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collected in 2009. These data are referred to as the RIVE 2005 data. These data are included only <br />to document historic trends and not in any way to satisfy any of the required bond release <br />vegetation sampling requirements. <br />Statistical Analysis of Data. As required by the Division's regulations, it is not necessary to <br />achieve sample adequacy for reclamation monitoring corresponding to the Phase III bond release <br />sampling efforts provided that the success standard has been achieved, the reverse null <br />hypothesis is used and that the required minimum number of transects have been sampled. <br />According to the Regulations found in Rule 4.15.11 (2), a minimum of a least 15 transects for <br />cover and 30 transects for production and shrub density must be collected even if sample <br />adequacy is achieved with fewer transects. Therefore, all of the data collected in this evaluation <br />were analyzed for sample adequacy in order to determine whether the Division's requirements <br />had been satisfied. The sample adequacy formula contained in the DRMS regulations was used, <br />wherein a precision of 0.10 was used for cover and production and 0.15 for shrub density. <br />On all of the areas sampled, the field data were analyzed in terms of "total plant cover" to <br />determine whether sample adequacy was achieved prior to leaving the site being sampled. On <br />the reclamation blocks and reference areas sampled for production and shrub density, a <br />minimum of 30 samples were collected and the data analyzed for sample adequacy before the <br />reverse null approach was applied to determine revegetation success. <br />According to previous written guidance received from Mr. Dan Mathews and Ms. Sandy Brown <br />of the DRMS, if sample adequacy is achieved on both the reclaimed and reference areas, and the <br />reclamation sample mean exceeds 90% of the standard, no statistical testing is required and <br />revegetation success can be demonstrated by direct comparison. If sample adequacy is not <br />achieved for one or both of the reclaimed or reference areas sampled, but the reclaimed sample <br />mean exceeds 90% of the approved standard, then the reverse null statistical hypothesis, as <br />found in the CDRMS regulations can be used. <br />Results <br />Field Sampling Dates. Most of the data utilized in this evaluation were collected between July <br />21 -25, 2009. Subsequent evaluation of the data revealed that some additional cover transects <br />were needed, so the sampling was finished on August 29, 2009. At the time of the field <br />sampling, all of the plants were actively growing and it is believed that the sampling was <br />performed close to the period of optimum plant growth, when the plant cover and production <br />were near their peak. A total of 75 plant species were identified in the 67 cover transects and 60 <br />shrub density transects sampled in this evaluation. A list of all of the 93 plant species <br />encountered in the field sampling efforts in this evaluation is presented in Table 1, Kerr Mine <br />Plant Species List, <br />Sample Adequacy. A statistical summary and analysis of the data collected to characterize the <br />plant cover, production, and shrub density is presented in Table 2, Man Mine - 2009 Statistical <br />Summary and Sample Adequacy Calculations. This table documents that a sufficient number of <br />