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Blackburn Wastewater Treatment Plant Upgrade Study

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Section 4.0 - Blackbum <strong>Treatment</strong> Options<br />

Secondary <strong>Treatment</strong><br />

Secondary activated sludge processes involve aeration basin(s) and clarifiers.<br />

<strong>Wastewater</strong> enters the basins where it is aerated and mixed with a population<br />

of preconditioned microorganisms. Soluble organic material is removed from<br />

the wastewater by biological oxidation, and the insoluble material is removed<br />

by physical entrapment and adsorption within the floc. This mixture of<br />

microorganisms and organic matter is called mixed liquor suspended solids, or<br />

activated sludge. AAer leaving the aeration basin, the mixed fiquor is<br />

separated into a clear supernatant fraction (secondary effluent) and settled<br />

solids (return activated sludge). The return activated sludge is pumped back to<br />

the aeration basin and mixed with the raw influent to maintain the microbial<br />

population. The solids retentmn time (SRT) or sludge age, is controlled by<br />

daily wasting a fraction of either the mixed liquor or the return activated<br />

sludge. This serves to offset excessive microbial growth in the aeration basin.<br />

Conventional activated sludge processes are designed solely for BOD and TSS<br />

reduction; an hydraulic retention time of only 7 h, and a sludge age of 4 to 7 d<br />

are required for this. If ammonia toxicity in the effluent is an issue, the<br />

retention times must be increased to foster nitrification, which is the<br />

conversion of ammonia to nitrites and nitrates. Organisms, which perform this<br />

reaction generally, grow at a slower rate. This modification is called extended<br />

aeration, and involves doubling the hydraulic and solids retention times. A<br />

small non-aerated compartment known as an anoxic selector is usually<br />

included at the inlet to the aeration tank. This environment favours the growth<br />

of flac-forming organisms over filamentous organisms, which enhance the<br />

settleability of the mixed liquor, which in turn improves the quality of the<br />

secondary effluent. In addition, it reduces some of the nitrates produced in the<br />

nitrification reaction. Nitrates are converted to dissolved nitrogen, which<br />

evolves as nitrogen gas to the atmosphere.<br />

In the event that primary treatment is not included, the secondary treatment<br />

parameters described above would require further increase by a factor of<br />

approximately 1.5 to 2.0. A process flow diagram of the activated sludge<br />

process as it may be applied at this site is described below. Screened<br />

wastewater is combined with return activated sludge and enters an anoxic cell,<br />

which in turn discharges to an oxidation ditch equipped with fine bubble<br />

diffusers and mixers to drive the flow around the circuit. Due to the absence of<br />

primary clarifiers, the oxidation ditch will be sized for a hydraulic retention<br />

time of 24 h to ensure nitrification. The mixed liquor then flows to two<br />

secondary clarifiers, each sized for 50 percent of the total flow. Emuent from

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