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SR0085076_OWTS
Environmental Health - Public
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4200 – Liquid Waste Program
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SR0085076_OWTS
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Last modified
9/30/2022 4:13:58 PM
Creation date
9/29/2022 9:09:49 AM
Metadata
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Template:
EHD - Public
ProgramCode
4200 – Liquid Waste Program
FileName_PostFix
OWTS
RECORD_ID
SR0085076
PE
4201
FACILITY_NAME
AHERN TRUCK STOP
STREET_NUMBER
29700
Direction
S
STREET_NAME
AHERN
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
25502014
ENTERED_DATE
3/29/2022 12:00:00 AM
SITE_LOCATION
29700 S AHERN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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11 <br /> Design <br /> It is used for applications with high strength waste streams (such as Type 7 applications and any application with a significant volume of <br /> restaurant waste, such as Type 5)to condition the waste stream prior to secondary treatment by raising dissolved oxygen levels. <br /> An aeration tank,followed by a clarification tank, is situated between the primary treatment system (or pre-anoxic tank if used)and the <br /> secondary treatment system. <br /> Design Notes and Special Considerations: <br /> Pre-aeration units should be sized to provide the appropriate amount of oxygen to reduce organic waste strength or to reduce BODS to less <br /> than 400 mg/L. For systems with high BODS influent values from restaurant waste,pre-aeration can be sized to accomplish approximately <br /> 50% reduction in BODS values. For systems with extreme BODS influent values from food or wine processing, pre-aeration can be sized to <br /> accomplish approximately 75% reduction in BODS values. For recommendations on sizing pre-aeration and clarification tanks,see Appendix A. <br /> Pre-aeration is required for all Application Type 7 systems,and highly recommended for systems that have greater than a 50%contribution of <br /> flow from restaurants(primarily Application Type 5 systems).Orenco provides a number of standard pre-aeration packages for lower flow rang- <br /> es and can assist in sizing and recommendations for higher flow or extreme BODS influent values, Contact Orenco for configurations and sizing. <br /> Standard AdvanTex Treatment Stage <br /> Purpose and Description: <br /> After primary or pre-anoxic treatment,effluent is transported to the recirculation-blend tank or chamber,where it is blended with AdvanTex <br /> filtrate.The blended wastewater is distributed over the AdvanTex textile media and percolates down through the media,where it is filtered, <br /> cleaned,and nitrified by the naturally occurring microorganisms populating the media.After treatment,a portion of the filtrate is returned to the <br /> recirculation-blend chamber while a portion is transported to the next treatment stage or to dispersal. Note that a portion of the recirc-blend (or <br /> filtrate) is often returned directly to the pre-anoxic treatment stage. <br /> In the secondary treatment process,AdvanTex units filter and clean effluent from the primary treatment system.When loaded at or below <br /> the applicable loading rate,they typically achieve treatment levels of< 10 mg/L BODS/cBODS and TSS(30-day average or 30-day arithmetic <br /> mean),with total nitrogen (TN) reduction typically>60%and nitrification averages of 95% (range 90-99%). <br /> For nitrogen loading rates and sizing requirements,refer to the AdvanTex Unit Sizing section of this document. <br /> Post-Anoxic Treatment Stage <br /> Purpose and Description: <br /> The post-anoxic treatment stage provides additional denitrification after secondary treatment in wastewater systems that require significant <br /> reductions in TN,TIN,or NO3-N. Nitrified AdvanTex filtrate from the secondary treatment stage is transported to an anoxic zone inside of the <br /> post-anoxic tank. During post-anoxic denitrification, BOD is consumed during the conversion of NO3 to N2 gas by facultative heterotrophic <br /> bacteria.The N2 gas is then returned to the atmosphere.There are two options for post-anoxic treatment—standard post-anoxic treatment <br /> without media or an anaerobic moving bed bioreactor(MBBRd)with media.A supplemental carbon feed unit is required for both options to <br /> provide the post-anoxic stage with the necessary carbon-to-nitrogen ratio for effective denitrification. <br /> Design Notes and Special Considerations: <br /> Post-anoxic tanks are typically sized at 100%of the Average Day Design Flow. For denitrification to take place,oxygen levels must be depleted to <br /> the level that nitrate becomes the primary oxygen source for microorganisms. Requirements for effective denitrification include ... <br /> • Dissolved oxygen levels<0.5 mg/L(preferably<0.2 mg/L) <br /> • Carbon-to-nitrogen ratio of 4:1 to 8:1 <br /> • Sufficient residual alkalinity(100 mg/L±) in the secondary treatment stage to ensure optimum pH in the post-anoxic stage <br /> • Temperature of the waste stream shall remain above 50° F(10° C)at all times and should typically be above 59° F(15° C) <br /> For standard post-anoxic treatment meeting the above conditions, reduction of nitrate(NO3)through conversion to nitrogen gas(N2)should exceed <br /> 70%. For additional nitrogen reduction, Orenco recommends a denitrifying Moving Bed Bioreactor. MBBRd units are built in insulated fiberglass <br /> vessels.They can achieve up to 90% reduction of nitrate(NO3)through conversion to nitrogen gas(N2)and are typically configured as follows ... <br /> • Fiberglass vessel,sized at 50%Average Day Design Flow,with media retention screens and filters as needed <br /> • Media fill is typically 20%of the vessel volume <br /> • One pneumatic ejector provided per 4 lineal ft(1.22 m)of vessel to ensure optimal mixing and food delivery to the media <br /> • Blowers, housed in a control building,to power ejectors <br /> Orenco Systems°•800-348-9843•+1 541-459-4449•www.orenco.com NDA-ATX-1 <br /> Rev.8,©10/20 <br /> Page 13 of 38 <br />
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