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EXHIBIT 5 <br />additional cover and shrub density samples were also collected. Phase III sampling <br />corresponded to transects 31 through 50 and typically applied only to production transects, but <br />in instances where sample adequacy was not achieved for plant cover, then additional cover <br />and shrub density samples were collected. <br />When sample adequacy was determined to be just a few more than the minimum of 15 cover of <br />30 production transects, additional transects were usually sampled sequentially until sample <br />adequacy was achieved. For the Greasewood Reference Area, after 13 cover transects had been <br />sampled, sample adequacy was found to equal 26.2 transects. After 19 transects had been <br />sampled, sample adequacy was calculated to equal 50.8 transects. Since sample adequacy was <br />increasing with each additional number of samples collected, evidence suggested that it would <br />be necessary to sample to the maximum number of transects (50) and there was no need to <br />periodically stop and reevaluate the data and determine whether sample adequacy had been <br />achieved. However, after 35 transects had been sampled, from randomly located sample sites, <br />and sample adequacy was calculated and found to equal 32.4 transects. Since sample adequacy <br />was achieved, sampling stopped. On this site, the subsequent transects were sampled based <br />upon which transect was located closest to the end of the transect being sampled. Given the <br />fact that the transect location and bearing was randomized, the location of the closest transect to <br />this point is considered to be random as well. Examination of Map 2.04.10 -3, Rhino Energy <br />LLC, Fruita Unit Train Loadout - Greasewood Reference Area, clearly documents that the <br />transect locations were randomly located and sampled on this site. Therefore, there was no bias <br />due to sequence of how the sample transects were sampled. <br />The DRMS regulations at Section 4.15.11 (1) states that "all aspects of the vegetation sampling <br />program must be conducted to ensure a reasonable, unbiased estimate of the appropriate <br />population parameter. Consistency in sampling shall be required in comparison between the <br />reclaimed area and the undisturbed area. Both random and systematic sampling designs are <br />acceptable." The Vegetation Guideline on page 5 states "it is important that unbiased samples <br />be obtained. In general, the Division recommends that transect samples be randomly located." <br />There is an abundance of documentation clearly showing that a "systematic sampling" <br />approach yields data that is more biased and certainly not less biased as is being suggested by <br />the DRMS and the most unbiased data is obtained from a completely randomized sampling <br />approach. Similarity, if a "random" sampling effort is used to determine transect locations but <br />then a "systematic sampling" approach is used to sample these coordinates, the end result <br />would yield more not less sampling bias. By implementing a two -stage "random sampling <br />approach," such as was used herein, by firstly selecting purely random coordinates and then <br />secondly, by randomly sampling those coordinates or transects in a random manner, would <br />yield less unbiased data than would a two -phase sampling approach that uses random sampling <br />during Phase I and a systematic sampling approach during Phase II <br />In a classic statistical treatise, written by D. R. Cox entitled "Planning of Experiments" <br />published by John Wiley & Sons in 1958, "randomness" is defined as a "situation where there <br />