CEE 690K ENVIRONMENTAL REACTION KINETICS Lecture #16 Case Study: - - PDF document

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4/12/2008 Updated: 12 April 2008 CEE690K Lecture #16 1 Print version CEE 690K ENVIRONMENTAL REACTION KINETICS Lecture #16 Case Study: Nitrogenous Disinfection Byproducts Primary Literature as noted Introduction David A. Reckhow


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CEE690K Lecture #16 1

Updated: 12 April 2008

Print version

CEE 690K

ENVIRONMENTAL REACTION KINETICS Lecture #16

Introduction

David A. Reckhow

Case Study: Nitrogenous Disinfection Byproducts

Primary Literature as noted

PROTEINS AS IMPORTANT REACTIVE COMPOUNDS IN DRINKING WATER TREATMENT

Dave Reckhow

University of Massachusetts - Amherst

Junsung Kim, Guanghui Hua, Gladys MA WRRC Conference 8 April 2008 g g y Makdissy, John McClellan, Cynthia Castellon, Darlene Buttrick

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Outline

Formation of N-DBPs from NOM

N N

Occurrence Characteristics Chemistry of selected End Products DHAN DHAD NDMA Reactivity of Specific Nitrogenous Constituents Amino Acids Proteins & others Key N-DBPs and Methods to be developed

Reactions with Chlorine

Oxidized NOM and inorganic chloride The Precursors!

HOCl + natural organics (NOM)

  • Aldehydes

Chlorinated Organics

  • TOX
  • THMs
  • HAAs

Th THM Th THM

Cl Cl Cl C H Br Cl Cl C H Br Cl Br C H Br Br Br C H Chloroform Bromodichloromethane Chlorodibromomethane Bromoform

The THMs The THMs

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The Haloacetic Acids

Cl Cl Cl C COOH Br Cl Cl C COOH Br Cl Br C COOH Br Br Br C COOH Cl Cl Cl Br Trichloroacetic Bromodichloroacetic Chlorodibromoacetic Tribromoacetic Acid Acid Acid Acid

(TCAA)

Cl H C COOH Br C COOH Br H C COOH H Cl Cl Br Dichloroacetic Bromochloroacetic Dibromoacetic Acid Acid Acid

(DCAA)

N-DBPs we know about: end products

Certain to come from N-organics when using free Certain to come from N-organics when using free

chlorine

Major types: Cyanogen Halides Haloacetonitriles

H l h

Cl Cl H C C Br Cl C Br Br H C Dichloroacetonitrile Bromochloroacetonitrile Dibromoacetonitrile H N C N C N

CNCl & CNBr Halonitromethanes (DCAN) (BCAN) (DBAN)

Cl Cl Cl C C Trichloroacetonitrile

(TCAN)

N

Special focus on these compounds because of large data set

Cl Cl Cl C NO Chloropicrin

(CHP)

2

9 species

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Why N-DBPs?

Nitrogenous organics are generally quite reactive Can be enhanced by chloramination Some evidence that they are major contributors to

adverse human health effects of DBPs

Very little is known about N-DBPs Analytical chemistry is more complicated

y y p

yrrole ntrol

DBP Chemical Class

Work of Michael Plewa

8

CHO Cytotoxicity

DBNM BNM TBNM BDCNM BCNM DCNM CNM TCNM DBCNM Tribromop MX Bromate EMS +Con bromo-4-oxopentanoic Acid

  • -3-bromopropenoic Acid

bromopropenoic Acid mopropenoic Acid mobutenedioic Acid bromopropenoic Acid mo-3-methylbutenedioic Acid Bromoacetamide Dibromoacetamide Chloroacetamide Dichloroacetamide Other DBPs Haloacetamides

  • -3-bromopropenoic Acid

Trichloroacetamide Iodoacetamide Haloacetonitriles Dibromoacetonitrile Bromoacetonitrile Bromochloroacetonitrile Chloroacetonitrile romochloro-4-oxopentanoic Acid Iodoacetonitrile Dichloroacetonitrile Trichloroacetonitrile Halomethanes Iodoform Bromoform Chlorodibromomethane Chloroform

CHO Cell Cytotoxicity as %C½ Values (~LC50) Log Molar Concentration (72 h Exposure)

10-6 10-5 10-4 10-3 10-2

IAA BAA TBAA DBCAA DBAA BDCAA BCAA CAA TCAA DCAA D B T B B D C T D 3,3-Di 3-Iodo 3,3-Di Tribro 2-Brom 2,3-Di 2-Brom DIAA Haloacetic Acids Halo Acids Halonitromethanes July 2006 BIAA 2-Iodo 3,3-Br

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Lowest Observed Adverse Effect Level

Quantitative Structure-Toxicity Models

100 200 f halogenated DBPs 5 10 15 er of halonitriles

All Halo DBPs Halonitriles

AWWARF report by Bull et al., 2007

>1000 >100-1000 >10-100 >1-10 >0.1-1 >0.01-1 Distribution of estimated chronic LOAELs, mg/kg day-1 Number of 5 Numbe

