Make Water Anywhere with Pall Integrated Membrane Systems · Control of inlet suspended solids (SDI...

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Tim Lilley, Pall Corporation Portsmouth, April 2012 Make Water Anywhere with Pall Integrated Membrane Systems

Transcript of Make Water Anywhere with Pall Integrated Membrane Systems · Control of inlet suspended solids (SDI...

Page 1: Make Water Anywhere with Pall Integrated Membrane Systems · Control of inlet suspended solids (SDI >3 for RO/NF) Microbial barrier Integrity assurance Sensitive, automated test to

Tim Lilley, Pall CorporationPortsmouth, April 2012

Make Water Anywherewith Pall Integrated Membrane Systems

Page 2: Make Water Anywhere with Pall Integrated Membrane Systems · Control of inlet suspended solids (SDI >3 for RO/NF) Microbial barrier Integrity assurance Sensitive, automated test to

The information contained in this document is the property of the Pall Corporation, and is supplied for

the use of the assigned recipient only.

Unauthorised use or reproduction is prohibited, and the information contained herein is not to be

supplied to others without the specific approval of an officer of the Pall Corporation.

COPYRIGHT 2012

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Contents

Constituents of source waterFundamentals of membrane desalinationMembranes – functions and propertiesSustainable operationConclusions

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Constituents of source water

Water contaminants will include dissolved solids and suspended solids

Seawater contains between 30 and 50 g/l of dissolved salts. Depending on thewater source, other contaminants will be present across the entire range

with huge problems associated with the suspended components

0.0001 0.1 1.0 10 1000.001 0.01 Size (µm)Size (µm)

Inorganic salts Organics Colloidal Virus/Bacteria Mineral/General/Mixed

Dissolved Suspended

Membrane RO Nanofiltration Membrane UF & MF Depth/Media Settlement

Dissolved

Range where contaminants may exist or behave as a dissolved/suspended state

© 2012, Pall Corporation

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Constituents of waterC

onta

min

ant L

oadi

ng T

SS (m

g/l)

103

102

101

100

10-1

10-2C

onta

min

ant L

oadi

ng T

DS

(mg/

l)

105

104

103

102

101

100

Suspended Solids Dissolved Solids

Seawater

Seawater

Optimum membrane range Alternative technology range

© 2012, Pall Corporation

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Constituents of waterSuspended solids - Removed by a filtration media or membrane processes

Dissolved contaminants - Removed by Reverse Osmosis (RO)

RO MembranePost Treatment

Remineralisation andchlorination

Backwash Conc Retentate

Distribution

Strainer MF Membrane

Raw Seawater

Pretreatment:Chemical addition

FiltrationMonitoring

RO MembranePost Treatment

Remineralisation andchlorination

SASRF Conc Retentate

Distribution

Strainer MF Membrane

Raw Seawater

© 2012, Pall Corporation

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Contaminants in Water

0.0001 0.1 1.0 10 1000.001 0.01 Size (µm)Size (µm)

Inorganic salts Organics Colloidal Virus/Bacteria Mineral/General/Mixed

Dissolved Suspended

Membrane RO Nanofiltration Membrane UF & MF Depth/Media Settlement

Dissolved

Range where contaminants may exist or behave as a dissolved/suspended state

RO MembranePost Treatment

Remineralisation andchlorination

SASRF Conc Retentate

Distribution

Strainer MF Membrane

Raw Seawater

© 2012, Pall Corporation

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Membrane separation

Filtrate

Feed contaminants

Feed

Filtrate/Permeate

Microporous/Semipermeablemembrane

Direct or “dead-end” flow Crossflow

Feed

© 2012, Pall Corporation

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Uniform inner and outer skinned UF membrane with narrow pore range ensures highly efficient rejection characteristics

Microfiltration

Ultrafiltration

Complete uniform pore structure through the thickness (no skin) polyvinylidene fluoride (PVDF) membrane construction

Membrane configurations

© 2012, Pall Corporation

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Membrane vs conventional filtration

Features / Performance Evaluation

Sand Filter / MMF/DMF

Membrane MF Benefit of Pall MF

Protection of potential RO + ++++0.1 µm rating removes particulate fines (colloids and oxidized metals eg. Fe, Mn, As) & micro organisms

Silt Density Index (SDI) + ++++ Filtrate with SDI <3

Turbidity ++ ++++ Filtrate with turbidity < 0.1 NTU

Microbial removal + ++++ 6 log removal of microorganism and pathogens

Consistency in performance + ++++ Continuous

Integrity testable - ++++ Assurance of safe potable water supply

Flexibility to cope with variable feeds and hydraulic loads ++ ++++ Broad operation range, handles upsets

Reliability & longevity ++ ++++ Superior strength of HC-PVDF membranes

Modular & expandable + ++++ Future needs, by modules or banks

Waste minimization + +++ Unique Air-scrub-feature for high recovery

Footprint and weight + +++ Compact design, small footprint

Response to oil in feed ++ +++ CIP will clean membranes while SF blocks

- : not available ++ : fair+++ : good++++ : excellent + : poor

© 2012, Pall Corporation

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Membrane filtration vs conventional

