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CORRESPONDENCE_2009 - 2014
Environmental Health - Public
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4400 - Solid Waste Program
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PR0400042
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CORRESPONDENCE_2009 - 2014
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Entry Properties
Last modified
12/29/2020 11:58:17 AM
Creation date
9/21/2020 12:24:46 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
CORRESPONDENCE
FileName_PostFix
2009 - 2014
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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EHD - Public
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05/26/2009 13:27 9518273 9 DOUGLAS KUNEY RAGE 05/14 <br /> mechanical aerators may reduce the faceequirement <br /> consid ly, but at the expense of si ifi t operating <br /> costs. Aerators are normally appliedto solve odor probl <br /> with .existing lagoons. So, aerobic processes are usually <br /> ill suited for lagooning Poultry wastes. <br /> Anaerobic systems are generally e lagoon stems of choice <br /> for treating poultry wastes. a systemsare designed on <br /> the basis of volume for a specified °t wa tee load, and can <br /> decompose stere organic c mateer unit of volume thAn <br /> ae r io processes. ThO balance of this dighussion will deal <br /> with anaerobic lagoon Systems. <br /> Iddolly, lagoon texpexature should be ca t at 95 F to <br /> maintain a balance between - o g amathana-forminq <br /> anaerobic bacteria. The lagoon will produt minimum odors <br /> when thwm bacteria groups are balanced. idweverr as° a .A. <br /> practical matter, the operator has littlecin 1 over r <br /> 1 t Rapid do in a e may i <br /> be avoided by the lagom an deep as ;possible. <br /> However, there are practical depth: deep lagoons <br /> r Sumer <br /> re slowly in shallow 1. a nott effect is t <br /> and 1 more slowly , <br /> more days of <br /> temperature are likely to be more a <br /> high dive few d of higher winter <br /> biologically g ; <br /> a e; when temperature of the Jago n fails into a <br /> range of 59 to 39 F, bacterial activity Isiminimal. <br /> Therefore,, a moderate depth QZ 8 to 12 f is generally a <br /> good compromise. <br /> The wide ea of temperatures givenfor m1nimal bacterial <br /> activity is due, in part, to the fact thatIthe lagoon <br /> process is , o of twO v diffO=Gnt tyPpes <br /> of bacteria. The first,. i - oseesis quite <br /> robust is active d 39 F. theco <br /> stage, <br /> methane formation, is more sensitive to chAnge, and .has vexy <br /> limited activity below 59 p. So,, acid lev4kls typically <br /> incromm during wint4r without significant utilization of <br /> acidsby methane bacteria. Consequentlyo e;son acidity <br /> produced during winter is similar in effjcj to lagoon <br /> overloading,, and contributes incr i its spring odor <br /> levels frM the Impon. Likewise, sudden +- . <br /> caanges upset, the ba fa ex t in an in a <br /> in id-fed disagreeable . s usually Occurs <br /> in early spring, and sometimes in the fall1 a winter <br /> of little bacterial action, but with loading of ° <br /> wasteials, higher spring waterincrease <br /> mioxvbial action, and foul odors are Sometimes genioratod as { <br /> bacteria pqpulations are re-*stablinhed. <br /> I ' <br /> Desirable combinations of bacteria groups itre obtained when, <br /> among other conditions, lagoon in betwe 7.0 7.5. <br /> Imbalances in pH are most Often a result 0 sudden <br /> tcharges <br /> , overloading, or slug leading of wastes. <br />
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