CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14...
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CEE 371 Lecture #14 11/21/2009
Lecture #14 Dave Reckhow 1
CEE 371Water and Wastewater
Updated: 21 November 2009
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Water and Wastewater Systems
Lecture #14
David Reckhow CEE 371 L#14 1
Drinking Water Treatment: ChlorinationReading: Chapter 7, pp.233-238, 259-262
Forms of Chlorine applied to waterChlorine gasg
Cl2
Sodium Hypochlorite liquid (Hypo) NaOCl
Calcium Hypochlorite solid
Traditional method
Becoming more common
Ca(OCl)2
Other formsOrganic-N based compounds and resins
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Chlorine Cont.The hypochlorous acid
HOCl H + OCl+ -↔
on o
f tot
al (α
)
0 4
0.5
0.6
0.7
0.8
0.9
1.0
α0=HOCl/CT α1=OCl-/CT
The hypochlorous acid ionizes to hypochlorite.
Although both hypochlorous acid and hypochlorite are disinfectants, hypochlorous acid is much more powerful
pH4 5 6 7 8 9 10 11
Frac
tio
0.0
0.1
0.2
0.3
0.4
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acid is much more powerful. The equilibrium reaction is:
][]][[101016.3 5.78
HOClOClHxKa
−+−− ===
QuestionAt pH 8.5, the percent of the total free p , pchlorine that is in the most effective form is:A. 0%B. 9%C. 27%D. 50%E. 73%F. 91%G. 100%
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Chlorine reacts quickly with substances in water so
Chlorine demand Iq y
that the effective residual is always less than the doseChlorine residual = chlorine dose – chlorine demand
The effective concentration; this is This is what you
Chlorine demand is usually measured for a particular water and it may depend on the contact time and dose
It may be estimated from known water quality
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concentration; this is the “C” in “Ct” add to the water
Chlorine Demand IISummation of at least 3 typesyp
Chlorine demand = inorganic demand + fast organic demand + slow organic demand
Inorganic demand is based on known stoichiometry – see next slidestoichiometry see next slideBoth types of organic demand are highly variable
As a first approximate you can use:Fast + slow organic demand = 0.25*TOC
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Inorganic Chlorine Demand IMajor inorganic ions responsible & reactionsj g p
Manganese: 1M/M
Iron: 0.5M/M
Sulfide: 4M/M when sulfate is product
+−+ ++→++ HClMnOOHMnHOCl 3222
−−++ ++→+ OHClFeFeHOCl 21
2132
21
Ammonia: 1.5 M/M, when nitrogen gas is produced
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+−−− ++→+ HClSOHSHOCl 544 24
+−+ +++→+ HOHClNNHHOCl 21
221
21
221
421 2111
Inorganic Chlorine Demand IIMolar Calculation
Where all concentrations are in moles/liter
Mass-based Calculation
][5.1][4][5.0][][ 422 +−++ +++=− NHHSFeMnDemandInorganic
)(67)(88)(630)(31 22 +−++ +++ NHHSFeMnDemandInorganic
Where all concentrations are in mg/L
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)(6.7)(8.8)(63.0)(3.1 4+++=− NHHSFeMnDemandInorganic
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QuestionYou have a raw water with the following gcharacteristics
TOC = 2 mg/L, Fe+2=0.5 mg/L, Mn+2=0.2 mg/L, HS-=0.1 mg/L, NH4
+=0.3 mg/LWhat is the chlorine demand?A 0 3 mg/LA. 0.3 mg/LB. 0.9 mg/LC. 3.7 mg/LD. 4.2 mg/LE. 5.5 mg/L
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Cl2 gas: larger installations1 ton cylindersy
With small (150 lb) vertical tanks in background
Requires separate sealed room orsealed room or bldg.
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Avon, CO
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Commercial Chlorinatorfeed
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Fig 7-18; pg. 236 in H&H
Large chlorinatorchlorinator
Vacuum created at aspirator injectorinjector
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Figure courtesy of Wallace & Tiernan Co.
