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PERMFILE121258
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PERMFILE121258
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Entry Properties
Last modified
8/24/2016 10:19:42 PM
Creation date
11/25/2007 9:12:49 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M2004078
IBM Index Class Name
Permit File
Doc Date
3/8/2005
Doc Name
Adequacy Review
From
DMG
To
SW TKO Joint Venture LLC
Media Type
D
Archive
No
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for such area, and the acreage of unlined pit floor. If the applicant elects to run the model both <br />with and without mitigation measures to be employed, the applicant should be specific in <br />quantifying the mitigation measures to be employed. Following such assessment, the applicant <br />will need to describe the lateral and•vertical extent of the predicted groundwater impacts and the <br />various offsite structures that will be affected, ie: high production imgation wells, shallow <br />alluvial domestic wells, deep aquifer domestic wells, and wetlands dependent on shallow alluvial <br />groundwater. <br />25. The applicant proposes a variety of mitigation measures on page 9 of the report. The <br />applicant will need to quantify the specific mitigation measures to be employed, and specify the <br />location(s) of where such measures will be employed, the length of time for the mitigation <br />measures to be employed, volumes and quality of water to be involved in the mitigation, and <br />how the appropriate volumes and quality of water will be delivered to the various mitigation <br />locations. The applicant will need to specify any structures that will need to be constructed <br />either on-site or offsite in order to deliver the mitigation water. The applicant will need to <br />specify the monitoring measures that will be employed to provide assurance of delivery of the <br />appropriate volume of water and quality of water to be used for mitigation. In addition to total <br />suspended solids and pH, water quality testing will need to include parameters such as total <br />dissolved solids, electrical conductivity, opacity, and palatability (for domestic wells). The <br />applicant will also need to submit a specific map or exhibit which shows the location(s) and <br />type(s) of mitigation measures to be employed. The applicant may also want to consider the use <br />of French Drains between the various cells <br />26. Please clarify whether the post-construction (reclamation) simulation for predicted <br />groundwater impacts considers the impacts to the groundwater system at a time when the <br />compacted clay liner is completed for all cells. If not, the applicant will need to assess the <br />potential groundwater impacts, such as mounding and/or shadowing, during such time. The <br />assessment of impacts will need to describe the lateral and vertical extent of changes to the <br />existing groundwater system and whether such impacts will intersect offsite structures such as <br />Weld County Road 6, Weld County Road 27, Colorado Highway 85, building foundations, leach <br />fields, shallow domestic wells, deep aquifer domestic wells, or high production irrigation wells. <br />(Iri the event o~"adverse mounding effects, the applicant may want to consider the installation of <br />French Drains in strategic locations.) <br />27. Please provide a specific map or exhibit showing the locations of all existing and proposed <br />water monitoring locations, whether they be wells or peizometers, whether they be on-site or off- <br />site. Please be sure to include the locations of the two (2) control points along the South Platte <br />River. The specific monitoring locations should also be identified according to ownership and <br />construction data such as diameter, total depth, and existing depth to groundwater. Although not <br />required, the Division recommends the applicant also include a description of the location and <br />horizontal distance to any other groundwater users that may cause interference of the monitoring <br />well. The location of the 2 control points along the South Platte River should also be <br />28. Please revise the table of existing water monitoring data to include all baseline water <br />monitoring data collected to date. The Division will require a full 12 months of baseline water <br />level monitoring prior to initiation of de-watering activities. In the event a full 12 month set of <br />
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