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Thesis - faculty.ait.ac.th - Asian Institute of Technology

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nitrification-denitrification process, an external carbon source in <strong>th</strong>e form <strong>of</strong> le<strong>ac</strong>hate,<br />

me<strong>th</strong>anol etc. could be necessary. An external carbon source could fur<strong>th</strong>er increase <strong>th</strong>e<br />

operational costs. Chemical treatment by coagulation, flocculation and precipitation<br />

eliminates <strong>th</strong>e increased chemical costs making <strong>th</strong>is option realistic for ammonia removal.<br />

Thus, ammonia stripping seems to be <strong>th</strong>e most viable option. While ammonia stripping can<br />

be conducted in p<strong>ac</strong>ked towers wi<strong>th</strong> efficiencies up to 95 %, <strong>th</strong>e intention <strong>of</strong> <strong>th</strong>is study is to<br />

merely reduce le<strong>ac</strong>hate wi<strong>th</strong> total nitrogen content <strong>of</strong> 1,800-2,000 mg/L to a level below<br />

toxicity for fur<strong>th</strong>er biological treatment, for which a conventional ammonia stripping<br />

would be sufficient. Thus, by maintaining an optimal operating condition by controlling,<br />

air flowrate and pH, an ideal condition based on ammonia removal, ammonia toxicity and<br />

mixing power efficiency could be obtained using a conventional stirred tank.<br />

One <strong>of</strong> <strong>th</strong>e main disadvantages <strong>of</strong> ammonia stripping is <strong>th</strong>e high cost associated wi<strong>th</strong><br />

pH adjusters. The choice <strong>of</strong> pH adjuster is also crucial in design and rendering <strong>th</strong>e process<br />

cost effective, a reduction in <strong>th</strong>e amount <strong>of</strong> adjuster can be brought about by pre-aerating<br />

<strong>th</strong>e le<strong>ac</strong>hate. The syn<strong>th</strong>etic le<strong>ac</strong>hate used in <strong>th</strong>is study has an average pH <strong>of</strong> 8.5 ±0.5. Since,<br />

<strong>th</strong>is is already in <strong>th</strong>e alkaline range; <strong>th</strong>e amount <strong>of</strong> buffer added to raise pH for ammonia<br />

stripping is not significant.<br />

2.13.3 Need for Membrane Biore<strong>ac</strong>tors<br />

If <strong>th</strong>e pre-treatment <strong>of</strong> ammonia stripping fails, <strong>th</strong>is would lead to shock loading in<br />

<strong>th</strong>e biological system, making it difficult for <strong>th</strong>e floc to settle down. This problem can be<br />

solved by <strong>th</strong>e adoption <strong>of</strong> a membrane process to repl<strong>ac</strong>e <strong>th</strong>e clarifier in a normal <strong>ac</strong>tivated<br />

sludge process since <strong>th</strong>e membranes can retain total solids until <strong>th</strong>e sludge recovers from<br />

shock loading <strong>of</strong> ammonia.<br />

Purification <strong>of</strong> le<strong>ac</strong>hate by membrane processes aids in preventing fur<strong>th</strong>er<br />

contamination <strong>of</strong> groundwater resources and surf<strong>ac</strong>e water. However, in selecting a<br />

treatment option, or a combination <strong>of</strong> treatment operations, <strong>th</strong>e economic feasibility and<br />

affordability <strong>of</strong> <strong>th</strong>e technology should also be considered. In <strong>th</strong>is regard, membrane<br />

filtration has proven to be a justifiable and economic solution in most cases, even when <strong>th</strong>e<br />

overall costs for <strong>th</strong>e purification are compared wi<strong>th</strong> o<strong>th</strong>er appro<strong>ac</strong>hes for le<strong>ac</strong>hate treatment<br />

(Peters, 1997).<br />

By coupling <strong>of</strong> a membrane wi<strong>th</strong> <strong>th</strong>e <strong>ac</strong>tivated sludge re<strong>ac</strong>tor, a membrane biore<strong>ac</strong>tor<br />

emerges as a logical treatment option. The reduced operational costs associated wi<strong>th</strong><br />

immersed membrane biore<strong>ac</strong>tors proves advantageous in its application and <strong>th</strong>erefore<br />

preferred in <strong>th</strong>e present study.<br />

The use <strong>of</strong> a MBR allows <strong>th</strong>e HRT to be reduced from 1 to 10 days (Qasim and<br />

Chiang, 1994) to less <strong>th</strong>an 24 h. This reduction is drastic and viable in terms <strong>of</strong> operation<br />

costs and effectiveness. Reduction in SRT from conventional <strong>ac</strong>tivated sludge SRT <strong>of</strong> 15<br />

to 60 d has <strong>th</strong>e advantage <strong>of</strong> reducing air requirements in <strong>th</strong>e MBR. Maintaining a lower<br />

MLSS is advantageous since lower <strong>th</strong>e sludge produced, <strong>th</strong>e greater is <strong>th</strong>e effectiveness <strong>of</strong><br />

aeration. This appro<strong>ac</strong>h effectively reduces <strong>th</strong>e aeration requirements and a smaller SRT<br />

and HRT reduces <strong>th</strong>e required re<strong>ac</strong>tor volume and <strong>th</strong>us <strong>th</strong>e capital cost.<br />

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