Differences of filtrate qualities between traditional prefiltration and Microza® prefiltration (Deposits during SDI measurements)

Feedwater After traditional

pre-filtration

After MF

© 2012, Pall Corporation

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Raw seawater

Filtered seawater

Pre-treatment membrane operation

Previously filtered seawater

Air inlet

Backwash outlet

Time

Tran

smem

bran

e Pr

essu

re

© 2012, Pall Corporation

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Filtration Backwash & air scrub

Raw seawater

Filtered seawater Previously filtered seawater

Air inlet

Backwash outlet

Pre-treatment membrane operation

© 2012, Pall Corporation

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Pre-treatment performance imperatives

Given the broad range of inlet solids and the life expectancyIt is vital to use a physically robust and chemically resistantMembrane:

Homogenous constructionChemically inert PVDF High degree of crystallinity

Skinned ultrafiltration membranes will not withstand the rigoursof repeated backwashing and air scrub. Resulting in deterioration

of performance with time

Performance metricsParticulate (RO pre-treatment)

Turbidity < 0.1 NTUSDI < 2 (RO feed requires SDI <3)Total suspended solids - background

Microbiologicals (RO pretreatemnt and drinking water production)Giardia, Crypstosporidium > 6 log removal (99.9999%)Virus 0.5-3 logAnimal Parasites

© 2012, Pall Corporation

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Membrane integration

Conventional spiral wound compositepolyamide RO membrane configuration

Highly crystalline PVDFpre-treatment membrane

0.1µm rated membrane fibre, 1.2mm OD, 0.8mm ID

Homogenous fibre material imparting high mechanical strength

© 2012, Pall Corporation

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DTRO configuration

Disc Tube RO (DTRO) membrane alternative configuration

© 2012, Pall Corporation

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Membrane properties & considerationsPre-treatment

Protection of downstream equipment, processes & functionsControl of inlet suspended solids (SDI >3 for RO/NF)Microbial barrier

Integrity assuranceSensitive, automated test to confirm performance

Sustainable operationAbility to reverse pore occlusion (filtration process)Withstand aggressive cleaning proceduresChemical resistance

RODesired rejection rates for ionic speciesMinimal loss of production through flow channel and membrane fouling

© 2012, Pall Corporation

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Operational considerations - sustainability

The pre-treatment stage can face extremely challenging and sometimes often variable feed water conditionsAs the filtration membrane retains solids, it exhibits an increase in transmembrane pressure (TMP) as previously demonstratedThe increase in TMP must be completely recoverable, this is achieved with physical and chemical cleaning regimes

Reverse filtration with previously filtered water in combination with air scourRegular (24 hr – infinite) flux maintenance clean (ClO-)CIP (~monthly – infinite) Chemical clean (ClO- + NaOH)Chemical cleaning can be eliminated with low flux operation

Membrane prefiltration dramatically reduced cleaning burden of downstream ROMembrane prefiltration reduces scale formation in RO by reduced precipitation nucleation

© 2012, Pall Corporation

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Sustainable operation

Rapid increasing TMP associated with elevated algae

Normally increasing TMP

Stable TMPrestoration value

MF TMP trends in heavily contaminated feed water

© 2012, Pall Corporation

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Sustainable operation

Robust and chemically resistant membranes are required to withstand the rigours of feed water duty and the associated aggressive cleaning

procedures over the years of their service life

Highly crystalline PVDF exhibit greater mechanical and chemical resistance (Liu, C. 2007). Factors affecting stability..

• Morphology of polymers: crystalline vs. amorphous polymers• Chemical composition, inc structure of monomers • Molecular architecture - average mol wt & distribution, branching, cross linking.• Chain orientation with respect to the major stresses during operation• Structure and geometry of membranes• The presence of catalysts and inhibitors for chemical reactions relevant to

chemical degradation of polymeric membranes

© 2012, Pall Corporation

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Shipboard Series

AT32 - 40m3/day AT25 - 20m3/day

MF pre-treatmentupgrade DTRO special

Submarine

© 2012, Pall Corporation

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ConclusionsMembrane technology has a long history in water treatment but recent developments in construction and polymer chemistry have enabled significant broadening of this scope – particularly as a conventional media filter replacement optionRobust polymeric prefiltration membranes remove virtually all suspended solids and produce a high quality filtrate with background levels of TSS and SDIMembranes provide dependable barriers to microorganisms in drinking water supply and as such enable treatment of freshwater sources (Bunker feed) Combining MF membranes as pre-treatment to RO enables the latter to function under optimum conditions and produce a treated water quality that is reliably within demanding target limitsThe control of TSS and microbial burden reduces bio fouling of RO membranes and delays scale formation enabling optimum RO production and extended lifeThe robust MF membranes can continuously maintain throughput when challenged with a wide range of inlet solids and algae conditions with effective TMP regeneration

© 2012, Pall Corporation