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COMPLIANCE INFO_2009-2016
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4400 - Solid Waste Program
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PR0400042
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COMPLIANCE INFO_2009-2016
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Last modified
4/16/2024 10:27:44 AM
Creation date
7/3/2020 11:18:10 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
2009-2016
RECORD_ID
PR0400042
PE
4452
FACILITY_ID
FA0000120
FACILITY_NAME
OLIVERA FOOD INC
STREET_NUMBER
944
STREET_NAME
BOWMAN
STREET_TYPE
RD
City
FRENCH CAMP
Zip
95231
APN
19128019
CURRENT_STATUS
01
SITE_LOCATION
944 BOWMAN RD
P_LOCATION
99
P_DISTRICT
003
QC Status
Approved
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SJGOV\cfield
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FilePath
\MIGRATIONS\SW\SW_4452_PR0400042_944 BOWMAN_2009-2016.tif
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EHD - Public
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0512612009 13:27 9518273349 DOUGLAS KUNEV PAGE 10/14 <br /> r E <br /> I <br /> maximum "full" level and an emergency spillway) should be <br /> provided between the settled embankment height and the <br /> bottom sof the emergency spillway. <br /> 'iW_o�StaQA IaQeQ19S <br /> Two-stage lagoons (Figure 2) require more total volume than <br /> sirA916-Mage lagoons, but effluent from the second stage <br /> will be of higher quality which is desirable when effluent <br /> is to be recycled for flushincr buildings. While -effluent <br /> May be recycled from well-designed primary lagoons, flushing <br /> water will contain fewer solids and disagreeable odors, will <br /> be less Carroaive, and the threat of d"Seame transmission <br /> sill be less when recirculated from a second-stage lagoon. <br /> Two-stage lagoons provide a number of advaritages over single ' <br /> anaerobic lagoons. However. in poultry apldlications, more <br /> than twa units in sariress is rarely benefi.ciaj. The first <br /> stage should be planned to contain the minimum design <br /> treatment vole: for an anaerobic unit, and should be <br /> maintajned at a constant depth using an overflow devise into <br /> the second stage. Design of the send-stage will depend on <br /> intandAd use. Faux ebloratives for sacnrid-atasja units are <br /> Possible: (1) source Of water for flusshinc}, (2) further <br /> treatment of wastes, (3) holding of effluent for land <br /> disposal, (4) a armbination of the above.) <br /> Exact design of second-stage units for options 1. 2, and -a. <br /> would best be based on analysis of wastewater which each <br /> unit will receive. This information will iarely be <br /> available for individual farm situations, ]hut a rule-of- <br /> thumb is ordinarily sufficient. A second-stage lagoon <br /> should be made large enough to contain an *ultry wastes to <br /> be loaded into the total system (first- and second-stages) <br /> between planned irrigation times, plus a milniaaum design <br /> volume of 54 percent of the first-stage unit. M *- water <br /> depth of second-stage lagoons should be 4 to 6 feet. This <br /> will encourage aerobic conditions, resulting in better <br /> quality f UShing vater. All pumping for irrigation and <br /> flushing should be from the second-stage lagoon. <br /> The second-stage unit may only be used foriholding overflew <br /> from <br /> the for lagoon until it can be coxiveniantly <br /> irrigated crop utilization. In such cases, the second <br /> unit should be as deep an practical and sized to Mold the <br /> total volume of all wastes and runoff which will enter the <br /> entire system, including safety margins. 0hen feasible, <br /> contents from the entire second-*stage unitimay be removed <br /> and applied to the land. Where lagoons are installed in <br /> high-water tablas areas, contents should not be lowered below <br /> the existing water table to prevent disc{turleiing the phygieal <br /> and biological seal. !. <br /> I <br /> 273 <br /> • E <br />
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