INFRASTRUCTURE - Sewage Removal System - Handout
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Transcript of INFRASTRUCTURE - Sewage Removal System - Handout
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CIVILENGINEERINGII
INFRASTRUCTURE:
SEWAGEREMOVALSYSTEM
Wastewater
Usedwater(liquid)andsolidsthatflowtoand
t roug t ewastewaterco ect onsystem.
Awastewatercollectionsystemconsistsofall
facilitiesforthecollection,transportation,
,
,
wastewater.
Wastewater
Thetypicalwastewatertreatmentplantis
1. Protectpublichealth.
2. Protectpublicwatersupplies.
3. Protecta uaticlife.
4. Preservethebestusesofthewaters.
5. Protectadjacentlands.
Wastewater
Theprincipalsourcesofdomesticwastewater
nacommun tyaret eres ent a areasan
commercialdistricts.
Otherimportantsourcesinclude:
stormwater(runoff)
Groundwater(infiltration).
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Wastewater:Sources
Wastewaterisgeneratedbyfivemajorsources:
1. Humanandanimalwastes
2. Householdwastes
3. Industrialwastes
4. Stormwaterrunoff
5. Groundwaterinfiltration
Wastewater:Classification
Wastewatercanbeclassifiedaccordingtothesourcesofflows:
. ,householdwastes,smallamountsofgroundwaterinfiltrationandsmallamountsofindustrial wastes.
2. Sanitarywastewater Consistsofdomesticwastesandsignificantamountsofindustrialwastes.
3. Industrialwastewater Consistsofindustrialwastesonly.
. om ne was ewa er ons s so acom na ono san arywas ewa eran stormwaterrunoff.Allthewastewaterandstormwaterofthecommunityistransportedthroughonesystemtothetreatmentplant.
5. Stormwater Containsaseparatecollectionsystem(nosanitarywaste)thatcarriesstormwaterrunoffincludingstreetdebris,roadsalt,andgrit.
Wastewater:Classification
Compositionof DomesticSewage
TypeofWastewater SourceofWastewater
GrayWater
Washingwaterfromthe
kitchen ,bathroom,laundry
(withoutfecesandurine).
BlackWater Waterfromflushtoilet(feces
andurinewithflushedwater).
YellowWater Urinefromseparatedtoilets
andurinals.
Wastewater:Characteristics Physical
1. Color
2. Odor
3. Temperature4. Flow
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Wastewater:Characteristics Biological
Bacteria,viruses,andparasitesmakeupthebiologicalcharacteristicsofwastewater.
Thefeedingactivitiesoftheseorganismsassistindecomposingwastewater.
Aerobicbacteriadecomposeorganicmatterinthepresenceoffreeoxygen.
Anaerobicbacteriadecomposeorganicmatterthatisshutofffromfreeoxygen,suchasintheinteriorofamassoffecesoradeadbody.
Theproductsofanaerobicdecompositionhaveanextremelyunpleasantodor.Matterinwhichthisconditionexistsissaidtobeseptic.
Alargenumberofthebacteriainwastewaterarecoliform bacteria thosefoundinthedigestivetractofnormalhumans.
Wastewater:CollectionSystems
Wastewatercollectionsystemscollectandconveywastewatertothetreatmentplant.
The com lexit of the s stem de ends on the size of the communit and the t eofsystemselected.
SeparateSystem SanitarySewer:Carriesdomestic andindustrialwasteinadditiontoinflowandinfiltration.
StormSewer:Carriesstormwater,replacesnaturaldrainage
Thesizeofthepipesaremuchsmallerthanacombinedsewersystem.
Minimizesthetotalquantityofsewagewhichleadstothefollowingadvantages: Smallerpumpingstations
Usedforbothstormwaterandwastewater.
Preferredforareaswithlongrainyseasons.
Wastewater:CollectionSystems Wastewater:CollectionSystems
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Wastewater:CollectionSystems
GravityCollectionSystem
Mostsewersaredesignedtoflowbygravity
nc u essewerp pe rom ome osep c an or oamunicipalcollectorpipe
Gravitysewersmustfollowthetopographyoftheland
thecollectionlinesareslopedtopermittheflowtomovethroughthesystemwithaslittlepumpingaspossible.
