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2900 - Site Mitigation Program
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PR0542125
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Last modified
6/1/2021 2:01:14 PM
Creation date
6/1/2021 1:50:30 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0542125
PE
2965
FACILITY_ID
FA0024196
FACILITY_NAME
CONSOLIDATED TREATMENT FACILITY
STREET_NUMBER
0
STREET_NAME
GOLDEN VALLEY
STREET_TYPE
PKWY
City
LATHROP
Zip
95330
APN
19121008 19122013
CURRENT_STATUS
01
SITE_LOCATION
GOLDEN VALLEY PKWY
P_LOCATION
07
QC Status
Approved
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EHD - Public
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July 6, 2017 Monitoring Well Installation Workplan <br />samples. 8 The perforated length (well screen) shall be selected to provide samples <br />representative of the uppermost portion of the first encountered groundwater and produce <br />sufficient yield for adequate purging and sampling. The well slot size (perforation size) shall <br />be selected based on water-bearing sediment texture encountered, but shall not be smaller <br />than 0.010 inch slotted screen. All well-casing joints will be flush-threaded and watertight. <br />The bottom of the well will include a minimum 1-foot solid casing sump, sealed with either <br />a flush-threaded or slip cap (if a slip-cap is utilized it shall be secured with threaded <br />stainless steel screws). <br />3.2. Filter Pack <br />The annular spacing between the well casing and formation will be filled with clean filter <br />pack material matched to the slot size of the well screen (#212 sand, which was used for the <br />existing monitoring wells located at the site). The objective for the filter pack material is to <br />exclude the entrance of fine silts, sands, and clays into the monitoring well yet provide <br />sufficient well-yield for effective well purging and sampling. Filter pack material will be <br />nonreactive, not degrade or consolidate after placement, and obtained from clean sources <br />and properly packaged for handling, delivery, and storage. <br />Filter pack material will be placed in the well boring to a depth of 1-foot above the top of the <br />well screen. The filter pack depth will be checked, and the volume of filter pack material <br />considered for verifying that no bridging of filter-pack materials occurred. Each well will be <br />gently surged during filter-pack installation (i.e., surging will occur after the filter-pack is <br />poured into the annulus between the casing and borehole wall, but prior to the installation <br />of the transition and sanitary seals). <br />3.3. Transition and Sanitary Seals <br />The remaining annular space will be filled with a transition seal (minimum thickness of 2 <br />feet) set on top of the filter pack, followed by a neat-cement based sanitary seal to land <br />surface (minimum thickness of 10 feet). Bentonite will be used for the transition seal. For <br />depths greater than 30 feet, and where water is present in the borehole, the material will be <br />installed by use of a tremie pipe or equivalent. Where bentonite exists in the borehole in dry <br />form, potable water will be added and sufficient time allowed for the bentonite to properly <br />hydrate before placement of the sanitary seal. <br />The sanitary seal will be placed within the annular space between the top of the transition <br />seal to land surface. Sealing material shall be neat cement. Drilling fluid or cuttings from the <br />borehole will not be used as the sealing material. All water used for sealing mixtures shall <br />be potable. <br />8 Quarterly water-level and water sampling equipment and procedures are described in the <br />Consolidated Treatment Facility semi-annual monitoring reports submitted to the RWQCB. <br />HydroFocus, Inc. 6
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