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PPhosphorusRecoveryTechniquesCONTENTSPARTONE
IntroductionPARTTWO
Reserves
SituationPARTTHREE
Techs
for
P-RecoveryPARTFOUR
Discussion1PARTONEINTRODUCTIONINTRODUCTIONWhat
is
Phosphorus?Phosphorusisanonmetalofthenitrogengroupandisessentialforalllifeonourplanet.Phosphaterock/phosphoriteandaregeologicaldepositsofphosphateexistingallovertheworld:sedimentaryandigneousphosphaterockdeposits.Themajorityoftoday’sglobalphosphaterockproductionisusedinagriculturalproductsand/orapplications,mainlyinfertilizers(CisseandMrabet,2023).Cisse,L.,andMrabet,T.(2023).Worldphosphateproduction:overviewandprospects.PhosphorusResearchBulletin,15,21–25.INTRODUCTIONDepletion
of
PhosphorusHowever,
naturalPresources(phosphaterock)aredepleting.And
theregulationsonthedischargeofphosphorushasbeenincreasinglystringent
(Steen,1998).The
potentialtechniquestorecoverphosphorus
fromwastestreamsinviewofenhancingtheavailability
needs
to
be
explored.Existingfull-scaleP-recoverytechniquescan
be
divided
due
to
its
field
among
theliquidphase,
sludge
phase,andsludge
ash.Althoughthefull-scale
P-recoverytechniqueshavebeenshowntobetechnologicallyfeasible,
theeconomicalfeasibility,legislationandnational
policiesarethemajorreasonswhythesetechniquesarenotyetoperational
worldwide.Steen,I.(1998).Phosphorusavailabilityin21stcentury:managementofanonrenewable
resource.PhosphorusandPotassium,217,25–31.2PARTTWORERESERVES
SITUATIONRERESERVES
SITUATIONAgricultural
ApplicationsNon-Agricultural
ApplicationsThe
Utilization
of
PhosphorusFertilizer
industryPesticidesAnimal
fees
supplementsFood
industryHousehold
applicationsMetal
surface
treatmentCorrosion
inhibitionFlame
retardantsMuller,J.,Reinhardt,M.,G¬unther,L.,Dockhorn,T.,Dichtl,N.,Urban,I.,Weichgrebe,D.,Rosenwinkel,K.H.,Bayerle,N.,andVesterager,N.O.(2023).Fundamentalsandfeasibilityofnutrientrecyclingusingtheseaborneprocess.ConferenceontheManagementofResiduesEmanatingfromWaterandWastewaterTreatment,Johannesburg,South-Africa.RERESERVES
SITUATIONMoroccoMost
important
ProducerLow-level
consumptionAsia
(China)High-level
productionExceeding
consumptionFigure1.GlobalproductionandConsumptionofphosphorus(datafromU.S.Geologicalsurvey,2023;IFA,2023).North
AmericaConsiderable
reserves
Large
productionLack
of
high-quality
p-rockCurrent
DistributionRERESERVES
SITUATIONOpen/Close
P-cycleOpen
Phosphorus
CycleBothsolidandliquidsourcesareregardedaswastestreams.Thefocusliesonminimizingthecostofdisposal.Thewasteenterstheenvironment,causingphosphoruslossesandeutrophicationproblems.11%removedinprimarytreatment(primarysludge)20-30%removedinsecondarytreatment(activated/surplussludge)Approximately90%removedandincorporatedintothesewagesludge(CornelandSchaum,2023)Thesludgeproducedendedupinlandfills,incineratorsorinthesedimentsofcanalsandrivers(Mainstoneetal.,2023).Cornel,P.,andSchaum,C.(2023).Phosphorusrecoveryfromwastewater:needs,techniquesandcosts.WaterScienceandTechnology,59,1069–1076.Mainstone,C.P.,Davis,R.D.,House,A.,andDay,M.(2023).Phosphorusandriverecology:tacklingsewageinputs.EnglishNature,Peterborough,England.RERESERVES
SITUATIONOpen/Close
P-cycleClose
Phosphorus
Cycle/Sludge
AshP-Recovery
