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Study On Ammonium Removal Process From Light Polluted Water Source At A Low Concentration

Posted on:2008-08-31Degree:MasterType:Thesis
Country:ChinaCandidate:X H GeFull Text:PDF
GTID:2252360212976990Subject:Environmental Engineering
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With rapid development of economy, the pollution of water sources such as NH4+ (NH3) pollutant is increasingly serious as well as population dramatically increasing and living condition greatly improved. Water supply system has been out of capacity both in water amount and water quality. China and many other countries have already established strict limitation of NH4+-N or NH3 in drinking water criterion.In order to find suitable method and process for ammonium removal from water source, synthetic water containing NH4+-N at about 10ppm was treated by two combination techniques.Method 1:①NH4+-N was nitrified to NO3--N by immobilized microbiological pellets in inner-circulated fluidized bed reactor continuously;②NO3--N was removed by IRA400JCl ion exchange resin in columns and the resin regenerated by 35%NaCl solution;③regeneration waste brine was treated by biological denitrification in SBR reactor before being drained to environment.①It showed an efficient and stable NH4+-N nitrifying performance under the condition of temperature 2030℃and DO 34mg/L. Removal rate reached above 90% within HRT30min when influent NH4+-N at 1015mg/L and both NH4+-N and NO2--N was below 0.25 mg/L in the effluent within HRT27min when influent below 10mg/L. pH value of effluent water remained at 7.27.3 automatically. Removal loading could reach 256.1mg-N/(L-pellet·h) and oxygen uptake rate raise to 1170.9mg-O2/(L-pellet·h). The nitrifying process fit to zero-grade degradation kinetics. High biomass retention was observed in SEM.②NO3- removal by IRA400JCl ion exchange resin was efficient and the process fit to Langmuir well. About 675 bed volumes (BV) raw water could be treated before effluent NO3- above 10mg-N/L. Breakthrough capacity could reach 19.99kgNO3--N/m3-resin, and the removal rate was about 98.709%. The resin saturated with NO3- was regenerated smoothly and conveniently with 35% NaCl solution.③The regeneration waste brine could be treated by the anaerobic biological denitrification in SBR after 2 months’cultivation and climation. 2.5m3 biological reactor and 0.25m3 ion exchange columns were necessary while NH4+-N removal capacity is 120t/d. The SV for biological part was about 48m3/m3·d while 480m3/m3·d for ion exchange part.Method 2:①NH4+-N was absorbed continuously by 150g new clinoptilolite at a size of 0.551.30mm filled in multiple smart columns in parataxis style;②clinoptilolite was regenerated with saturated NaCl solution when full of adsorption;③NH4+-N removal again by regenerated clinoptilolite;④regeneration again…To be recycled and circulated. The regeneration waste brine was treated by ammonia escaping from alkaline solution with heat.①NH4+ adsorbed by new clinoptilolite in columns gradually, 92.67L water was treated after 32.5h when effluent got to 1mg-N/L. The maximum adsorption capacity was about 12.76mg-N/ (g-zeolite). SV was about 421.6m3/m3·d.②Clinoptilolite was regenerated with saturated NaCl solution smoothly and efficiently. The recovery rate increased above 90% after 130min. The NH4+-N in regeneration brine got to its maximum of 4966mg-N/L. 1.875kgNaCl/(L-zeolite) were used for regeneration and the waste brine was totally about 7.76BV.③About 193.28L water was treated within 63h by Clinoptilolite after regeneration. The maximum capacity was 15.56mg-N/(g-zeolite) and SV was 460.19m3/m3·d.④clinoptilolite saturatd with NH4+ was Regenrated. Recovery rate increased above 90% after 150min. About 300.4gNaCl was used for regeneration of 90g clinoptilolite and the waste brine was about 10.3BV. There was an accumulation phenomenon of NH4+-N in brine in one column after another and the maximum could reach 6000mg-N/L. The zeolite system was efficient, safe, low cost and convenient, especially fit to small scale water supply system. If the NH4+-N removal capacity was about 120t/d, 0.342m3 adsorption reactor was necessary. SV was about 350.9m3/m3·d.In a word, both two methods were stably efficient for NH4+ removal at a low concentration. The process was simple, economical and feasible for engineering application.
Keywords/Search Tags:light polluted water source, NH4+ at low concentrations, immobilized nitrifying pellets, ion exchange, biological denitrification, adsorb by zeolite
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