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RULE 4 PERFORMANCE STANDARDS <br /> followed depending on the resulting community that evolves (see Section 4.15.7 above). For <br /> grassland testing the weighted average approach (Rule 4.15.7 (4) (b)) will be utilized where <br /> reference area data and revegetated area data are"weighted"(each combined into single values for <br /> comparison) based on the proportional acreage of pre-mine communities within the disturbance <br /> area footprint. Testing will then follow procedures detailed under Rule 4.15.11 (2)with preference <br /> being given first to subsection (a) [direct comparison], second to subsection (c) [reverse-null <br /> testing], and third subsection(b) [classic t-test]. <br /> For "targeted" Post-2008 sagebrush steppe revegetation (targeting the rangeland land use <br /> subcomponent of wildlife habitat), herbaceous cover will be considered adequate for final bond <br /> release if it is not less than 70%* of the sagebrush reference area's herbaceous cover with a 90% <br /> statistical confidence utilizing a standard students statistical t-test comparison of the means. If <br /> necessary, a reverse-null hypothesis testing procedure may be utilized in accordance with <br /> procedures detailed in Rule 4.15.11 (2) (c). As allowed under Rule 4.15.8 (3) (ii), relaxation of <br /> the herbaceous cover standard for areas targeting wildlife habitat post-mining land uses is designed <br /> to compensate for revegetation techniques(prescribed ecological reclamation approach)that must <br /> discourage grasses to encourage shrubs in the post-revegetated community. For "evolved" post- <br /> 2008 sagebrush steppe revegetation,the grazingland cover standard will be maintained. <br /> A higher percentage of herbaceous cover is not practical or desirable for the following reasons: <br /> 1. It is well documented that in mined-land reclamation the establishment of shrubs to reach <br /> bond release levels has proven to be very difficult. Perhaps the most detrimental condition <br /> affecting shrub establishment is the competition from herbaceous vegetation. At a <br /> minimum herbaceous cover, levels should be less than the premining condition. If the <br /> herbaceous levels to be obtained were set higher than the premining condition, the ability <br /> to achieve bond release levels for shrubs would be most adversely affected. Higher levels <br /> of herbaceous cover would adversely compete against woody vegetation and hinder its <br /> successful establishment. <br /> 2. In mined-land reclamation, it is important to have adequate herbaceous cover to provide <br /> for erosion control. The reference areas at Colowyo indicate herbaceous cover values of <br /> 41.8%and 30.17% for the mountain shrub and sage reference areas,respectively. <br /> Colowyo is located at approximately- 7,300 feet in elevation. The period of highest <br /> potential erosion occurs in the springtime during snowmelt. At this time of year, erosion <br /> control is provided almost exclusively by herbaceous vegetation. Erosion control by shrub <br /> cover is virtually insignificant since the potential erosion occurs from snowmelt rather than <br /> raindrop impact. Therefore, if pre-mining levels of herbaceous vegetative cover can be re- <br /> established, logically a comparable level of erosion control will be achieved. <br /> The value of 70%has been selected given the following rationale: 1)herbaceous competition must be significantly restricted to facilitate emergence <br /> and erowth of shrubs as indicated under Rule 4,15.11(3)(ii)-_21 the original value is 90°/n_31 a value of 50%seems too low to adeau=ly control <br /> erosion;4)by regulation(4.15.11 (3)(a))a reduction to 70%is allowed for one of the demonstrations for revegetation success for woody plant <br /> density;and 5)70°/o of the herbaceous material in a native reference area should be adequate to control erosion on slopes 10%or less. <br /> Rule 4 Performance Standards 4-65 Revision Date: 11/18/19 <br /> Revision No.: MR-211 <br />