liquid
phaseP-Recovery
solid
phasePhosphatecanberecoveredfromtheliquidphase,sludgephaseandmono-incinerated(sludgeisincineratedseparatelyfromotherwastes)sludgeash(CornelandSchaum,2023).Thephosphorusrecoveryratefromtheliquidphasecanreach40–50%atmost,whilerecoveryratesfromsewagesludgeandsewagesludgeashcanreachupto90%(CornelandSchaum,2023).ThesubstantialdifferencebetweenthetraditionalPremovalandP-recoveryfromwastewateristhatPremovalaimsatobtainingaPfreeeffluentbytransferringPtosludgewithchemicalandbiologicalprocesses.P-recovery,ontheotherhand,aimsataP-containingproductthatcanbereusedeitherinagricultureorinP-industry.Cornel,P.,andSchaum,C.(2023).Phosphorusrecoveryfromwastewater:needs,techniquesandcosts.WaterScienceandTechnology,59,1069–1076.3PARTTHREETECHS
FOR
P-RECOVERYTECHS
FOR
P-RECOVERYFinal
Products1Lessindependentofp-concentration,butmorerelatedtowastewateralkalinity.TheincreaseofboththesolutionpHvalueandtheCa/Pratioaretwoapproachestooverenegativeinfluenceofcarbonateontheprecipitationofphosphate.Becauserecoveredcalciumphosphateistheeffectivepositionofphosphaterock,itcanbereadilyacceptedbythephosphateindustry(Driveretal.,1999).Calcium
Phosphate2Magnesiumisthelimitingelement
inmostsewagetreatmentapplicationsMgCl2orMgO
isaddedtotheprocessas.Thesaturation
pointofasolutionisstronglyinfluencedbypH,Ifthefeedstream
doesnothavesufficientalkalinity,sodiumhydroxideisaddedand/orCO2
isstrippedfromthesolution.Strutive3Itcanbefurtherprocessedtohighqualityphosphoricacidandotherphosphoruspounds.Phosphoricacidobtainedviawhitephosphorusisthemainsourceofphosphatesusedindetergentsandothernon-fertilizerapplications.White
PhosphorusDriver,J.,Lijmbach,D.,andSteen,I.(1999).WhyRecoverPhosphorusforRecycling,
andHow?EnvironmentalTechnology,20,651–662.From
Wastewater
in
Mixed
TanksTECHS
FOR
P-RECOVERYPHOSPAQ&ANPHOSBoththePHOSPAQandANPHOSprocessesaredevelopedintheNetherlandsfortheprecipitationofstruvite.ThePHOSPAQprocess,developedbyPaques,takesplaceinoneaeratedCSTR.Asaresultofaeration,thepHincreasesbycarbondioxidestrippingandprovidesmixing.Additionally,magnesiumoxideisaddedtothereactortoremovephosphateasstruviteatapHof8.2–8.3.Thestruviteisharvestedfromthebottomofthereactorandtransferredintoacontainerbymeansofascrewpress.Thedryweightoftheharvestedstruviteisaround75%andthecrystalshaveanaveragesizeofaround0.7mm(Driessenetal.,2023).Figure
4.
Process
scheme
of
PHOSPAQDriessen,W.,Abma,W.,VanZessen,E.,Reitsma,G.,andHaarhuis,R.(2023).Sustainabletreatmentofrejectwaterandindustrialeffluentbyproducingvaluablebyproducts.14thEuropeanBiosolidsandOrganicResourcesConference.Leeds,UK.From
Wastewater
in
Mixed
TanksTECHS
FOR
P-RECOVERYPHOSPAQ
&
ANPHOSTheANPHOSprocessisoperatedinbatch
intwoseparatereactors.
Afterthereactionthestruviteisprecipitated,
dewatered
anddried.Theinstallation
isplacedinbetweentheanaerobictreatmentandaerobictreatmentof
thewastewatertreatmentplant.Thestruvitethatisobtainedduringtheseprocessesarefine
crystals
thathavethestructureofsand.Thestruvitewasfirstclassifiedasasecondary
rawmaterialandexportedaswastetoGermanywhereitisused
asrawmaterialfortheproduction
of
fertilizers
ormixedwithotherfertilizers
toobtainagoodnutrientcontent.Figure
4.
