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• SPECIES MEAN DENSITY (STEMS/SOM21 <br />Artemisia tridentate ssp. tridentate 17.00 <br />Atriplex canescens 0.20 <br />Juniperus osteosperma 0.03 s #/ac #/ha <br />Total 17.23 2.34 2,517 6,292 <br />Minimum sample size required (nm;~)= 2 (based on total density) <br />The sagebrush vegetation type as identified within the study area occurs on shallow soil that <br />occurred predominantly in map units 98C and 98D. The native vegetation on these soils is <br />typically apinyon-juniper dominated woodland or a shrub dominated rangeland. As evidenced <br />by the cover data, and verified by field observations, the pinyon-juniper woodland overstory <br />has been essentially removed. The removal of this overstory plus fhe level of disturbance <br />associated with livestock use and man's impact has completely altered the composition of the <br />site. Impacts include occasional chaining, and chemical spraying to reduce sagebrush plus <br />poor cattle management practices that has led to most desirable plant species being removed. <br />In evaluating the Guide for Determining Forage Condition attached to the Pinyon-Juniper <br />• Woodland Site Description, it is apparent that the sites would only warrant a poor forage <br />condition rating. Note that no woodland site index information has been provided in the Site <br />Description. The stocking rate for the sagebrush type is estimated at a low 0.09 AUM's/ac or 12 <br />acres/AUM assuming use of all grasses and the more palatable fortis. <br />As stated earlier, the sagebrush-1 type represents a remnant native community that has been <br />severely altered because of intensive agricultural land use and associated support activities. <br />Though these sites normally have apinyon-juniper tree overstory (previously discussed), these <br />have most likely been removed for fencing materials, firewood, land clearing, and from the <br />impacts of high concentrations of grazing animals. Most of the type occurs where it is <br />impractical to irrigate. The pastures are usually heavily stacked at least during part of the year, <br />resulting in a high level of animal pressure from grazing and trampling. The sites are also <br />periodically used as equipment parking, storage, or boneyard areas and winter livestock <br />feeding areas. The shallow soils, rock outcrops, and low natural precipitation, further reduce <br />the potential productivity of the site, while increasing the potential for further deterioration and <br />decreasing the opportunity for any recovery. The majority of species encountered during cover <br />• (REVISED 9/99) 2.04.10 - 74 <br />