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2018-02-05_REVISION - C1992081 (29)
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2018-02-05_REVISION - C1992081 (29)
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Last modified
2/5/2018 12:38:12 PM
Creation date
2/5/2018 9:55:43 AM
Metadata
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Template:
DRMS Permit Index
Permit No
C1992081
IBM Index Class Name
Revision
Doc Date
2/5/2018
Doc Name
Proposed Decision and Findings of Compliance
From
Hayden Gulch Terminal, LLC
To
DRMS
Type & Sequence
RN5
Email Name
JDM
Media Type
D
Archive
No
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Drill seeding will be the preferred method of planting. Broadcast or hydroseeding will be <br />employed where steep slopes or small areas limit accessibility of the seed drill. Mulching <br />will be achieved by use of a cover crop of winter wheat or barley. HGT has found that the <br />use of straw mulch introduces undesirable weedy species into the reclaimed area and will <br />thus not be required. 12.7 acres were reseeded at the facilities area in 2011. <br />Revegetation success will be monitored qualitatively through visual observations. <br />Quantitative sampling shall occur in the 3rd and 6th years after reclamation (2014 and <br />2017) for cover, species, production, and woody plant density. <br />Reclamation success will be determined by comparison with associated reference areas. <br />Cover in the reclaimed areas will be estimated by the point -intercept method and shall be <br />deemed acceptable if it is greater or equal to 90% of the cover in the appropriate reference <br />area with 90% statistical confidence. There are four approved reference areas; Dryland <br />pasture, Improved pasture, Rangeland and Meadow. The locations of the reference areas <br />are shown on Map 20-1 in the PAP. <br />Vegetation production will be measured by harvesting 1/2 m2 to 1 m2 plots in both <br />reclaimed and reference areas. If production in the reclaimed area is 90% or more of the <br />production of the associated reference area at a 90% statistical confidence, it shall be <br />deemed acceptable. <br />Neither dryland pasture nor improved pasture designations will be required to meet a <br />species diversity standard since post -operational land use will be for agricultural use. The <br />rangeland areas will be differentiated by either upland rangeland or lowland rangeland. <br />Upland rangeland will establish 5 perennial grasses with 50% or greater frequency each. <br />Three of these grasses will contribute greater than I% relative cover. A minimum of two <br />forbs will be established with an occurrence of 50% or greater. At least one shrub will be <br />established with a frequency of 10% or greater. On lowland rangeland, six grasses shall <br />be established each with 50% or greater frequency (with four of the grasses contributing <br />more than one percent relative cover each). A minimum of one forb, with greater than <br />50% frequency, will be present in the lowland rangeland type. <br />Species diversity in the reclaimed areas along the TAHR corridor will be concentrated on <br />the herbaceous component. The shrub component will rapidly reestablish naturally from <br />the surrounding undisturbed vegetation. In the low sagebrush vegetation type associated <br />with the TAHR, baseline studies identified three grasses with relative cover greater than <br />three percent. No forbs with relative cover values of three percent or more were found in <br />the baseline study. Thus, a minimum of three grasses will be established and each will <br />contribute relative cover values of three percent or greater. Each species will not exceed <br />40 percent relative cover and the total of the three species will not exceed 75 percent <br />relative cover. In addition, two forbs and one shrub will be established, but no relative <br />cover values are specified. <br />In the meadow vegetation type of the TAHR, four grasses contributed relative cover <br />greater than three percent in baseline studies. No forbs contributed relative cover values <br />W. <br />
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