Process
scheme
of
PHOSPAQDriessen,W.,Abma,W.,VanZessen,E.,Reitsma,G.,andHaarhuis,R.(2023).Sustainabletreatmentofrejectwaterandindustrialeffluentbyproducingvaluablebyproducts.14thEuropeanBiosolidsandOrganicResourcesConference.Leeds,UK.NuReSysstandsforNutrient
Recycle
System
andisoperatedintworeactors.TheNuReSysprocessdiffersfromtheANPHOSprocesssinceitisoperated
incontinuousmodeinsteadofbatchatalowerresidencetime.Another
differencewiththeANPHOSprocessistheuseofMgCl2asamagnesium
sourceandtheadditionofa29%NaOHsolutiontothecrystallizationreactor
insteadofusingMgO.Thecrystallizationtankisequippedwithasimple
bladeimpellerandaspecificdevelopedandfullyautomatedcontrolalgorithm
ensuresanoptimalpH(8–8.5),reagentdosingandvaryingmixing
intensity.Inthiswaythegrowthofnovelcrystallinematteruponexisting
crystals
occursandpreventsunwantedimpellerorreactorscaling.NuReSysFrom
Wastewater
in
Mixed
TanksTECHS
FOR
P-RECOVERYFigure5.SchematicoverviewoftheNuReSysprocess(modifiedfromMoermanetal.,2023).Moerman,W.,Carballa,M.,Vanderkerckhove,A.,Derycke,D.,andVerstraete,W.(2023).Phosphateremovalinagro-industry:Pilotandfull-scaleoperationalconsiderationsofstruvitecrystallization.Waterresearch,43,1887–1892.PHOSNIXThePhosnixprocessisasidestreamprocessthatenableseffectivephosphateremovalandrecoveryfromthedigesterwastewaterofthesludgetreatmentprocessasgranulatedstruvite(UenoandFuji,2023;Nawa,2023).
Thewastewaterisfedintothebottomofafluidizedbedreactor.Thecolumncontainsabedofgranulatedstruvite,whichactsasaseedmaterialforcrystalgrowth.Magnesiumhydroxideisaddedinamagnesiumtophosphateratioof1:1andthepHisadjustedto8.2–8.8withtheadditionofsodiumhydroxideandbyairstripping(UenoandFuji,2023).Acrystalretentiontimeof10daysallowsthegrowthofpelletsbetween0.5and1.0mminsize,afterwhichtheyarepurgedfromthebottomofthereactorcolumn.Finegranulesofstruviteintheseparatedliquidarereturnedtothereactioncolumntoprovidenewseedmaterialinordertoassurethecontinuityoftheprocess(UenoandFuji,2023;Ueno,2023).Thelargerpelletsarefedintoahopperwherethewatercontentisreducedtolessthan10%.From
Wastewater
in
Fluidized
Bed
ReactorsTECHS
FOR
P-RECOVERYNawa,Y.(2023).P-recoveryinJapan–thePHOSNIXprocess.BALTIC21–PhosphorusRecyclingandGoodAgriculturalManagementPractice,Berlin.Ueno,Y.(2023).FullscalestruviterecoveryinJapan.In:Valsami-Jones,E.(Ed.),Phosphorusinenvironmentaltechnology:Principlesandapplications.London:IWA,p.496–506.Ueno,Y.,andFuji,M.(2023).Threeyearsexperienceofoperatingandsellingrecoveredstruvitefromfullscaleplant.EnvironmentalTechnology,22,1373–1381.CrystalactorFrom
Wastewater
in
Fluidized
Bed
ReactorsTECHS
FOR
P-RECOVERYTheCrystalactorwasoriginallydevelopedtoremovecalcium
fromdrinkingwater.
And
EBPRistreatedintheCrystalactortoconcentratethephosphateinasidestream.Thephosphaterichflowiscollectedinbuffertanks.Ascarbonatesinhibitcalciumphosphateprecipitation,theyareremovedinacascadestripperbeforethewastewaterflowenterstheCrystalactor.The
Crystalactorconsistsofacylindricalfluidizedbedreactorinwhichfiltersandisusedasseedmaterial.Thestrippedwastewaterispumpedthroughthereactorinanupwarddirection,andatsuchahighvelocitythepelletbediskeptinafluidizedstate.EfficientcalciumphosphatecrystallizationrequiresapHof9.Therefore,Ca(OH)2solutionisaddedtothereactorandthedosageiscontrolledbypHmeasurement.Asthepelletsgrowinsizeandmass,theysinktothebottomofthereactor.Therecoveryratecanreach70–80%(CornelandSchaum2023).Cornel,P.,andSchaum,C.(2023).Phosphorusrecoveryfromwastewater:needs,techniquesandcosts.WaterScienceandTechnology,59,1069–1076.PEARL
&
