water treatment lecture 5 eenv
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water treatmentTRANSCRIPT
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IslamicUniversityofGazaEnvironmentalEngineeringDepartment
Water TreatmentWaterTreatmentEENV4331
Lecture5:Filtration
Dr.Fahid Rabah
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5.FiltrationinwaterTreatment
5.1 Definition of Sedimentation:Filtration is a solid liquid separation process in which theliquid passes through a porous medium to remove asmuch fine suspended solids as possible
5.2 Locations of filtration tanks in water treatment:Filtration tanks are used in all types of water treatmentplants except for disinfection treatment plants. SeeFigures 5.1 through 5.4 illustrating the location of filtrationtanks.
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River
Screen
RiverWater
PreSedimentation
Screen
Coagulation FlocculationSedimentation
DistributionDisinfection StorageFiltration
Figure5.1:FiltrationTreatmentPlant (RiverWater)
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Screen
Surfacewater
S di t tiCoagulation Flocculation
Sedimentation
DistributionDisinfection StorageFiltration
Figure5.2:FiltrationTreatmentPlant
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GroundWaterWater
RapidMixing Flocculation Sedimentation Recarbonation
DistributionDisinfection StorageFiltration
Figure5.3:SofteningTreatmentPlantSinglestagesofteningsoftening
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GroundWaterwell
FiltrationAeration
DistributionDisinfection Storage
Figure5.4:AerationTreatmentPlant( iron and manganese removal plant)(ironandmanganese removalplant)
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5.FiltrationinwaterTreatment5 3 Need for filtration:
Settlingisnotsufficienttoremoveallparticlesand5.3 Need for filtration:
flocsfromwater. FiltrationNeededforfineparticlesnotremovedbydi t tisedimentation.
FilterscanalsocaptureGiardia cysts, viruses,andasbestos fibersasbestosfibersTypicaloverflowqualitiesfromsedimentationtanksrangefrom1to10NTU.Filtration,usuallyrapidsandfiltration,isthenemployedforfurtherpolishing,i.e.togettheturbidity to lower than 0 5 NTU (as required byturbiditytolowerthan0.5NTU(asrequiredbylegislation).Rapid sand filtration after prior sedimentation is the
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Rapidsandfiltrationafterpriorsedimentationisthemostcommonconfigurationworldwide
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5.FiltrationinwaterTreatment
5.4 Types of filters used in water treatment:Granular material filters are the most used types of filtersin water treatment. Usually sand, anthracite, and Garnet.y
There are three types of granular filters:1. Single medium filters :
one type of media is used: either sand or anthraciteone type of media is used: either sand or anthracite
2. Dualmedia filters: two types of media is used usually sandand anthraciteand anthracite
3. Multimedia filters: three types of media are used usuallysand , anthracite , and Garnet
Most famous filters in water treatment are Rapid Sand Filters.Most famous filters in water treatment are Rapid Sand Filters.
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5.FiltrationinwaterTreatment
5.5 Geometry and components of Rapid Sand Filter:y p p
Rapid sand filters are always rectangular tanks.
Figures 5.5 to 5.10 show typical Rapid sand filters used inwater treatment.
