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2012-09-06_REVISION - M2008070 (21)
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2012-09-06_REVISION - M2008070 (21)
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Last modified
6/15/2021 2:25:46 PM
Creation date
9/13/2012 12:53:51 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M2008070
IBM Index Class Name
REVISION
Doc Date
9/6/2012
Doc Name
AM-01 APPENDIX D: ENVIRONMENTAL ANAYSIS - WHITE RIVER CITY GRAVEL PIT PHASE 2
From
WESTERN GRAVEL
To
DRMS
Type & Sequence
AM1
Email Name
THM
Media Type
D
Archive
No
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3.8 NOISE <br />Affected Environment: The Phase 2 site is located in a rural setting where existing noise levels <br />are primarily caused by natural sources such as wind, water, birds, insects, and the like, though <br />Hwy 64 and overhead aircraft clearly contribute to increased noise levels in this locale. The <br />nearest residence to the pit is over 1500 feet north of the Phase 2 site and lies adjacent to Hwy <br />64. This residence is owned by Sam and Virginia Love, who also own all the immediately <br />adjacent lands and are leasing their property for the Phase 2 gravel pit operation. The house is a <br />seasonal dwelling for hired help in their agricultural operations. There are no other residences <br />within 2 miles of the Phase 2 site. <br />The gravel pit operations are subject to noise pollution regulations as established by RBC <br />(Section 260 —Noise and Vibration). Specifically, noise levels generated by stationary <br />equipment may not exceed 65 dBA at the edge of the Property. Uses that exceed this level <br />during limited periods of construction are exempt from this restriction, provided that the activity <br />is carried out during daylight hours. Since the pit will only operate during daylight hours and <br />the construction phase will be limited, the Proponent will be required to meet the 65 dBA limit <br />for stationary equipment during normal pit operations. <br />Environmental Consequences of Proposed Action: Stationary equipment in the gravel pit will <br />include items such as a rock crusher, screening /washing plant, asphalt plant, concrete plant and <br />conveyor belts, all of which will generate noise. However, the pit is located a significant distance <br />from any residence and it will be initially shielded from residences and Hwy 64 by the spoils <br />stockpiles. Further, since pit operations will necessarily involve excavation, the pit will <br />gradually fall below the remaining outer structure of the natural bench (on top of which the <br />stockpiles will rest) which will further shield noise emanating from the site. <br />Mitigation: Though no data exists concerning ambient noise levels on the site, the presence of <br />the White River, prevailing westerly breezes and the proximity of Hwy 64 and regular overhead <br />aircraft flights would suggest a moderate ambient noise level in the area. The absence of towns <br />or residential structures in close proximity to the site also significantly reduces the risk of noise <br />levels exceeding the maximum level allowed by RBC regulations. However, once the site is <br />operational, noise levels should be monitored to ensure compliance with RBC standards. The <br />following noise reduction precautions will be undertaken to ensure compliance with the <br />regulation: <br />❑ Pit operations may occur during daylight hours only. <br />❑ Pit operations may only occur Monday- Saturday. <br />❑ An earthen berm will be constructed around the north side of the pit to shield noise <br />emanating from pit operations and create a buffer between the pit and the residence <br />located across the White River to the north. <br />❑ Monitoring will occur once the pit is operational to ensure compliance with RBC <br />standards. <br />Environmental Solutions, Inc. Page 24 of 30 March 09 <br />
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