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I' <br /> <br /> <br />I' <br />I' <br />I' <br />I <br />i~ <br />Re u s <br />Stem density and survival. Overall, stem density typically ranged from 4079 to 607 stems per <br />acre across all sites with a standazd deviation of approximately f26% (Table A-2). High <br />standazd deviation is typical of shrub density estimates due to the clumped nature of plantings. <br />Site 97-1D contained the most dense stands of shrubs with an estimated 4079 stems per acre. <br />Substantial recruitment of seeded shrubs or from the seed bank appears to be the source of these <br />shrubs. Sites with the lowest stem densities are 96-1, 95-4b, and 97-1b and range from 607 to <br />842 stems per acre. These sites were planted indifferent years and on different aspects. <br />Common site factors which may effect density are not present. Both 95-4b and 97-1b have <br />generally good survival and appear have been planted at a lower density. Site 96-1 survival is <br />poor with survival ranging from 13 to 26%. During 1997 monitoring, this site was noted as <br />having 65% of plants browsed. Low survival is most likely the result of this intensive browse <br />damage. <br />Percent survival varied widely by species. Gambel's oak survival was excellent and ranged from <br />70 to 90%. Chokecherry and serviceberry survival ranged generally from 32 to 90%. Bitterbrush <br />(Purshia tridentata), Wood's rose (Rosa woodsii) and Snowberry (Symphoricarpus oreophilus <br />did quite poorly. Bitterbrush survival was 25% although this species only occurred in one plot <br />and the sample size was relatively small. Wood's rose and snowberry survived poorly in all <br />planting units with few exceptions. In plots 96-1 W, survival of Wood's rose (IS%) and <br />snowberry (30%) dropped from 61 % and 50% respectively observed during previous <br />monitoring. In a similar pattern on site 96-1, survival of Wood's rose (13%) and snowbeny <br />(18%) dropped from 26% and 45% observed during previous monitoring. Both of these sites had <br />exceptionally high rates of herbivory during 1997. Estimated herbivory on 96-1 and 96-1 W were <br />65% and 66% respectively during 1997. Browse damage appeazs to substantially impact survival <br />of these species at the seedling stage. <br />In several instances, percent survival exceeded 100%. Survival percentages are complicated by a <br />number of factors in plots 97-1 c, 97-1d, 97-2, and 97-1 W. Possible complicating factors aze : 1) <br />seedbank recruitment; 2) seeding of shrubs onto planted sites; 3) resprouts of planted shrubs; and <br />4) miscounts by field technicians. On planting units 97-Id and 97-1 W, a substantial number of <br />serviceberry, bitterbrush, and snowberry seedlings were noted as establishing from seed. The <br />source of this seed is unknown. Seed could be contained in the seed bank or be result of seeding <br />efforts. Regazdless, germination and establishment of seedlings could greatly bolster the number <br />of stems on these sites. Sites 97-2 and 97-1c also contained Wood's rose and snowberry <br />seedlings which could not be accounted for by live planting. The snowberry appeazed to have <br />originated from seed while origin of Wood's rose given its fast growth rate could not be <br />determined. Resprouting of browsed or damaged shrubs previously counted as dead is a distinct <br />possibility for all plots, although this would not be expected to increase survival estimates <br />substantially. Miscounts by field technicians is also a possibility with minor implications for <br />altering survival estimates. Seeding of shrubs and seedbank recruitment aze likely <br />underestimated as potential sources of stems. <br />