UASB 2009
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Transcript of UASB 2009
AEROBIC METHOD
ANAEROBIC METHOD(UASB PROCESS)
Anaerobic Process
Fats, proteins, polysaccharides
Step -1 Facultative & anaerobic bacteria: Very slow for grasses, agriculture residue
Fatty acids, amino acids, sugars
Step -2 Fermentation & beta Oxidation (Grow rapidly)
Simple Organic compounds-- short chain fatty acids, alcohols,
BOD converted to bacterial cells
Step- 3, Methanogenesis Strict Anaerobic Bacteria. Grow slowly (Intolerant to pH & Temp )
CH3COOH ---- CH4 + CO2
UASB Reactor
gas collector
biogasgas dome
inlet point
sludge blanket
sludge outlets
bafflesettlingzone
effluentgutter
deflector
biogas
inlet box
Granules
Removal Efficiencies
TSS 60-80%
BOD 60-70%
COD 60-70%
River Discharge Standards
TSS <50 mg/l
BOD <30 mg/l
Faecal Coliform <10,000 MPN/100 ml
DESIGN OF UASB REACTOR(Case Study of Karnal STP)
WASTWATER DATA USED
FLOW = 40 MLDBOD = 250 mg/LCOD = 400 mg/LTSS = 270 mg/LVSS = 70% of TSS = 189 mg/LInert SS = 270-189 = 81 mg/L
DESIGN PROCEDUREDesign Conditions:
Yield Coef. (Yobs) = 0.01 Kg SS/Kg BOD Upflow Velocity = 0.52-0.58 m3/m2/h or m/h Max Peak Upflow Velocity = 1.5 m/h HRT (Hydraulic Retention Time)= 8-12 Hrs. Height of the Reactor = 5.0 m Volumetric Loading = 0.8-1.2 Kg COD/m3/day Sludge Bed Concentration = 65 Kg TSS/m3 or 65000 mg/L
(Conc. 6.5 %)
No. of Reactors = 4 Nos.
Flow in each Reactor = 10 MLD = 10,000m3/d
= 416.67m3/hr
Peak Factor = 2.25
Peak Flow = 416.67 x 2.25
= 937.50 m3/h
Adopt Upflow Velocity = 0.54 m3/m2/h
Surface Area of the Reactor= 416.67/0.54
= 771.6 m2
Provide Reactor Size = 32 m x 24 m
Check for Peak Upflow
Velocity = 937.50/771.6
= 1.21 m/h < 1.5 m/h
Select Height of the Reactor
(to full-fill Sludge Bed & GLSS)= 5.0 m
Volume of the Reactor = 32 x 24 x 5.0= 3840 m3
Volumetric Loading = Q x COD/Vol.= 10,000 m3/d x 400 x10-3/
3840= 1.04 Kg COD/m3/d, OK
Calculated HRT = 3840/416.67= 9.21 hrs, OK.
Sludge Production
Considerations: A = Yield of biomass is 10 % of BOD degraded B = Fractions of VSS remain: (60 % VSS degraded) C = Inert solids (TSS-VSS) influent
Sludge Production
Expected BOD Removal Eff. = 70%Ash Content in TSS = 30%VSS Content = 70% of TSSNew VSS Produced in BOD rem. = 10% of BOD removed
= 0.1 x 0.7 x 250= 17 mg/L
Sludge Produced (A) = 40,000 x 0.017 kg/m3 = 680 Kg/d
Non-Degradable VSS = 40% VSS= 0.4 x 189= 75.6 mg/L
Sludge Produced (B) = 40,000 x 0.76 kg/m3 = 3024 Kg/d
Ash/Inert SS Received in flow = 30% TSS= 0.3 x 270= 81 mg/l
Sludge Produced (C) = 40,000 x 0.081 kg/m3 = 3240 Kg/d
Total Sludge Production = 680+3024+3240= 6944 kg/d
Methane Generation (COD basis)
Quantity of methane estimated from oxygen equivalent of methane gas.
CH4 + 2 O2 CO2 + 2 H2O. 16 g or 1 mole of CH4 equivalent to 64 g
COD. 1 g of COD = 1/64 mole of methane. 1 mole of methane = 22.4 liters of volume. 1 g COD = 22.4/64 = 0.35 Liters CH4
Energy/Electricity Production
Energy Equivalent of methane 33810 kJ/m3 of methane COD removed 11200 kg/d (70 %) Methane generated = 0.35 x 11200 = 3920 m3/d Energy produced = 3920 m3/d x 33810 kJ/m3 = 1533 KJ/s Theoretical Electricity produced = 1533 KW Efficiency of generator = 10 % - 20 % (generally 10 %) Actual Electricity Produced: 3679 kW-h/d
-Low Energy Consumption-Good removal Efficiencies-Generation of Methane Gas (Energy Recovery)-Small Land Area Requirements-Low Surplus Sludge Production-N,P,K Conc. Are Retained in Treated Eff.-Simple Construction, Operation & Maintenance
Salient Features of UASB Technology
Post-Treatment Options
Final Polishing Ponds Aerated Lagoons Combination of Aerated Lagoon & Ponds Down Hanging Sponged Media System
Final Polishing Ponds (FPP)
Aerobic Ponds having not less than 1 day HRT Water Depth 1.5 m Large area requirements Max. Removal Eff. 50% for TSS, 60 % for Total BOD Algal Growth Sludge Accumulation (desludging is required) No Feacal Coliform removal is expected
View of FPP
Facultative Aerated Lagoon (FAL)
Power is Required for Aerators Water Depth 3.0 to 3.5m Settling Tank is required (Solids-Liquid) Moderate HRT (12 hrs) No Feacal Coliform Removal is expected
View showing FAL