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CEE/EHS 597B Class #15: Special Treatment Issues: DBPs Dave - PDF document

CEE 597B DBPs CEE/EHS 597B Class #15: Special Treatment Issues: DBPs Dave Reckhow 2 1 CEE 597B DBPs 2007 John #1: Dr. John Snow 1813-1858 Cholera First emerged in early 1800s 1852-1860: The third cholera pandemic Snow


  1. CEE 597B DBPs CEE/EHS 597B Class #15: Special Treatment Issues: DBPs Dave Reckhow 2 1

  2. CEE 597B DBPs 2007 John #1: Dr. John Snow 1813-1858  Cholera  First emerged in early 1800s  1852-1860: The third cholera pandemic  Snow showed the role of water in disease transmission  London’s Broad Street pump (Broadwick St)  Miasma theory was discredited, but it took decades to fully put it to rest 3 Soho, Westminster 4 Picadilly Circus 2

  3. CEE 597B DBPs Photo courtesy of the Leal family and Mike McGuire John #2: Dr. John L. Leal  Jersey City’s Boonton Reservoir  Leal experimented with chlorine, its effectiveness and production 1858-1914  George Johnson & George Fuller worked with Leal and designed the system (1908) “Full-scale and continuous implementation of disinfection for the first time in Jersey City, NJ ignited a disinfection revolution in the United States that reverberated around the world” M.J. McGuire, JAWWA 98(3)123 5 Chlorination  1-2 punch of filtration & chlorination Greenberg, 1980, Water Chlorination, Env. Impact & Health Eff., Vol 3, pg.3, Ann Arbor Sci. US Death Rates for Typhoid Fever 6 Melosi, 2000, The Sanitary City, John Hopkins Press 3

  4. CEE 597B DBPs Conventional Treatment: 1910-present  Coagulation & solids separation  rapid mix, flocculation, settling, filtration  Disinfection  including clearwell for contact time  Most common for surface water Corrosion Control Fluoride Coagulant Chlorine Dist. Sys. Clear well raw water rapid flocculation Settling Filtration 7 mix John #3: Johannes J. Rook  Short Biography  Education  PhD in Biochemistry: 1949  Work experience  Technological Univ., Delft (~‘49-’54) 1921-2010  Laboratory for Microbiology  Early Research  Lundbeck Pharmaceuticals in Copenhagen, (~’55-?)  1955, Microbiological Deterioration of  Noury Citric acid Factory (in Holland) Vulcanized Rubber  Amstel Brewery  Applied Micro.  Rotterdam Water Works by 1963, chief chemist  1964, secured funds for a GC at (1964-1984). Rotterdam  1984-1986; Visiting Researcher at Lyonnaise des  Carlo Erba with gas sample loop Eaux, Le Pecq. 8 4

  5. CEE 597B DBPs John Rook & DBPs  Major Contributions  Brought headspace analysis from the beer industry to drinking water  T&O problems  Found trihalomethanes (THMs) in finished water  Carcinogens !?!  Published in Dutch journal H2O, Aug 19, 1972 issue  Deduced that they were formed as byproducts of chlorination  Proposed chemical pathways 9 Rook, 1974, Water Treat. & Exam., 23:234 DBP Epidemiology  Bladder Cancer Basis for current  DBPs linked to 9,300 US cases every year EPA regulation  Other Cancers 80 µg/L THMs 60 µg/L HAAs  Rectal, colon  Reproductive & developmental effects  Miscarriages & Low birth weight 20 µg/L THMs - high risk  Birth Defects Hwang et al., 2008  e.g., Cleft palate, neural tube defects  Other  Kidney & spleen disorders  Immune system problems, neurotoxic effects 5

  6. CEE 597B DBPs 11 Reactants Products Reduced Oxidized Inorganics Inorganics & inorganic Cl - HOCl DBPs OH - O 3 NH 4 + NH 2 Cl ClO 2 - ClO 2 & Organic DBPs Oxidized NOM NOM 6

  7. CEE 597B DBPs Formation of Cl 2 -driven DBPs Cl 2 The Halogenated DBPs NaOCl • THMs • HAAs and other haloacids Br-, I- • Haloaromatics • N-halo compounds • Halo-nitriles, aldehydes, nitros, etc OBr-, I 3 - NH 3 ~10% The non- NH 2 Cl halogenated DBPs CO 2 + Oxidized Natural Organic Organic ~90% Mater Compounds • Acids Anthropogenic • Aldehydes Chemicals • Ketones (PPCPs, Ag & 13 • Nitrosamines industrial products) Reactions with Disinfectants: Chlorine Oxidized NOM The Precursors! and inorganic chloride HOCl •Aldehydes + natural organics Chlorinated Organics (NOM) •TOX •THMs •HAAs The THMs Br Br Br Cl C H Cl H Br C H C H Br C Cl Cl Br Cl Cl Chloroform Bromodichloromethane Chlorodibromomethane Bromoform 14 7

