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ICOM 2008 | July 12-18, 2008, Honolulu, Hawaii USA
Importance of membrane reactor design on membrane performance in biofilm-MBR Igor Ivanovic, TorOve Leiknes ( NTNU - Norwegian University of Science and Technology Department of Hydraulic and Environmental Engineering, Trondheim, Norway
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Content BF-MBR concept and MBBR Membrane reactor requirements Membrane reactor design and fouling Strategies for minimizing fouling due to suspended particles Strategies for minimizing fouling due to colloidal particles Results and discussion Conclusion
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Biofilm process → Membrane process
BioFilm MemBrane Reactor (BF-MBR) concept Biofilm process → Membrane process Concept: SCOD PCOD Process: Objectives: One-step biological degradation Design membrane reactor for enhanced particle removal
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Biofilm reactor designed for Nitrification
Recirculation! Biomass attached for plastic carriers (by AnoxKaldnes) One-step biological degradation process Aeration demand (2-4 mgO2/L) – full nitrification (low organic load) after HRT=4-6 hours
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Biofilm reactor: performance and removal rates
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Particles and fouling (previous studies)
1. Suspended particles – MLSS - range > 1,2 µm 35 LMH 2. Colloidal particles – PSD number % - range 0,04 -1,2 µm
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Membrane reactor requirements
Particle separation unit! Higher fluxes (compared to AS-MBR) - i.e. > 30 LMH High recovery (R) – i.e. 95 % and more Short HRT (and SRT) – i.e. HRT < 1 hour
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☺way to go! Possible BF-MBR configurations ↓BF + AS ↑ !Not desirable!
Scenario No1: Typical submerge MBR configuration would convert biofilm reactor to activated sludge reactor due to accumulation of retained biomass ↓BF + AS ↑ !Not desirable! Biofilm reactor Scenario No2: External submerge membrane reactor opens possibility to keep retained biomass separated from biofilm and provides stable i.e. designed bioreactor operation ☺way to go! Biofilm reactor
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Suspended particle reduction – MLSS reduction
1. Complete mixed reactor CM-MR – Recovery (R)! 2. Rector with sludge pocket SP-MR – Separation coefficient Ks! c≠c2 ; c<c2
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Pilot plant configuration
MBBR: Total volume of reactor: 260 L Type of carrier: K1 – AnoxKaldnes Filling fraction – 67 % of reactor volume Surface area for biofilm growth m2/(m3 reactor volume) Total growth area m2 > 99% Nitrification achieved HRT=4 hours Membrane: Zenon ZW10 Membrane Pilot Module Nominal pore size – 0,04μm Material PVDF Membrane area- 0.93m2 Membrane operation: Production flux – 35 LMH Backwash flux – 42 LMH Operating cycle: 4.75 min/production 0,25 min/backwashing Recovery ~ 96 %
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CM-MR vs. SP-MR CM-MR: Volume=9 L HRT=0,3 hour
SolidRetentionTime SRT=7,5 hour Ks=1 Recovery ~ 96 % SP-MR: Volume=25 L HRT=0,7 hour SolidRetentionTime SRT=20,8 hour Ks=? Recovery ~ 96 %
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Comparison - performance
Separation factor Ks determinate at 3,4 and fouling rate decreased ~ 3 times
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Challenge – floating sludge in SP-MR!!!
With increasing volume of membrane reactor SRT increased. Longer SRT creating anoxic conditions inside sludge pocket and causing sludge bulking Improvements of membrane reactor were required!
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SP-MR and MSP-MR SP-MR: Volume=25 L HRT=0,7 hour
SolidRetentionTime SRT=20,8 hour Ks=3.4 Recovery ~ 96 % MSP-MR Volume=41 L HRT= 1,3 hour SolidRetentionTime SRT=33.3 hour Ks=? Recovery ~ 96 %
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Comparison - performance
Separation factor Ks of MSP-MR increased additionally up to ~ 2,5 times (Ks=8,4) and fouling rate decreased ~ 6 times Floating sludge was no longer problem!!!
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Colloidal particle reduction – PSD number% reduction
Colloidal (submicron) particles are not settable. Strategies to reduce colloidal particles: 1. Prevention of flocs brakeage during the membrane aeration (air scouring) 2. Flocculation – natural UP DOWN
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Colloidal particles reduction in MSP-MR
Inlet
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Membrane performance - TMP start up for CM, SP and MSP-MR
CM-MR Confirmed by less fouling measured – expressed in TMP development
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Conclusions Membrane reactor design play key role in fouling control in BF-MBR Confirmed reduction of fouling rate due to reduction of amount of particles (both suspended and colloidal) around membrane area New strategies for reduction of colloidal (submicron) particles required
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Acknowledgments MSc Students:
Financial support by: Norwegian research council (NFR) ZENON Environmental Inc., Canada, for supplying the membrane modules AnoxKaldnes, Norway, for support with the biofilm reactor EUROMBRA, Contract No , MSc Students: Francisco Sánchez Molada, Polytechnic University of Valencia Heidi Bold, ETH Zurich, Switzerland Martin Engmann, ETH Zurich, Switzerland Gerrit Senger, TU Berlin
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Thanks for your attention!
Acknowledgments Greetings from Trondheim's fjord! (sailing sessions edition) Thanks for your attention! QUESTIONS ?!? TorOve Leiknes: Igor Ivanovic:
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