Optimization of IEX resin regeneration in a zero liquid discharge drinking water treatment plant Klaas Schoutteten De Watergroep / Ghent University / KWR.

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Presentation transcript:

Optimization of IEX resin regeneration in a zero liquid discharge drinking water treatment plant Klaas Schoutteten De Watergroep / Ghent University / KWR

De Watergroep WTW Kluizen WTW De Blankaart Drinking water utility in Flanders, Belgium 3 million domestic customers 163 million m³ drinking water 72% groundwater, 28% surface water water-link WTW Kluizen WTW De Blankaart

Combining IEX and coagulation for NOM removal Current treatment: coagulation flotation New treatment (pilot plant): fluidized bed IEX coagulation flotation Reducing coagulant dose Improving overall NOM removal

IEX + coagulation pilots at 2 WTWs WTW Kluizen (Evergem) 60 000 m³/d DOC: 10 mg/L WTW De Blankaart (Diksmuide) 40 000 m³/d DOC: 13 mg/L

Important site-specific consideration No liquid discharge!  spent brine (high in organics and salts) must be treated on-site  coagulation of organics  solution is topped up with extra NaCl and reused as brine 1 BV brine = max. 1 BV of spent brine  Everything eluting outside of the ‘collected spent brine BV’  into drinking water fraction to be collected as wastewater (= 1 BV) not captured  into drinking water

Important site-specific consideration No liquid discharge!  spent brine (high in organics and salts) must be treated on-site  coagulation of organics  solution is topped up with extra NaCl and reused as brine 1 BV brine = max. 1 BV of spent brine  Everything eluting outside of the ‘collected spent brine BV’  into drinking water regeneration frequency NOM removal Cl- loss into drinking water high low

How important is Cl- loss? Drinking water limit: 250 mg/L Cl- Sources of Cl-: Ion exchange (SO42-, NOM, …  Cl-) Not-collected eluent Front broadening during resin regeneration (advection, dispersion, diffusion, …) Resin swelling after regeneration Coagulation in drinking water (FeCl3) Average Cl- content in feed water: WTW Kluizen: 48 mg/L Cl-, sometimes higher WTW De Blankaart: 121 mg/L Cl-, sometimes higher + higher regeneration frequency Cl- loss important!

Cl- loss, what can we do? Improve regeneration efficiency  reduce regeneration frequency Adapt spent brine collection

Improving regeneration efficiency Dosing method (slow trickling vs intermittent pumping)  slow trickling CT (10’ vs 30’ vs 60’)  min. 30’ H/D (2 vs 4 vs 6 vs 9)  acceptable from 4 on NaCl concentration (5% vs 7,5% vs 10%)  10% Alkaline regeneration (10% NaCl vs 10% NaCl + 2% NaOH)  alkaline: 26% more NOM desorbed

Adapting spent brine collection: ion elution profiles 1 BV spent brine → coagulation → brine Cl- loss → drinking water (35,1 g) SO42- rich fraction → coagulation → drinking water 1 BV spent brine → coagulation → brine Cl- loss → drinking water (12,5 g)

Composition of two spent brine fractions 1st fraction 2nd fraction Volume 0,82 BV 1 BV UV254 42% 58% SO42- 83% 17% Cl- 5% 95%

Advantages of collecting two spent brine fractions Nearly all NOM removed with IEX is processed through spent brine coagulation SO42--rich fraction: coagulation with Fe2(SO4)3 instead of FeCl3 In a later stage: perhaps also SO42- removal from SO42--rich fraction Less NaCl needed to top up spent brine Less SO42- accumulation in collected and recirculated spent brine

One step further: stepwise regeneration Objective: separate desorption of SO42- and NOM Regeneration with: 2 BV of 2% NaCl  will SO42- fraction still require NOM removal? 1 BV of 10% NaCl Additional advantage: 2% NaCl can be made by diluting 10% NaCl brine  ± 1,4 BV of spent brine can be collected

Stepwise regeneration 1st fraction 2nd fraction Volume 2,4 BV 1 BV UV254 27% 73% SO42- 94% 6% Cl- Much better SO42- separation But… Still too much NOM in 1st fraction Too much Cl- in 1st fraction (14 g) (not compensated by extra 0,4 BV collected)

Stepwise regeneration Origin of Cl- in 1st fraction: Co-eluting Cl- with SO42-: 1300 mg Cl-/L Much less loaded resin during 10% NaCl passage = more front broadening Origin of NOM in 1st fraction: Co-eluting NOM with SO42-: 1200 m-1 In transition zone 2% - 10% NaCl  In ZLD locations where Cl- loss should be minimized: single-step regeneration > stepwise regeneration

A special word of thanks: Janus Van Massenhove and Veerle D’Haeseleer klaas.schoutteten@dewatergroep.be