  8. CEE 597B DBPs The Haloacetic Acids  HAA5 & HAA6 include the two monohaloacetic acids (MCAA & MBAA) plus  One of the trihaloacetic acids: Br Br Cl Br COOH Cl C C COOH COOH C COOH Br Cl C Br Cl Cl Br Cl Trichloroacetic Bromodichloroacetic Chlorodibromoacetic Tribromoacetic Acid Acid Acid Acid (TCAA) HAA6 only Br Cl Br  And 2 or 3 of the COOH H C H C COOH H C COOH dihaloacetic acids Cl Br Cl Dichloroacetic Bromochloroacetic Dibromoacetic Acid Acid Acid 15 15 (DCAA) Haloacetonitriles  Others that are commonly measured, but not regulated include the: Br Br Cl  Dihalo- H C C N H C C N H C C N acetonitriles Cl Br Cl Dichloroacetonitrile Bromochloroacetonitrile Dibromoacetonitrile (DCAN) (BCAN) (DBAN) Cl  Trihaloacetonitriles N Cl C C Cl Trichloroacetonitrile 16 16 (TCAN) 8

  9. CEE 597B DBPs Halopropanones  As well as the: O H Cl etc  dihalopropanones C C C H H H Cl 1,1-Dichloropropanone (DCP)  trihalopropanones O O Br H Cl H etc. C C H Cl C C C H Cl C Cl H Cl H 1,1,1-Trichloropropanone 1,1,1-Bromodichloropropanone (TCP) 17 17 Factors Affecting DBP Formation  Time  pH  Dose  Temperature  Bromide/Ammonia  Pretreatment  Reactions with pipe walls & attached materials “I think you should be more explicit here 18 in step two” 9

  10. CEE 597B DBPs 1300 600 20 mg/L chlorine dose pH 7.0 1200 Time 20 o C 1100 500 TOX 1000  Major 900 THM, HAA Concentration (  g/L) Byproducts 400 TOX Concentration (  g/L) 800 700 300 600 TCAA 500 TTHM 200 400 300 Aquatic 100 200 DCAA NOM 100 0 0 0 20 40 60 80 100 120 140 160 300 350 19 (after Reckhow & Singer, 1984) Time (hrs) 1400 1200 pH Effects 1000 TOX Concentration (  g/L) 800 600 400 TCAA + DCAA TTHM 200 0 0 2 4 6 8 10 12 20 pH 10

  11. CEE 597B DBPs Significance of Bromide  Present in surface and groundwaters  Concentrations are highly variable  Not removed by most treatment processes  Readily oxidized by chlorine        k HOCl Br HOBr Cl     2 1 1 4 7 10 . [exp(  )] 754 9 . k x M s T     3 1 1 37 10 . @ 25 x M s C Therefore, bromide has a 13 second half life at pH 7, and 1 mg/L residual chlorine 21 Impact of Bromide on THM Formation 100 Data from: Minear & Bird, 1980 96 hours, pH 7.0 5 mg/L Chlorine Dose 80 CHCl 3 1 mg/L Humic Acid Percent of TTHM CHBr 3 60 CHBr 2 Cl 40 CHBrCl 2 20 0 0.0 0.4 0.8 1.2 1.6 2.0 22 Bromide Concentration (mg/L) 11

  12. CEE 597B DBPs Bromide: THAA Formation Note that TCAA is the only regulated THAA 330 pH 7, 25 o C, 7 days 300 CCl 3 COOH 25 mg/L chlorine dose 270 2.9 mg/L TOC Concentration (  g/L as Cl - ) 240 CClBr 2 COOH 210 180 CCl 2 BrCOOH CBr 3 COOH 150 120 90 60 30 0 0 1 2 3 4 5 Bromide Concentration (mg/L) From Pourmoghaddas, 1990 23 Case Study: Impact of time & chlorine dose 6 Cl 2 Demand 5 Chlorine Demand (mg/L) 4 3 2 Chlorine Dose 1 2.5 mg/L Loss of Residual 5 mg/L 10 mg/L 0 0 20 40 60 80 100 120 24 Time (hrs) 12

  13. CEE 597B DBPs Case Study: Impact of time & chlorine dose 220 200 THM 180 Total Trihalomethanes (  g/L) 160 140 120 100 80 60 Chlorine Dose 40 2.5 mg/L Loss of Residual 20 5 mg/L 10 mg/L 0 0 20 40 60 80 100 120 25 Time (hrs) THMs from Chlorination  Chlorine Residual @ 48 hrs  std = 0.8 mg/L 60 55  opt = 0.2 mg/L 50  Temp 45 THM Formation (  g/L)  Low = 13 C 40  High = 23 C 35 30 25 20 1-Chlorine: std dose: low temp 15 2-Chlorine: std dose: high temp 3-Chlorine: opt dose: low temp 10 4-Chlorine: opt dose: high temp 5 0 26 0 20 40 60 80 100 Reaction Time (hours) 13

  14. CEE 597B DBPs THMs from Chloramination  Addition of ammonia after 5 hrs free contact time 45 End of Initial Free Chlorine Contact Period 40 35 THM Formation (  g/L) 30 25 20 5-Chloramine: mid dose: 4.0 Cl 2 /N: low temp 15 6-Chloramine: mid dose: 4.9 Cl 2 /N: low temp 7-Chloramine: mid dose: 6.0 Cl 2 /N: low temp 10 8-Chloramine; low dose: 4.9 Cl 2 /N: low temp 9-Chloramine: high dose: 4.9 Cl 2 /N: low temp 5 10-Chloramine: mid dose: 4.9 Cl 2 /N: high temp 0 0 20 40 60 80 100 27 Reaction Time (hours) DBP Modeling  Power function models (Empirical)  simple to use  greater experience  Chemical kinetic models (Semi-mechanistic)  depends on time-varying concentrations of the precursors (reactants)  better adapted for use with a more integrated framework  combine with degradation terms  combine with hydraulic/reactor models  Chlorine boosting 28 14

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