WASSTRIPThePERALprocessrecoversstruvitefromthesludgeliquorofananaerobicdigester,ingfromaWWTPwithbiologicalphosphorusremoval.Thetechnologyisbasedoncontrolledchemicalcrystallizationinanup-flowfluidizedbedreactorwithmultiplereactivezonesofincreasingdiameters.Theprocesshastheadvantageofallowinglargestruvitepelletsfrom1.5to4.5mmindiametertobekeptinsuspensioninthebottomofthereactorwithoutwashingoutfinecrystalnucleifromthetopofthereactor.Struvitecrystallizationiscontrolledbyabinationofmagnesiumdose,pHcontrolandbymeansofatreatedeffluentrecycle(Kochetal.,2023).WASSTRIPstandsforWasteActivatedSludgeStrippingandisdesignedtoremoveinternalphosphorus.Thisbinationofthetwoprocessesresultsinahigherstruviteproductionandpreventsscalinginthedigesterandthedewateringapparatus.From
Wastewater
in
Fluidized
Bed
ReactorsTECHS
FOR
P-RECOVERYBritton,A.(2023).P-recoveryinNorthAmerica–Ostara’sPEARLTMprocess.PhosphorusRecyclingandGoodAgriculturalManagementPracticeBerlin,Germany,September28–30.Koch,F.A.,Mavinic,D.S.,Yonemitsu,N.,andBritton,A.T.(2023).Fluidizedbedwastewatertreatment.U.S.PatentNo.7622047B2.75%70%55%AIRPREXSEABORNETHERMOCHEMICAL
&
ELECTROTHERMALpH
increases
by
stripping
carbon
dioxideInternal
recycle
allows
the
structive
crystal
to
grow.The
recovered
struvite
quality
is
conform,
except
for
the
water
solubility.An
acidification
of
the
sludge
by
the
addition
of
sulfuric
acidThe
sulfur-rich
digester
gas
is
used
to
precipitateNutrient
are
recycled
Forthedryprocess,phosphorusis
recoveredbymeltingtheash.Used
assecondary
materialinthephosphateindustryfortheproductionofelementary(white)
phosphorusTwothermalprocesses
arerunningfullscale.Theremainingash(afterP-recovery)canbemixedwithcement
or
concrete.Bricksorsomeotherobjectscanbemadeofashortheashcanbe
melted
andsolidifiedasaceramic
materialSewage
Sludge
(Ash)From
Sewage
Sludge
(Ash)TECHS
FOR
P-RECOVERY4PARTFOURDISCUSSIONDISCUSSIONThe
Liquid
Phase
Vs.
The
Sludge
(Ash)The
Liquid
PhaseThe
Sludge
(Ash)a
simple
processrecycled
rate
40-50%Structive
or
calcium
phosphate
percipitated
in
a
stirred
tank
reactor
(much
simpler
to
operate)
or
fluidized
bed
reactor.Calcium
phosphate
are
seldom
used
at
full
scalea
complex
processhigher
recovery
rateslarge
amount
of
chemicals
and/or
energy
and
process
steps
requiredhigh
investment
and
operational
costsADDYOURTEXTSimpletechniquessuchastheprecipitationofphosphatefromtheliquidphaseseemtobepreferred(Satoriusetal.,2023),i.e.lesscostlyapproachesevenattheexpenseofloweryields.Phosphorusrecyclingfromashhastobeconsidered,forthehighcostofincinerationisnotassignedtotherecoveryofphosphorus.aluminumsaltsareproposedasanalternativetoprecipitatephosphatefromthewastewater.thephaseoutofthedirectuseofsludgetofarmlandinmanycountries.Theuseofphosphorusrecoverytechniqueswillincreaseinthefuture.Inthatcase,theuseofalternativeenergywouldbebeneficialifstruviteisprecipitatedfromwastewater.DISCUSSIONFuture
PerspectivesSatorius,C.,vonHorn,J.,andTettnborn,F.(2023).Phosphorusrecoveryformwastewater:ExpertsurveyonPresentuseandfuturepotential.WaterEnvironmentResearch,84,313–323.DISCUSSIONConclusionTherecovery
source
ofphosphorus
must
include
municipal
and
industrialwastewaterandsubsequentlyusingitasafertilizer.P-recoveryhasbeenwidelystudiedandanumberoffull-scaleinstallations
forP-recoveryarealreadyoperational,showingthat
P-recoveryistechnicallyfeasiblePhosphatecanberecoveredfromthe
liquidphase
(40-50%
recovery
rate),sludgephase(ash;
80-90%)
of
awastewatertreatmentplant.
P-recoveryfromtheliquidphaseisasimpleprocess,whereasP-recovery
fromthesewagesludgeashhasahigherenergyconsumptionandhigher
investmentcost.Themostappropriatewayvaries.Britton,A.(2023).P-recoveryinNorthAmerica–Ostara’sPEARLTMprocess.PhosphorusRecyclingandGoodAgriculturalManagementPracticeBerlin,Germany,September28–30.Cordell,D.,Rosemarin,A.,Schr¬oder,J.J.,andSmit,A.L.(2023).Towardsglobalphosphorussecurity:Asystemsframeworkforphosphorusrecoveryandreuseoptions.Chemosphere,84,747–758.Cornel,P.,andSchaum,C.(2023).Phosphorusrecoveryfromwastewater:needs,
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