Main components of Rapid sand filter are: Main components of Rapid sand filter are:1. A concrete tank2. Filter media3 Under drain system3. Under drain system4. Backwash system: pressurized water and air lines
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Figure5.5:Rapidsandfiltercomponents
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Figure5.6a:Rapidsandfiltercomponents: withgraveland
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p p gperforatedpipesunderdrainsystem
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Fi 5 6b
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Figure5.6b:Rapidsandfiltercomponents: withgravelandperforatedpipesunderdrainsystem
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Figure5.7:Rapidsandfiltercomponents: withgraveland
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p p gperforatedpipesunderdrainsystem
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Fi 5 8
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Figure5.8:Rapidsandfiltercomponents:withductsunder drainsystem
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Figure5.9:Rapidsandfiltercomponents:withnozzleunder drainsystem
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5.FiltrationinwaterTreatment
Figure 5.10 :Figure5.10:Rapidsandfilterperforatedslabandnozzleunderdrain
system
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5.FiltrationinwaterTreatment
Figure5.11:Nozzle used in Rapid sand filterNozzleusedinRapidsandfilterunderdrainsystem
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5.FiltrationinwaterTreatment
5.6 Operation of Rapid Sand Filter:
There are two modes of operation of Rapid sand filterThere are two modes of operation of Rapid sand filter
Filtration mode ( see Figure 5.12 )
Backwashing mode ( see Figure 5.13 )
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5.FiltrationinwaterTreatment
5 7 Filtration mode:
Waterflowsdownwardthroughabed5.7Filtrationmode:
ofsandandgravel Particles are captured on and between Particlesarecapturedonandbetweensandgrains
Filteredwateriscollectedintheunderdrain, sent to disinfectiondrain,senttodisinfection
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5.FiltrationinwaterTreatment
5 8 Backwash mode:
Sand is backwashed when
5.8Backwashmode:
Sandisbackwashedwhen Itbecomesclogged,or Turbidityoffilteredwatergetstoohigh
During backwash, water is pumpedDuringbackwash,waterispumpedupwardsthroughthesandbed
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5.FiltrationinwaterTreatment
Sandbecomesfluidized,andparticlesareflushedfromthesand
Dirtybackwashwaterispumpedintoasettling pond and eithersettlingpond,andeither Recycledbackintoplant,orDi d Disposed
Backwashingcanconsume1%to5%ofaplantsproduction
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22Figure5.12:Rapidsandfilterduring
filtration
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Figure5.13:Rapidsandfilterduringbackwashing
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5.FiltrationinwaterTreatment
5.9Filtermediaproperties
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Figure5.14:filtermediagraindistribution
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5.FiltrationinwaterTreatment
h f l d d h d h lThesefiltersusesandandcrushedanthracitecoalonagradedgravelbase.
Medialayersarearrangedinacoursetofinegradationinthedirectionofflow,whichallowsgreaterdepthofpenetrationoffloc particles.p
Multimediafiltersareselectedwithspecificgravitiessothatmoderate intermixing between media layers occurs duringmoderateintermixingbetweenmedialayersoccursduringbackwashing.
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5.FiltrationinwaterTreatment5.10FiltermediapropertiesThefiltermediaischaracterizedbytwomainparameters: the effective size and the uniformity
Effectivesizeofthefiltermedia
parameters:theeffectivesizeandtheuniformitycoefficient.
Th ff ti i f th di i th di tTheeffectivesizeofthemediaisthediameterthat10%ofthefiltermediaislessthanitsizeandisdenotedasd10.
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ddU
Uniformitycoefficientofthefiltermedia
10dU=Uniformitycoefficientd60 =sievesizethatpasses60%byweightd10 =sievesizethatpasses10%byweight
d60 andd10 arefoundbysieveanalysisofthemediatobeusedinthefilter.
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Anotherimportantsievesizeisd90 thatisusedtocalculatethebackwashrate.
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5.FiltrationinwaterTreatment
27Figure5.15:Rapidsandmedialayers
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Figure5.16:Rapidsandmedia layersmedialayers
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5.FiltrationinwaterTreatmentTable 5.1Table5.1
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5.FiltrationinwaterTreatmentTable 5 2Table5.2
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5.FiltrationinwaterTreatmentTable 5.3Table5.3
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5.FiltrationinwaterTreatment
Figure5.17:Headlossandeffluentturbidityincreasewithtimeduringfiltration
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y g
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5.FiltrationinwaterTreatment
Figure5.14:Headlossinrapidsandfilter during filtration cycle
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filterduringfiltrationcycle
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Figure5.14:Headlossinrapidsandfilter
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g p
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Headlossinacleanfilter
CarmenKozeny equation:
2 vAV
gk
Lh 2
3
2)1(
dAV
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sAQv
Where,k=dimensionlesscoefficient,5forsand,6foranthracite;v filtration rate m3/m2 d or filtration velocity m/d
s
v=filtrationratem3/m2.d,orfiltrationvelocitym/d.A=thegrainsurfacearea;As=surfaceareaofthesandfilter;V= the grain volume;V=thegrainvolume;=filterporosity;around0.40forsandfilter=shapefactor;1forsphericalparticles,0.70forsand;=dynamic viscosity; N s/m2
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=dynamicviscosity;N.s/m=waterdensity;kg/m3
h=headlossincleanfilter,m
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Example5.1:
Adualmediafilteriscomposedof0.30manthracite(meanparticlesize0.20mm)thatisplacedovera0.60mlayerofsand(meanparticlesize0.70mm)
/withafiltrationrateof9.78m/h.Assumethegrainsphericity =0.75andporosity()=0.40forboth.Estimatetheheadlossinthecleanfilterat150C.
