA** — Sampled in 2016 <br />NA** — Sampled in 2016 <br />NA** — Sampled in <br />Species Density Sampling <br />for informational <br />for informational <br />2016 for informational <br />purposes <br />purposes <br />purposes <br />Hypoth. testing for cover; <br />Hypoth. testing for cover; <br />3 of 4 specified tests for <br />3 of 4 specified tests for <br />Success Demonstration <br />species diversity <br />species diversity <br />NA <br />Approach <br />(Provided for <br />(Provided for <br />informational purposes <br />informational purposes <br />only) <br />only) <br />* Up to a maximum of 50 samples or use of upper 90% confidence limit after 15 samples <br />**Not Applicable — Phase II bond release is concerned with cover values only <br />Cover Sampling <br />Cover data were collected along 50 m transects using a point -intercept method in which data were <br />recorded as interceptions of a point with a plant species, litter, standing dead plant material, soil, or rock. <br />Plant material produced during the current year and still standing was tallied by species. Litter was <br />considered to be any organic material that had fallen or had begun to fall to the soil surface. Standing <br />dead was any dead plant material produced in previous years, but which was still standing and had not <br />lodged or broken off to become litter. Inorganic material greater than 1 cm in diameter was considered <br />rock. The cover sampling points were optically projected using a Cover -Point Optical Point Projection <br />Device developed by ESCO Associates. The 50 m transects were randomly located and randomly <br />oriented in the reclaimed and reference areas. One hundred points were collected along each transect. <br />At each meter along the 50 m length, points were projected 0.5 m to the right and 0.5 to the left of the <br />transect, thus minimizing trampling effects. <br />First hit interceptions were used to calculate absolute top layer foliar cover (see FIRST HIT AVERAGE <br />COVER column in data tables) by dividing the number of interceptions for a particular species or ground <br />cover type by the total number of points taken (100). First hit relative vegetation cover was calculated by <br />dividing first hit absolute cover for each species by the total first hit vegetation cover (see FIRST HIT <br />2 <br />