DCAN

5 5 6.0 6.5

Chemistry of the end products

Surface Water

DCAN

hloroacetonitrile (μg/L)

2 0 2.5 3.0 3.5 4.0 4.5 5.0 5.5

Time (hrs)

20 40 60 80 100 120

Dich

0.0 0.5 1.0 1.5 2.0 10 mg/L 5 mg/L 2.5 mg/L Loss of Residual Chlorine Dose

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DHAN

K i di

C N C H Cl Cl C C H Cl Cl N OH H NH C C H Cl Cl N OCl H NCl

H2O

fast fast k2 k1 k4

DCAN OCl OH

Key intermediate Concentrations are

well known

C C Cl Cl OH C C H Cl Cl NH2 O C C H Cl Cl NHCl O H2O

Cl(+II) S (+IV)

C C Cl Cl O

pKa = 3.7

fast k1-2 k1-1

DCAD HOCl OH OH N-Cl-DCAD N-Cl-DCAD anion

C C H Cl Cl O OH NHCl2 NH3 C C H Cl Cl NHCl OCl OH C C H Cl Cl NH2 OH O fast fast

DCAA

Hydrolysis and oxidation

Proposed Rate Law for DCAN

Hydrolysis and oxidation k1 = 1.78 x10-7 ±0.35 x10-7 (s-1)

dC dt k k OH k Cl I C = − + + +

{ [ ] [ ( )]}

1 2 3

k2 = 3.42 ±0.31 (M-1s-1) k3 = 1.30 x 10-1 ±0.08 x 10-1 (M-1s-1)

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DCAN half-life based on pH & HOCl

  • At 20 C

100 1 Hour

  • From Reckhow,

Platt, MacNeill & McClellan, 2001

Aqua 50:1:1-13

  • Degradation in DS
  • bserved to

increase with increasing pH

ICR data:

rine Residual (mg/L)

1 10

OCl-

10 Minutes 1 Hour 8 Hours 1 Day 3 Days 1 Week

Obolensky & Frey, 2002

pH

6 7 8 9 10 11

Chlor

0.1

OH- H2O

3 Weeks

Halamides

Compounds Compounds Monohaloacetamides

Chloroacetamide, Bromoacetamide

Dihaloacetamides

Dichloroacetamide (DCAD) Bromochloracetamide (BCAD) Dibromoacetamide (DBAD)

T ih l

t id

Trihaloacetamides

trichloroacetamide & analogues

Chlorination byproducts Probably a bit less prevalent with chloramines Pre-oxidation will probably reduce subsequent formation

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Haloacetamides

M l f HAN

Measureable by GC

Mostly from HANs:

Acids Haloacetic ides Haloacetam itriles Haloaceton ⇒ ⇒

N-Halogenated Forms Free (f) Chlorine Sulfite Combined (c ) Total (t)

ual (mg/L)

10 100 DCAD Halflife 1 Hour 8 Hours 1 Day 10 Minutes

DCAD Stability

Chlorine Residu

0.1 1 3 Weeks 1 Day 3 Days 1 Week

HOCl

6 7 8 9 10 11

pH

6 7 8 9 10 11

OH-

3 Weeks 1 Hour 8 Hours 1 Day 3 Days 1 Week Reducing Conditions

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Nitrosamines

NDMA: typically formed at greater levels with

chloramination than with chlorination chloramination than with chlorination

Continues to form across DS?

  • ther nitrosamines (beyond NDMA) have been

reported in chloraminated water

Levels and mechanisms Earlier work: Valentine & Weinberg Earlier work: Valentine & Weinberg New mechanism: Mitch

Pathway to NDMA

Role of Dichloramine and oxygen Role of Dichloramine and oxygen

N

Cl Cl H

N

CH3 CH3 R

N N

H Cl CH3 CH3

R Cl Dichloramine Dimethyl(xx)amine Monochloro Unsymmetric Dimethylhydrazine (UDMH-Cl) O

O

O N

Cl Cl H

PRODUCTS Nitrosodimethylamine (NDMA) Oxygen N N

CH3 CH3 O

Based on recent work by Bill Mitch and colleagues

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19

The Unnatural Precursor?

Ranitidine (Zantac) 63% conversion to NDMA

Schmidt et al., 2006 [WQTC]

Introduced in 1981, largest selling prescription drug by 1988

Stomach ulcers and esophageal reflux

Mean concentration of 3000 ng/L estimated for raw municipal

WW (national average) WW (national average)

Sedlak 2005 AWWARF report

450 ng/L formation in raw WW expected Unknowns: how much does this persist in treatment and in the

environment?

