CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14...

23
CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 1 CEE 371 Water and Wastewater Updated: 21 November 2009 Print version Water and Wastewater Systems Lecture #14 David Reckhow CEE 371 L#14 1 Drinking Water Treatment : Chlorination Reading : Chapter 7, pp.233-238, 259-262 Forms of Chlorine applied to water Chlorine gas Cl 2 Sodium Hypochlorite liquid (Hypo) NaOCl Calcium Hypochlorite solid Traditional method Becoming more common Ca(OCl) 2 Other forms Organic-N based compounds and resins David Reckhow CEE 371 L#14 2

Transcript of CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14...

Page 1: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 1

CEE 371Water and Wastewater

Updated: 21 November 2009

Print version

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

David Reckhow CEE 371 L#14 2

Page 2: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 2

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

David Reckhow CEE 371 L#20 3

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%

David Reckhow CEE 371 L#13 4

Page 3: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 3

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

David Reckhow CEE 371 L#14 5

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

Where all concentrations are in mg/LDavid Reckhow CEE 371 L#14 6

Page 4: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 4

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

David Reckhow CEE 371 L#14 7

+−−− ++→+ 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

David Reckhow CEE 371 L#14 8

)(6.7)(8.8)(63.0)(3.1 4+++=− NHHSFeMnDemandInorganic

Page 5: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 5

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

David Reckhow CEE 371 L#14 9

Cl2 gas: larger installations1 ton cylindersy

With small (150 lb) vertical tanks in background

Requires separate sealed room orsealed room or bldg.

David Reckhow CEE 371 L#14 10

Avon, CO

Page 6: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 6

Commercial Chlorinatorfeed

David Reckhow CEE 371 L#14 11

Fig 7-18; pg. 236 in H&H

Large chlorinatorchlorinator

Vacuum created at aspirator injectorinjector

David Reckhow CEE 371 L#14 12

Figure courtesy of Wallace & Tiernan Co.

Page 7: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 7

Dose controlFlow pacingp g

Small home system

F ll l

David Reckhow CEE 371 L#14 13

Fig 7-19; pg. 237 in H&H

Full-scale municipal system

Dose controlFeed back system

Adjusts for varying chlorine demand

David Reckhow CEE 371 L#14 14

Fig 7-19; pg. 237 in H&H

Page 8: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 8

Hypochlorite Dosingdafd

David Reckhow CEE 371 L#14 15

Chlorine tanksLeft side is currently feedingRight side is on reserve

Page 9: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 9

Chlorine feeding systemg y

Page 10: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 10

Dose adjustment knob

Page 11: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 11

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)

David Reckhow CEE 371 L#20 21

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

David Reckhow CEE 371 L#14 22

Page 12: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 12

Chloramines: Breakpoint CurveMCA = monochloramineDCA = dichloramine

The Breakpoint

Combined Free

DCA = dichloramineFRC = free residual chlorineNmg

Clmg−− 26.7

NmgClmg−− 24

David Reckhow CEE 371 L#20 23

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

David Reckhow CEE 371 L#9 24

in service

NaOCl added just prior to entry

Page 13: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 13

Raw Water

Reservoirs &Reservoirs &Transmission Mains

Clearwell

9 Sept 06

Page 14: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 14

Clearwell

9 Sept 06

Clearwell

9 Sept 06

Page 15: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 15

Clearwell

9 Sept 06

Clearwell

29 Sept 06

Page 16: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 16

ClearwellFrom the plant site

29 Sept 06

ClearwellDropping a panel pp g pinto position

29 Sept 06

Page 17: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 17

Clearwell

29 Sept 06

Northampton Ground Storage

Finished water storage at plantFinished water storage at plantKnow as a “Clearwell”

View from Outer ringUnder construction

David Reckhow CEE 371 L#9 3429 Sept 06

Page 18: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 18

ClearwellExit portalp

29 Sept 06

ClearwellIn outer ring, looking SW?g, g

29 Sept 06

Page 19: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 19

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

David Reckhow CEE 371 L#14 37

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

David Reckhow CEE 371 L#14 38

Page 20: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 20

CT for Giardia & Free Chlorine

Portions of H&H Table 7-4 are

David Reckhow CEE 371 L#14 39

Table 7 4 are extracted from this table

Source: EPA, 1999, Guidance Manual for Disinfection Profiling & Benchmarking

asdfasdf

David Reckhow CEE 371 L#14 40

Page 21: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 21

Also below

Storage profile

542 ft surface elevation, the washwaterpumps can no longer draw

David Reckhow CEE 371 L#14 41

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

David Reckhow CEE 371 L#14 42

Page 22: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 22

Outer Cell DataStep DosepDecember 13, 2007

Lag time = 6.6 min=0.00458 days

David Reckhow CEE 371 L#14 43

Testing for Ct criteriaStep dose tracer testp

tR = 11.52 hr = 691.1 mint10 = 318 mint10/tR = 0.46

At 6.5 MGD

David Reckhow CEE 371 L#14 44

min459319.05.6

0732.2=== d

MGDMGtR

min211)46.0(4591010 ==⎟⎟

⎞⎜⎜⎝

⎛=

tracerRR t

ttt

Greater than 157 min

Page 23: CEE 371 Water and Wastewater Systems · asdfasdf David Reckhow CEE 371 L#14 40. CEE 371 Lecture #14 11/21/2009 Lecture #14 Dave Reckhow 21 Also below Storage profile 542 ft surface

CEE 371 Lecture #14 11/21/2009

Lecture #14 Dave Reckhow 23

To next lecture

David Reckhow CEE 371 L#14 45