Wheregravityflowisnotpossible,pumpsareused
Largemunicipallift(pump)station
Theslopeofthelinesmustkeepthewastewatermovingat
avelocity(speed)of2to4ft/sec.
Wastewater:CollectionSystems
ForceMainCollectionSystem wastewateriscollectedtocentralpointsandpumpedunderpressureto
thetreatmentplant.
.
Theuseoftheforcemainsystemallowsthewastewatertoflowtothetreatmentplantatthedesiredvelocitywithoutusingslopedlines.
VacuumSystem
wastewatersarecollectedtocentralpointsandthendrawntowardthetreatmentplantundervacuum.
Thesystemconsistsofalargeamountofmechanicalequipmentandrequiresalargeamountofmaintenancetoperformproperly.
Generally,thevacuumtypecollectionsystemsarenoteconomicallyfeasible
PumpingStations
providethemotiveforce(energy)tokeepthewastewatermovingatthedesiredvelocity.
Theyareusedinboththeforcemainandgravitysystems.
SewerHydraulics
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SewerHydraulics SewerHydraulics
Findthediameterofthepiperequiredtocarry3
. partially;d/D=0.67,slope=0.4%,n=0.013.
1. Findtheflowangle
2. FindQp/Qf
3. Ca cu ateQf4. Findthediameterofthepipe(D)
5. Findthepartialflowvelocity(Vp)
ManningsRoughnessCoefficientnforVariousTypesofPipe
Example SewerHydraulics
Assumethesewerlinegradegivesasewer
ve oc tyo . m sw t a a u sewer ow.
Theslopeofthelineis0.0081.Whatisthe
diameteroftheuncoatedcastironsewerline?
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DesignCriteria
Wastewaterflow Flowvariesaccordingto:
1. Theseason
2 . We at he rcondidtions
3. Weekofthemonth,dayoftheweekandtimeoftheday.
Estimatepeakflowisused
Estimationofthedesignflow,Qdes: Percapitawastewaterflowdependsuponrateofwatersupplytothecommunityandrateof
groundwaterinfiltration.
Averagedailywaterconsumptionpercapitafordomesticareas,Qavg Averagedailywaterconsumptionpercapitaforinstitution,Qavg Averagedailywaterconsumptionforcommercialandindustrialareas.
Infiltration/Inflow:
Qinfl Qinfil Qdes =Qmax+QVI QvI =Qinfl +Qinfil Qmax=0.8xQavg xPf (0.8=80%returnfromwatersupply)
DesignCriteria
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DesignCriteria Example
Agravitypipeservesacommunityof50,000
n a tants. e engt o t ep pe s m
andtheaveragewaterconsumptionis120
L/c/d.Useaninfiltrationrateof30m3/day.km,
andawastewaterproductionrateof80%.
Neglecttheinflowrate.CalculateQdes and
Qmin.
DesignCriteria Example
SewerAppurtenancesStreetGutter
Atriangleopenchannelalongthecurbstoneofstreetswhichcarrythestormwateralongstreetstotheinlets.
FlowinastreetguttercanbecalculatedbytheManningformula,modified for a trian ular utter crosssection
Thewaterdepthatthecurvecanbecalculatedfromtheflowandthestreetcrosssectionandslope.
The
width
over
which
the
water
will
spread
is
equal
to
yz.
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SewerAppurtenances
SewerAppurtenances SewerAppurtenances
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SewerAppurtenances SewerAppurtenances
Manholes
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PipesMaterialsandLoadsPipesMaterialsandLoads
Loadsonsewerlinesareaffectedbyconditionsofflow roundwater ad acent earth andsuperimposedsituation.
Commontrenchcutsforsewerpipes
PipesMaterialsandLoadsLoadsduetobackfill
Dependson: Trenchwidth
Depthofexcavation
Unitweightofthefillmaterial
Frictionalcharacteristicsofthebackfill
W=verticalloadonpipeasaresultofbackfill,(lb/ftorN/m)
C=dimensionlessloadcoefficientbasedonthebackfillandratiooftrenchdepthtowidth.
