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2021-09-03_PERMIT FILE - C1981019A (8)
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2021-09-03_PERMIT FILE - C1981019A (8)
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Last modified
5/10/2023 2:22:44 PM
Creation date
4/27/2022 2:26:16 PM
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Template:
DRMS Permit Index
Permit No
C1981019A
IBM Index Class Name
Permit File
Doc Date
9/3/2021
Doc Name
Permits
Section_Exhibit Name
Volume 15 Rule 2
Media Type
D
Archive
Yes
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RULE 2 PERMITS <br /> density of woody plant species; and 4) species composition. The potential presence or absence of <br /> threatened and/or endangered plant species was also assessed (see section 2.04.11(5). Qualitative <br /> information concerning minor vegetation types was also included. The inventory resulted in a <br /> comprehensive inventory of vegetation communities that exist in the Collom permit expansion area. <br /> Six major vegetation community types were identified within the Vegetation Study Area: 1) Aspen, 2) <br /> Bottomland, 3) Grassland, 4) Juniper Scrub, 5) Mountain Shrub, and 6) Sagebrush. Four minor <br /> vegetation community types/land uses were identified: 1) Improved Pasture, 2) Cultivated Land <br /> (Cropland), 3)Disturbed Areas,and 4)Wetlands. Within the six major types,descriptive sub-types(mesic <br /> or xeric)were also identified in the mountain shrub and sagebrush types. <br /> Methods — The identification and delineation of vegetation community types within the Collom permit <br /> expansion area was initiated through the use of 2002 true-color aerial imagery with approximately 1.5- <br /> meter resolution. Vegetation communities were mapped based on photographic signatures to a polygon <br /> size of approximately one acre using ArcGIS software. On-ground vegetation surveys conducted during <br /> the summer of 2005 used this preliminary delineation to ground-truth, correct, and refine community <br /> locations and boundaries. <br /> Field corrections were then used to re-delineate the vegetation communities within the Vegetation Study <br /> Area, as well as within a two-mile Wildlife Study Boundary external to the Vegetation Study Area, to a <br /> polygon size of approximately 0.25 acre. This post-sampling delineation was performed using 0.5-meter <br /> resolution color-infrared remote sensing imagery exposed in September of 2005. <br /> Sample Layout — Fifty sample sites (or 15 to 30 for reference areas) were systematically selected (in an <br /> unbiased manner) within each vegetation community type. Sample locations were selected by placing a <br /> nested grid over each type on a computer generated map. Intersections throughout the grid representing <br /> sample points were utilized for the 2005 field effort. Modifications to sampling point were made in the <br /> field as necessary; as preliminary mapping efforts made prior to ground verification were used in the <br /> sample point selection process. Community identification was refined, and some original delineations <br /> were combined based upon observed field characteristics. Grassland and sage reduction areas were <br /> combined under the grassland category and riparian, wetland, and other bottomland types were combined <br /> under the bottomland category. The nested grid sampling design allowed the original grid dimension to <br /> be changed(100 x 100, 200 x 200, 300 x 300) if additional or fewer samples were needed for a particular <br /> vegetation type. If sample points landed within small, unmapped inclusions of another type (e.g. a patch <br /> of sagebrush within a mountain shrub designation), the sample point was utilized, but later labeled to <br /> reflect the actual community found to occur on the ground. <br /> Once sample locations were located in the field, the vegetation parameters of percent ground cover, <br /> production, and woody plant density were collected. Data collection techniques for each parameter are <br /> detailed below. <br /> A detailed description of the sample layout protocol applied during 2005 baseline vegetation evaluations <br /> is provided in Exhibit 10, Item 6. Sampling point locations are displayed on Map 4. <br /> Ground Cover — Determination of ground cover was achieved by placing 10-meter point-intercept <br /> transects at each sample location. At each one-meter interval along the transect, a "laser point bar" was <br /> situated parallel to, and approximately 1.5 meter vertically above the ground surface. This equipment was <br /> used to record a set of 10 readings as hits on vegetation (by species), litter, rock (>2mm), or bare soil. <br /> This resulted in a total of 100 intercepts per transect or one percent cover per intercept. Second hits, <br /> where strata overlap in the downward projection of the hit, were also recorded to complete species <br /> Collom—Rule 2,Page 45 Revision Date: 12/20/19 <br /> Revision No.: TR-135 <br />
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