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COMPLIANCE INFO_PRE 2019
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PR0538355
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COMPLIANCE INFO_PRE 2019
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Last modified
12/19/2024 11:54:18 AM
Creation date
9/17/2020 8:14:40 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2200 - Hazardous Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
PRE 2019
RECORD_ID
PR0538355
PE
2227
FACILITY_ID
FA0022165
FACILITY_NAME
LATHROP WATER TREATMENT FACILITY / CORP YARD
STREET_NUMBER
2112
Direction
E
STREET_NAME
LOUISE
STREET_TYPE
Ave
City
Lathrop
Zip
95330
APN
19816003
CURRENT_STATUS
01
SITE_LOCATION
2112 E Louise Ave
QC Status
Approved
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KBlackwell
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EHD - Public
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H2O Urban Solutions, Inc. Page 2 <br /> Discussion <br /> The City continuously seeks to minimize the cost of treating and delivering water. Strong <br /> political and legal forces limit the City's authority to increase water rates, so stabilizing water <br /> program costs by improving existing operations is a necessity. Solids handling at the LAWTF has <br /> proven more costly than originally expected when designed. The labor and energy costs to <br /> operate the existing filter press are approximately$65,000 annually, since the process is not <br /> fully automated. Alternatives for dewatering solids include other mechanical methods (i.e. belt <br /> press, centrifuge), though use of these may not result in significant reductions in cost. Non- <br /> mechanical processes (i.e. drying beds) have the greatest potential to minimize solids disposal <br /> costs. <br /> The advantages and disadvantages of drying beds for solids dewatering (as opposed to the <br /> current filter press) are provided below. <br /> Advantages Disadvantages <br /> • Passive (less labor) • Large Area or "footprint" needed <br /> • No energy used for dewatering • Not effective in winter/spring <br /> • No moving parts, machinery, or • Requires more time for dewatering <br /> regular maintenance • Requires additional chemical use to <br /> • No replacement or reconditioning condition solids prior to spreading <br /> required <br /> Drying beds are generally a preferred solids drying process for most agencies located in the <br /> areas where the weather is conducive to solar drying, but often space limitations restrict their <br /> use. However,the LAWTF facility has adequate, undeveloped areas for placement of drying <br /> beds. The bed size depends on the solids content of the filter backwash, so concentrating the <br /> solids by pretreating with lime or other coagulant is necessary for reasonable bed size and cost. <br /> Conditioning solids with chemicals is a common practice, and promoted by the U.S. EPA. 1 <br /> A disadvantage of drying beds specific to the City is the cost to change its solids handling <br /> process. Implementation of dying beds will require capital costs to construct the beds and <br /> modify certain existing process (i.e. remove the filter press, re-route piping, modify existing <br /> chemical systems, etc.). Though the drying beds are not complex (a bed of sand placed over <br /> gravel in a concrete basin), the size of the beds result in a significant capital cost. As previously <br /> mentioned, the size of the beds can be significantly reduced if the solids are conditioned prior <br /> to placement on the beds. Adding lime to the solids will enhance the dewatering process, and <br /> assumed to be part of drying bed facility modifications. <br /> The system envisioned for LAWTF would include the sand drying beds,followed by evaporative <br /> or evapotranspirative elimination of the drained water (see Figure 1). Water drained from <br /> solids placed in the drying beds will be held in concrete lined basins. If the chemical <br /> characteristics are acceptable, the water may be diverted to the existing earthen-lined <br /> 1 Design Manual, Dewatering Municipal Wastewater Sludges, U.S. EPA,Office of Research and Development. <br />
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