C= wor =unitweightofbackfill,(lb/ft3 orkg/m3)
B=widthoftrenchattopofsewer,(ftorm)
k=ratiobetweenactiveinternalpressureandexternalverticalpressure
F=frictioncoefficientbetweenthebackfillmaterialsandthetrenchverticalsides.
PipesMaterialsandLoads
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WastewaterTreatment
Thebasicstepsinwastewatertreatmentare:
Preliminarytreatmenttoprotectplantoperation
Settling
toremovesolids
Biologicaltreatmenttoremoveorganicmatter
Disinfectiontoremovepathogens
Solidsprocessingtoprovidesafefinaldisposal.
WastewaterTreatment
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Wastewater:SecondaryTreatment
Themainpurposeofsecondarytreatmentsometimes referred to as biolo ical treatment is
toprovideBODremovalbeyondwhatisachievablebyprimarytreatment.
RemovesBODanddissolvedandcolloidalsuspendedorganicmatterbybiologicalaction.
,
dioxideandmoreorganisms
Secondarytreatmentproducesaneffluentwithnormorethan30mg/LBODand30mg/LTSS.
Wastewater:SecondaryTreatment
ActivatedSludge Secondaryorbiologicaltreatmentisperformedina
tankcontaininga"soup"ofstarvedmicrobescalledactivatedsludge.Likeus,thesemicrobesrequireairtolive(theyareaerobicorganisms)andthusairispumpedintothetank.
Microorganisms inthisaerationtankusethedissolvedandparticulateorganicmatterasfood,producingmore
.
Thusthewastematerialsthatlefttheprimaryclarifierarechangedintomicroorganisms whichcanbecollectedandseparatedfromthewater.
Wastewater:SecondaryTreatment
Clarifier
Separateoutthemicroorganisms(activatedslud e so that ust clean water is left.
Some
of
the
solids
collected
in
the
secondary
clarifier(returnactivatedsludge)aresentbacktotheaerationtanktotreatmorewastewaterandtheexcess(wasteactivatedsludge)ispumpedto
treatment.
Thecleanwaterthatflowsoutthetopoftheclarifierissentalongfordisinfection.
Wastewater:Disinfection
Wastewatereffluentisdisinfectedtoprotectublic health in eneral.
Can
be
accomplished
by
adding
chlorine
or
by
exposingthewastewatertoultravioletlight(UV).
Disinfectionwithchlorinecanproducechemicalswhicharedangeroustopublichealth,soalternativessuchasultravioletlightarebecomingmorepopular.
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Wastewater:TertiaryTreatment
Themethodsandprocessesthatremovemore
substances)fromwastewaterthanaretakenoutbyconventionalbiologicaltreatment.
Inotherwords,advancedwastewatertreatment
followssecondarytreatmentorthatincludesphosphorusremovalornitrificationinconventionalsecondarytreatment.
MeasuringPlantPerformance
Toevaluatehowwellaplantortreatmentunitprocessisoperating,performanceefficiencyorpercent
.
PlantPerformanceandEfficiency
%Removal=[InfluentConcentration EffluentConcentration]x100
InfluentConcentration
UnitProcessPerformanceandEfficiency
Theconcentrationenteringtheunitandtheconcentrationleavingtheunit(i.e.,primary,secondary,etc.)areusedtodeterminetheunitperformance.
MeasuringPlantPerformance
PercentVolatileMatterReductioninSludge
MeasuringPlantPerformance:
HydraulicDetentionTime Thetermdetentiontime(DT)orhydraulicdetentiontime(HDT)
referstotheaveragelengthoftime(theoreticaltime)adropof, ,
channel.
Itiscalculatedbydividingthewaterorwastewaterinthetankby
the
flow
rate
through
the
tank.
Theunitsofflowrateusedinthecalculationaredependentonwhetherthedetentiontimeistobecalculatedinseconds,minutes,hoursordays.
Detentiontimeisusedinconjunctionwithvarioustreatmentprocesses,inc u ingse imentationan coagu ationan flocculation.
Detentiontimeisassociatedwiththeamountoftimerequiredforatanktoempty.
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HYDRAULICDETENTIONTIME
DetentionTimeinDays
DetentionTimeinHours
DetentionTimeinMinutes