Membrane Filtration Basics 101 Paul J. Delphos, Black & Veatch 757-456-5380, ext 12 VA AWWA Plant Operations Committee Operators Conference Virginia Beach, VA May 19-21, 2014
Presentation Overview Market Assessment Membrane Theory Example Applications
What’s The Big Deal?? 1 st Significant MF/UF System in North America in 1993 (Saratoga, CA – 3.6 mgd) Over 250 plants now on-line Historically, small facilities (i.e. < 1 mgd) for small clients Trend is to fewer, but larger facilities Minneapolis – 70 and 90 mgd Singapore – 72 mgd Lancaster – 24 mgd, expandable to 36 mgd
Desalination Is Growing As Well Ca Capacity ity (mg (mgd) Numb Number er of of Inst Installa allation tions EDR EDR SWRO SWRO BWNF BWNF 15 44 92 20 71 110 110 250 BWRO BWRO
Other Perspectives Membrane System Sales To Reach $9 Billion by 2008 (Mcllvaine Company, 2006) $6.8 Billion in 2005 (33% Top End Growth) Nearly All New Revenues Are Includes Desalination and Low-Pressure Membranes From New Projects Microfiltration from $1.9 to $2.5 Billion Only 2.5% of US Drinking Water is Treated with MF/UF Membranes Expected to Reach $10 Billion by 2010
What Are Membranes? Submerged/Vacuum Cartridge/Pressure
Membrane Theory Overview Organic macromolecules Organic compounds Colloids Viruses Dissolved Bacteria salts Pollens Yeasts 0.0001 0.01 0.001 10 1 0.1 100 um Reverse osmosis Smallest Polio hair visible Giardia Nanofiltration microorganisms virus to naked Ultrafiltration eye Microfiltration Sand filter
How Do Membranes Work? Membranes can remove anything that is larger than its pores.
Giardia Cryptosporidium
Membrane Failure Mode • Membranes fail incrementally – one fiber at a time. • Statistically, individual fiber breaks are insignificant to the overall microbial water quality.
On-Line Integrity Testing Bubble point Air pressure Direct Measures Sonic wave Bio-challenge Turbidity Indirect Particle Measures monitoring The accepted standard is moving towards continuous (safety interlock) turbidimeters. Detection limit 0.001 NTU.
Some Key (and New) Terms OLD NEW Overflow Rate Flux Declining Rate Flux Decline ???? Specific Flux/Permeability Backwash Reverse Filtration Filter Breakthrough Membrane Integrity Filtered Turbidity Log Removal Backwash Volume Recovery Filter Head Loss Transmembrane Pressure
Piloting Overview Number of Systems? Regulatory Acceptance Verified Membrane Applicability Basis of Design Operator Experience
Data Evaluation Flux Recovery/Waste Disposal Cold Water TMP Issues Daily Cleans vs. Monthly Cleans City of Lancaster MF Pilot 60 12 Turbidity 50 10 40 8 TOC/UV254 gfd psi 30 6 20 4 Particle Counts – log removal 10 2 MIT’s 0 0 Nov Jan Mar Apr Jun ZW 500-C, Sp Permeability @ 20°C ZW 500-C, Instantaneous Flux ZW 500-C, Average TMP
Membrane Fouling Mitigation Measures Causes Chlorination Biological Cross-Flow Organic/Colloidal/ Backwash Particle Chemical Cleaning Chemical Scaling Additives/Coagulants Membrane Compression Pretreatment Synthetic Polymers
Membrane Fouling Directly Impacts Costs Fouling is the limiting factor in most membrane system designs By removing organics, or natural organic matter (NOM), membranes become much more effective Coagulation removes NOM by: Charge Neutralization Adsorption To Precipitates With membranes, coagulation is geared to TOC removal The “cake layer” on pressure systems improves TOC removal
Membrane Fouling 16 14 12 Backwash & Chemical Cleaning Pressure - psi 10 Backwash 8 6 Irreversable Membrane Fouling Fouling 4 2 0 0 50 100 150 200 250 300 Time
Membrane Fouling Example Before and After Backwashing 22 (1) (3) (4) (5) (6) (7) (8) (2) (1) Vacuum increase due to flux increase corresponding to re-adjusted permeate flow. 20 (2) Rain event - organics/color raw water spike, alum dosage not increased to compensate. 18 (3) High vacuum alarm --> tank dumped, re-started with higher alum dosage. 16 (4) Caustic dosing interrupted. (5) High vacuum alarm --> clean 14 (6) Clean - vacuum recovers to 4"Hg. TMP (psi) (7) Ferric dosing interrupted? (Floc tank pH = 6.8). (8) High vaccum alarm --> system off for 6.5 hours and 12 then re-started. 10 8 6 4 2 0 22- 24- 26- 28- 30- 1- 3- 5- 7- 9- 11- 13- 15- 17- 19- 21- Jul Jul Jul Jul Jul Aug Aug Aug Aug Aug Aug Aug Aug Aug Aug Aug Before BP Vacuum Date After BP Vacuum
