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SU0003122
Environmental Health - Public
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THORNTON
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2600 - Land Use Program
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SU0003122
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Entry Properties
Last modified
5/7/2020 11:29:41 AM
Creation date
9/9/2019 10:38:07 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0003122
PE
2633
FACILITY_NAME
SA-93-26
STREET_NUMBER
26440
Direction
N
STREET_NAME
THORNTON
STREET_TYPE
RD
City
THORNTON
ENTERED_DATE
11/6/2001 12:00:00 AM
SITE_LOCATION
26440 N THORNTON RD
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\T\THORNTON\26440\SA-93-26\SU0003122\APPL.PDF \MIGRATIONS\T\THORNTON\26440\SA-93-26\SU0003122\CDD OK.PDF \MIGRATIONS\T\THORNTON\26440\SA-93-26\SU0003122\EH COND.PDF \MIGRATIONS\T\THORNTON\26440\SA-93-26\SU0003122\CORRESPOND.PDF
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EHD - Public
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Technical Description <br /> NH3 +HOCI NH2Cl (monochloromine) +H2O <br /> NFV1 +HOCI NHC12 (dichloromine) +Hz0 <br /> NHCl2 +HOCI NCI (nitrogen trichloride) +H2O <br /> These reactions are extremely important, as the. disinfecting power of a unit of chlorine as <br /> hypochlorous acid is between 25-100 times as great as that of a unit of chlorine as monochloramine. <br /> Ifthe effluent has not gone through a quality nitrification/denitrification process,the levels of ammonia <br /> at the chlorine contact stage will be high enough to convert the potent chlorine to a less-than-potent <br /> monochloramine.In addition to combining with ammonia,hypochlorous acid reacts with amino acids, <br /> proteins, and other organic matter to produce chlorine compounds which have very low disinfecting <br /> power, and it combines with sulfites, nitrates, and ferrous or manganous ions to produce chlorine <br /> compounds which have absolutely no disinfecting power. For this reason, it is very important that if <br /> chlorine is to be used, the chlorine receiving effluent be of the highest quality possible. <br /> Although the Bio-Pure system is perfectly capable of producing this high-quality effluent at the <br /> chlorine contact stage, AquaClear recommends the use of ozone as the preferred method of dis- <br /> infection. Should chlorine be required by local ordinance,it is advisable that an ozone generator follow <br /> chlorine contact. This will accomplish two things: In virtually all cases it will assure a 99.999% <br /> pathogen kill and, at the same time,will convert the chlorine residual to a chlorate which will be taken <br /> up by plant life without harm. This conversion is expressed as: <br /> 3C1-+03 —)� 3C1+302 --> C1+503 <br /> After the SNT pump transfers the supernatant from the clarifier,the clarifier sludge return(SLR)pump <br /> returns the sludge, and any floatables which surfaced during the clarification stage, to the aeration <br /> chamber for reprocessing. This sludge,along with the fresh incoming waste,becomes the food source <br /> for new cell growth and a carbon source for denitrification. <br /> Because of this 100% returned-sludge;process, the Bio-Pure system is capable of removing an <br /> average of 96%of nitrates. The 100%returned activated sludge(RAS) provides dead bacterial cells <br /> as the carbon source for new cell growth.These new cells utilize the NO along with the PO 41 causing <br /> removal of nitrates and phosphorus. The dead cells also provide a food source for the incoming <br /> bacteria. Upon completion of the sludge return, the MLT pump can again fill the clarifier. <br /> Upon completion of the second quiescent settling :period in the chlorine contact chamber, the <br /> supernatant is then pumped through tertiary filters, and finally the tertiaried effluent may be <br /> dechlorinated and further sterilized by optional ultraviolet light prior to discharge. <br /> Settled sludge from each stage,and filter backwash,are returned to the aeration chamber and recycled. <br /> If physical pretreatment is incorporated in a buffer tank, settled sludge and backwash may be <br /> selectively returned to the buffer tank or to the aeration chamber. <br /> ADDITIONAL PRETREATMENT(may not lbe required) <br /> DISINTEGRATION. If required, influent may be disintegrated by pretreatment prior to entering the <br /> aeration chamber by one of three methods: J <br />
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