A H d l i th th it lA.Headlossintheanthracitelayer:
mh 0508.000272.0*0020*750
6400*1000*819
)40.01(*00113.0*6*30.02
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B.Headlossinthesandlayer:
002.0*75.040.0*1000*81.9 3
2
mh 6918.000272.0*007.0*75.0
640.0*1000*81.9
)40.01(*00113.0*5*60.02
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B.Headlossinthesandlayer:y
mhtotal 743.06918.00508.0
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Headlossduringfiltration(None clean filter)(Nonecleanfilter)
Where
filterdtl bVavh Where,v=filtrationratem3/m2.d,orfiltrationvelocitym/d.a,b=coefficientsdependingonthefiltermediaproperties;Vfilt d = filtered volume per unit area of filter since last backwash; m3/m2Vfiltered filteredvolumeperunitareaoffiltersincelastbackwash;m /m(hl)t =headlossatanytime(t),m
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Example5.2:
Afilterhasaheadlossof0.30mwhenclean(newlywashed),and1.30mafter24hrsoffiltrationatarateof1.5L/s.m2 .Estimatetheheadlossbothimmediatelyafterbackwashand10hrslater,ifthefiltrationrateischangedto2L/s.m2 .
A.Estimatethevaluesofaandb:
5.15.1 0*
10005.130.0 ba
3600*24*1000
5.1*1000
5.130.1 ba
Bysolvingthe2equationssimultaneously,a=200,b=5.14
B.Calculateheadlossforthenewflowrate:
2 mbH 40.00*20010002
0
mH 88.13600*10*10002*14.5200
10002
10
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1000100010
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FiltrationhydraulicsCalculations
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FiltrationhydraulicsCalculations
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FiltrationhydraulicsCalculations
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Calculationsoffilterbackwashrate
Thebackwashflowrateiscalculatedusingthefollowingequations:
90
5.0
90
7.330408.069.1135d
Gd
v nb
3d 2
390
gsd
Gn
Where,b k h t 3/ 2 d
bdesignb vv 3.1vb =backwashratem3/m2.d,d90 = sievesizethatpasses90%byweight=dynamicviscosity;N.s/m2
= water density; kg/m3 = waterdensity;kg/m3
s = filterparticlesdensity;kg/m3
Gn =Galileonumber,dimensionlessg = gravitational acceleration m/s2
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g= gravitationalacceleration,m/s
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Calculationsoffilterexpansion
Theexpansionduringbackwashiscalculatedusingthefollowingequations:q
ee LL
11 22.0
s
designbe v
v s
Where,L= beddepthduringfiltration,mL = expanded bed depth mLe =expandedbeddepth,me =expandedbedporosity,dimensionless=bedporosityduringfiltration,dimensionlessv = settling velocity of the filter particles m/svs=settlingvelocityofthefilterparticles,m/s
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Calculationsofheadlossduringfilterbackwash
Headlossduringbackwashingiscalculatedusingthefollowingequation:q
seeLh 1
Where,Le =expandedbeddepth,me =expandedbedporosity,dimensionless
d k / 3 =waterdensity;kg/m3
s =filterparticlesdensity;kg/m3
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BackwashhydraulicsCalculations
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BackwashhydraulicsCalculations
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BackwashhydraulicsCalculations
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BackwashhydraulicsCalculations
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FiltrationhydraulicsCalculations
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