SEM Images of Fouling Layer (UF Membrane, CA, 100k MWCO) Clean Membrane Growth of NOM Fouling Layer Over Time Effect of Backwashing on Fouling Layer HIOP Cake Layer with Sorbed NOM Effect of Backwashing on Cake Layer
Clean Membrane, CA 100k MWCO
Dead-End Filtration – 30 Minutes
Dead-End Filtration – 1 Hour
NOM Layer Before Backwash
NOM Layer After Backwash
Coagulant Aid (HIOPS) + NOM Before BW
Coagulant Aid + NOM After BW
Potential Applications For Low Pressure Membranes Turbidity/pathogen/TOC removal on raw water Replace conventional filters following flocculation/sedimentation Treatment of conventional filter backwash water Pretreatment ahead of RO or NF membrane system Fe/Mn removal following oxidation Arsenic Removal Pathogen removal following conventional treatment
Typical Pressure MF/UF System Permeate Cl 2 Finished Air System Water B/W Water Pumping Supply Particle Pump Strainer Raw Membrane Finished Water Modules Water Backwash Waste/ Source Storage Concentrate To CIP System Disposal
Submerged - Enhanced Coagulation Coagulant Permeate Pump Flash Mixer Feed Water Bleed/Concentrate Flocculation Chamber High solids concentration in tank Air
Pressure vs. Submerged Filtered Filtered Filtered Water Water Water 5 to 50 psi Solids and Liquids Under Pressure
Pressure vs. Submerged Pressure Submerged Advantages Advantages Skid-mounted Use of existing tanks Easy to install Larger systems Great for small systems Low energy Easy competition Great for poor raw water High Fluxes Low fouling Backwash recovery Disadvantages Disadvantages Larger systems Fouling/energy Modifications can be expensive Low Dosages of Coagulant Low flux rates Backwashing Concentrate with fiber breakage
Outside-In vs. Inside-Out Filtered Filtered Filtered Water Water Water 5 to 50 psi Solids and Liquids Under Pressure
Outside-In vs. Inside-Out Outside-In Inside-Out Advantages Advantages Submerged option Great with clean water Larger active area Cross-flow operation minimizes irreversible fouling Higher solids Disadvantages Lower Pressure Recirculation required Dead-end flow Higher flux requirements Disadvantages High fouling potential Lower comparative flux Increased energy Irreversible fouling?
MF/UF Modes of Operation Cross-flow Conventional (Dead-End) Feed Feed membrane filter membrane filter
Principal Suppliers of Low Pressure Drinking Water Membrane Systems Membrane System Suppliers Membrane Module Suppliers Pall Corporation (MF/UF) GE (UF GE - Zenon Environmental, Inc. Evoqua (MF) (MF/UF) Dow (UF) Evoqua Water Technologies Toray (UF) (Siemens - US Filter/Memcor Hydronautics, Inc. (UF) (MF) ) Asahi (MF) Wigen, Inc. (UF) H2O Installations WesTech Kruger
Primary Elements of Low-Pressure Membrane System Feed water/vacuum pumps Ancillary pumps Automatic screens Skids with PLC-based controls Clean-in-place (CIP) SCADA system/PLC network Air delivery system Waste holding tank/pumps Neutralization tank/pumps
Roanoke, VA – Crystal Spring Spring has been used for drinking water since 1880s In summer of 2000, VDH determine spring was GWUI as coliform counts increased Virginia Membrane Plants - Memcor - 14 Koch - 1 VDH “Approved” Other Membrane Manufacturers Competitive Bid Between Memcor and Pall
Crystal Spring WTP - Design Conditions 5 mgd firm (one rack out of service) 99.5% recovery (backwash recovery) No pretreatment (chlorine was recommended by Pall) 30 day cleaning cycle 60 minute backwash frequency 10-year membrane warranty Performance testing for successful bidder
Crystal Spring WTP - Bid Summary Cost US Filter - Pall Component Memcor Capital $1,600,317 $1,960,000 O&M (20-yr $436,625 $303,176 PW) Membrane Repl. $357,822 $429,130 (20-yr PW) Total 20-yr PW $2,394,764 $2,692,306
Performance Testing Operating Results Flux: 34.8 gfd @ 15 o C TMP: 1 psi increase per 15 to 18 days Average TMP: 10.5 psi Backwashing: 150 sec/90 minutes 97% Recovery CIP Interval of Over 90 days
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