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Dose controlFlow pacingp g
Small home system
F ll l
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Fig 7-19; pg. 237 in H&H
Full-scale municipal system
Dose controlFeed back system
Adjusts for varying chlorine demand
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Fig 7-19; pg. 237 in H&H
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Hypochlorite Dosingdafd
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Chlorine tanksLeft side is currently feedingRight side is on reserve
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Chlorine feeding systemg y
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Dose adjustment knob
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Chloramines I Inorganic chloramines are formed by the reaction of free chlorine with ammonia The reaction is stepwise giving monochloraminewith ammonia. The reaction is stepwise, giving monochloramine (equation 1) followed by dichloramine (equation 2). The dichloramine is quite unstable, forming nitrogen gas (equation 3) and some nitrate. This decomposition is responsible for the classic breakpoint chlorination phenomenon.
NH3 + HOCl --------> NH2Cl + H2O (1)
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3 2 2 ( )
NH2Cl + HOCl --------> NHCl2 + H2O (2)
NH2Cl + NHCl2 --------> 3H+ + 3Cl- + N2 (3)
Chloramines IIAdvantagesg
Less reactive so that it persists longer in distribution systemsMay be better at penetrating biofilms on pipe wallsForms smaller amounts of disinfection byproducts (DBPs)
DisadvantagesWeak disinfectant; appropriate as a secondary disinfectant onlyMay lead to tastes & odorsMay stimulate nitrification
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Chloramines: Breakpoint CurveMCA = monochloramineDCA = dichloramine
The Breakpoint
Combined Free
DCA = dichloramineFRC = free residual chlorineNmg
Clmg−− 26.7
NmgClmg−− 24
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MCA DCA FRC
Chlorine Dose
Compare with Fig 7-17 in H&H, pg. 234
Northampton’s Ground Storage4.0 MGTwo Concentric cells
Can be isolated to service one while keeping the other in service
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in service
NaOCl added just prior to entry
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Raw Water
Reservoirs &Reservoirs &Transmission Mains
Clearwell
9 Sept 06
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Clearwell
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Clearwell
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Clearwell
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Clearwell
29 Sept 06
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ClearwellFrom the plant site
29 Sept 06
ClearwellDropping a panel pp g pinto position
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Clearwell
29 Sept 06
Northampton Ground Storage
Finished water storage at plantFinished water storage at plantKnow as a “Clearwell”
View from Outer ringUnder construction
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ClearwellExit portalp
29 Sept 06
ClearwellIn outer ring, looking SW?g, g
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Clearwell or Ground StorageMulti-purposep p
Chlorine contact tank for achieving “Ct”Giardia controls
3 log Giardia is more restrictive than 4 log virus when using chlorine2.5 log credit given for Giardia (clarification + filtration), leaving 0.5 log for CtNorthampton has decided to see 1.0 log for CtNorthampton has decided to see 1.0 log for Ct
Buffering system flowsFire FlowBackwash Storage
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Evaluation of Clearwell (cont.)Ct requirements Design conditions
Design is for maintenance of Ct even when one of the two concentric tanks is taken out of service“t” is normally evaluated for peak hourly flow
Outer cell is considered less
gQ = 6.5 MGD max plant flowC = 0.5 mg/LTemp = 0.5oCpH = 7.5
efficient based on length to width ratio
22:1 for outer cell38:1 for inner cell
1.0 log inactivationCt = 79 mg/L - mint10 ≥ 157 min
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CT for Giardia & Free Chlorine
Portions of H&H Table 7-4 are
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Table 7 4 are extracted from this table
Source: EPA, 1999, Guidance Manual for Disinfection Profiling & Benchmarking
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Also below
Storage profile
542 ft surface elevation, the washwaterpumps can no longer draw
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longer draw suction
Tracer Test ITracer Test Conditions
Depth = 26.5 ftVolume = 2,073,200 galQ = 3000 gpm = 4.32 MGDFluoride concentration
k d 0 034 /
tR = 11.52 hr
Background = 0.034 mg/LTarget = 1.33 mg/L
Temperature = 10.1 CpH = 8.14
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Outer Cell DataStep DosepDecember 13, 2007
Lag time = 6.6 min=0.00458 days
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Testing for Ct criteriaStep dose tracer testp
tR = 11.52 hr = 691.1 mint10 = 318 mint10/tR = 0.46
At 6.5 MGD
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min459319.05.6
0732.2=== d
MGDMGtR
min211)46.0(4591010 ==⎟⎟
⎠
⎞⎜⎜⎝
⎛=
tracerRR t
ttt
Greater than 157 min
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To next lecture
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