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2009-06-02_PERMIT FILE - C1982056A (4)
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2009-06-02_PERMIT FILE - C1982056A (4)
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Last modified
8/24/2016 3:47:11 PM
Creation date
8/4/2009 10:38:32 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1982056A
IBM Index Class Name
Permit File
Doc Date
6/2/2009
Doc Name
Pages 2.05-65 to 2.05-122.1
Section_Exhibit Name
2.05 Operation and Reclamation Plans Part 2
Media Type
D
Archive
Yes
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Much of the pipeline excavation and borehole pad disturbance will occur in areas that are, or have previously been, <br />disturbed. For the remaining pipeline trench areas, consideration of soil horizon segregation must be balanced with the <br />objective of limiting overall surface disturbance. In the interest of minimising overall surface disturbance, TCC <br />proposes to not segregate and separately stockpile individual soil horizons for the pipeline trench disturbance, and <br />submits that this approach will not significantly alter soil suitability characteristics, since the differences between the <br />soil horizons is not significant over the areas to be affected by trenching. For the borehole drill-pad, individual soil <br />horizons will be segregated. Generally, to avoid contamination of the windrowed soil material, excavated material will <br />be temporarily placed on the opposite side of the disturbance area. BMP's for the construction activities include: <br />• Minimizing the area of surface disturbance <br />• Installation of the Foidel Creek crossing as a bored/jacked pipeline under the existing Foidel Creek road <br />crossing culverts (avoids new surface disturbance of the stream channel and floodplain) <br />• Completion of construction activities during the dry summer period <br />• Placement of staked straw wattles downgradient of all surface disturbance areas to intercept any surface runoff <br />and trap associated suspended solids <br />• Soil replacement and stabilization with either the standard rangeland or riparian seed mixtures (as appropriate) <br />immediately following completion of construction activities <br />Where pipeline disturbance traverses steep slopes, additional staked straw wattles will be placed on contour to limit <br />overland flow following revegetation seeding. Temporary drainage and sediment control measures will remain in-place <br />until vegetation is sufficiently established to effectively control runoff, erosion, and sediment loss. Drainage and <br />sediment control for the minor surface structures (borehole surface casing and any manhole(s)) will also utilize BMP's <br />including the vegetative filter provided by temporary vegetative stabilization, and berms and/or wattles, as appropriate. <br />As a relatively small (0.6 acres) linear surface disturbance, the additional disturbance required to either construct or <br />intercept and route runoff from the disturbed area to a sedimentation pond is not warranted. The proposed BMP's have <br />proven effective in controlling runoff and sedimentation from similar disturbances. Special design, constnzction, and <br />operational measures were taken to assure that there will be no discharge or mixing of mine water with surface <br />drainage. These measures include buried placement (approximately 5 feet below grade) of the Thickener Underflow <br />Pipelines within a secondary containment pipe within and in proximity to the Foidel Creek drainage, and installation of <br />differential pressure gauges, pump controls, and shut-off valves to provide for timely detection, shut-off, and isolation <br />of the pipeline in the event of pipeline leakage. <br />Field Geotechnical Investigations -TCC occasionally conducts field geotechnical investigations prior to, and as the <br />basis for, design and construction of engineered structures. Geotechnical investigations typically involve shallow soil <br />borings (up to 30 feet) using ahollow-stem auger, and/or excavation of shallow (up to 15 feet) test pits. For both soils <br />borings and test pits, surface disturbance is minimal (no more than 10 x 10 feet for boreholes, and 10 x 15 feet for <br />test pits) and both disturbance and subsequent stabilization occur within a timeframe of less than one day for each <br />site (typically test pit excavation/soils boring, and backfilling and leveling of the resultant small area/auger-hole, <br />occurs in a continuous sequence within the course of less than two hours for each location). The geotechnical <br />investigation activities do not involve the use of water and are conducted under dry conditions, so the potential for <br />related hydrologic impacts is negligible. All geotechnical disturbance is reseeded by broadcast seeding within 6- <br />months of disturbance, although natural revegetation typically occurs much sooner due to the limited timeframe and <br />extent of the associated disturbance. Occasionally perforated PVC pipe may be inserted in a completed borehole, <br />and the remainder of the hole backfilled with clean gravel, as a temporary piezometer installation to measure any <br />fluctuation in water-levels. This type of piezometer installation is normally very temporary (typically used less <br />than a month) and will not impact groundwater due to the shallow depth and use of natural cuttings as backfill. <br />Any piezometer installations are reclaimed by either pulling the PVC pipe and placing additional fill, or plugging <br />the PVC pipe in-place using bagged bentonite grout, then capping the installation with a minimum 1.5-foot surface <br />plug of natural clays or cement with a site marker. <br />18-Left Ventilation Shaft Installation (TR09-66) <br />Approximately 420 feet of the light-use road crosses upland areas, where road construction will involve removal of <br />any large vegetation and stripping and stockpiling of other vegetation, soil, and organic materials. Similarly, the <br />TR09-66 2.05-84.6 04/11/09 <br />
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