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1 ADVANT MA'NU:AL ll <br /> i &M <br /> 5 <br /> DO level drops,the degree of nitrification will wastewater constituents (i.e., BOD,TSS,TKN, <br /> 'I! normally drop as well,which could be a sign etc.). In this rase,the available alkalinity in the <br /> t <br /> of blinding or saturated flow conditions—any- water supply may not be adequate to accomplish <br /> thing that might inhibit free air from flowing the full level of nitrification desired. <br /> into the system. (Though it's quite possible to <br /> have low filtrate DOs and still have high effluent These constraints exist for all wastewater treat- <br /> qualit)6 as measured by BOD and TSS levels.) ment operations,regardless of whether the opera- <br /> tion involves a suspended growth contact stabi- <br /> Biological Growth on Filter lization process or an attached growth packed <br /> j With"fixed film" treatment systems,biological bed filter.Packed bed systems will perform better, <br /> i <br /> growth on the filter media is natural.The biomat especially if they have a large attached growth <br /> ? should appear light-brown to dark-brown in surface area per unit volume ratio, because of the <br /> color and gelatinous in texture. micro-sites near the attached side of the biomat, <br /> } Influent Characteristics where denitrification typically occurs,returning <br /> some of the alkalinity.Textile packed bed filters, <br /> Influent characteristics will greatly affect the because of their large surface area per unit <br /> amount of nitrogen reduction that is possible volume ratio,tend to perform even better. <br /> sfrom any wastewater treatment system. Nevertheless,additional buffering may be neces- <br /> pH:For normal residential nitrogen loads, <br /> sary to accomplish the level of nitrification <br /> i <br /> pH typically needs to be 6-8. desired. <br /> Alkalirft:Alkalinity is essential for nitrification. <br /> For each part ammonia that is nitrified,7.14 <br /> parts alkalinity are consumed(buffering the <br /> acidity caused by the release of hydrogen ions). <br /> I Consequently,if the degree of nitrification is less <br /> than expected,it could simply be that there isnt <br /> sufficient alkalinity to support more.Typical resi- <br /> dential nitrification requires alkalinity above 250± <br /> mglL for recirculating processes and double that <br /> for single pass processes.Many wastewater streams <br /> i do not have sufacient alkalinity to support complete <br /> nitrification. <br /> f <br /> Wastewater streams without sufficient alkalinity <br /> to support complete nitrification may,depending <br /> on the type of process,cause a depletion in the <br /> alkalinity to the point where the pH correspond- <br /> ingly drops to a level that causes the microbial <br /> activity to degrade(<6±). Recirculating the efflu- <br /> ent helps,since half the alkalinity can be restored <br /> ' in the recirc or process tank,wherever denitrifica- <br /> tion occurs(and adjusting the recite ratios may <br /> i also bring the pH back to preferred operating lev- <br /> els). But wastewater streams that are alkalinity- <br /> starved can't provide for 100%nitrification. <br /> The use of low flush fixtures requires special <br /> consideration. Low flush fixtures tend to reduce <br /> hydraulic loads,which causes elevation of <br />