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<br /> <br />2.0 Methods. . <br />2.8 Sample Adequacy. . <br />nR = reference area sample size <br />sA = affected area sample variance <br />sR = reference area sample variance <br />dA = degrees of freedom, affected area <br />dR = degrees of freedom, reference area <br />The t-value so calculated is compared to a two tailed t-value at <br />95% confidence (a = 0.05) for (nA + nR)-1 degrees of freedom from a statis- <br />tical table. If the calculated t value is less than or equal to the table <br />t value, the reference and affected areas are deemed "comparable" for the <br />parameter being considered. <br />2.9 Time of Sampling <br />All quantitative cover, production, and density data were collected <br />in August and early September 1982. <br />2.10 Species Diversity <br />Species diversity was calculated for each affected area and refer- <br />ence area vegetation type by reviewing the cover data to determine which <br />plants had a relative cover of 3 percent or greater. These species were <br />then grouped by major life-farm. Calculations were based on first-hit data. <br />2.11 Range Condition and Carrying Capacity <br />Range site descriptions from the Lentral Desertic Basins, Mountains <br />and Plateaus land Resource Area of the Soil Conservation Service (SCS 1971) <br />were reviewed along with soil and vegetation (cover and production) infor- <br />mation from the 1982 field program. Those range sites most applicable to <br />the study area were selected. The percent of original vegetation composition <br />present in each range site was estimated based on the 1982 field cover and <br />production data. The appropriate range condition of each range site was <br />then estimated based on the percent of original vegetation composition <br />present as follows: 0 to 25 percent--"poor"; 25 to 50 percent--"fair"; <br />