Abbreviations DMD: dimethyldiazene

Reaction of UDMH Reaction of UDMH

TMT: tetramethyltetrazene FMMH: formaldehyde

monomethylhydrazone

FDMH: formaldehyde

dimethylhydrazone

DMC: dimethylcyanamide DMF: dimethylformamide

From: Mitch & Sedlak, 2002 [ES&T, 36:588]

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The DBP Iceberg

ICR Compounds ICR Compounds

THMs, THAAs DHAAs

ICR Compounds ICR Compounds

50 MWDSC DBPs 50 MWDSC DBPs ~700 Known DBPs ~700 Known DBPs

Stuart Krasner Susan Richardson

Halogenated Compounds Non Non-

  • halogenated

halogenated Compounds Compounds

Organic Nitrogen Abundance

Ratio to carbon

mg-C/mg-N)

30 40 50 60

27

Ratio to carbon Redrawn from Westerhoff & Mash, 2002

Percentile

10 20 30 40 50 60 70 80 90 100

DOC/DON (m

10 20 30

27 15 8.2

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Ranges of Org-N by types

Estimates from literature surveys

Classification 50%ile 90%ile 99%ile DON 350 800 2000 Free AA 20 50 200 Combined AA 40 100 400 Order of magnitude estimates for organic nitrogen in surface waters (all values in µg-N/L) Combined AA 40 100 400 Nucleic acids 20 50 200 Amino Sugars 40 100 400 Humic-N 25 200 1000 Others

Amino Acids and Proteins

Simple Amino Acids

f M d AN

H2C C H COOH NH2

NH 2

some form THMs and HANs Highest reactivity for activated

AAs

Tyrosine & Tryptophan: activated

aromatic

Cysteine: sulfhydryl group Proteins

Alanine Alanine

HO C H2 C H COOH

Tyrosine Tyrosine

many linked AAs; relatively

unreactive polypeptide bonds

Reactions with proteins occurs

most readily on AA side chains

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Chlorine Demand

rine Demand (mg/mg-C)

4 6 8 10 12

Aquatic NOM Fractions

Selected Amino Acids

More reactive than

most NOM

Precursor

W h

  • l

e W a t e r s F u l v i c A c i d H u m i c A c i d W e a k H y d r

  • p

h

  • b

i c A c i d s H y d r

  • p

h

  • b

i c N e u t r a l H y d r

  • p

h

  • b

i c B a s e s H y d r

  • p

h i l i c A c i d s H y d r

  • p

h i l i c N e u t r a l s H y d r

  • p

h i l i c B a s e s M e t h i

  • n

i n e A s p a r t i c a c i d L y s i n e A r g i n i n e H i s t i d i n e A s p a r a g i n e G l u t a m i n e T r y p t

  • p

h a n P h e n y l a l a n i n e T y r

  • s

i n e C y s t e i n e C y s t i n e

Chlor

2

THM formation

ethane Formation (μg/mg-C)

35 40 45 50 55 60 65 70 80 100 120 140

Aquatic NOM Fractions

Selected Amino Acids

113 147

Minor except

for two

Tryptophan Tyrosine

Precursor

W h

  • l

e W a t e r s F u l v i c A c i d H u m i c A c i d W e a k H y d r

  • p

h

  • b

i c A c i d s H y d r

  • p

h

  • b

i c N e u t r a l H y d r

  • p

h

  • b

i c B a s e s H y d r

  • p

h i l i c A c i d s H y d r

  • p

h i l i c N e u t r a l s H y d r

  • p

h i l i c B a s e s M e t h i

  • n

i n e A s p a r t i c a c i d L y s i n e A r g i n i n e H i s t i d i n e A s p a r a g i n e G l u t a m i n e T r y p t

  • p

h a n P h e n y l a l a n i n e T y r

  • s

i n e C y s t e i n e C y s t i n e

Trihalome

5 10 15 20 25 30

y

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SLIDE 14

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Trihaloacetic Acid

Like THMs Tryptophan Tyrosine

etic Acid Formation (μg/mg-C)

30 35 40 45 50 55 60 80 100 120 140

Aquatic NOM Fractions

Selected Amino Acids

107 137 105

Precursor

W h

  • l

e W a t e r s F u l v i c A c i d H u m i c A c i d W e a k H y d r

  • p

h

  • b

i c A c i d s H y d r

  • p

h

  • b

i c N e u t r a l H y d r

  • p

h

  • b

i c B a s e s H y d r

  • p

h i l i c A c i d s H y d r

  • p

h i l i c N e u t r a l s H y d r

  • p

h i l i c B a s e s M e t h i

  • n

i n e A s p a r t i c a c i d L y s i n e A r g i n i n e H i s t i d i n e A s p a r a g i n e G l u t a m i n e T r y p t

  • p

h a n P h e n y l a l a n i n e T y r

  • s

i n e C y s t e i n e C y s t i n e

Trihaloace

5 10 15 20 25

Dihaloacetic Acid

Aspartic acid

etic Acid Formation (μg/mg-C)

25 30 35 40 45 50 55 60 100 150 200 250 300 350 400

Aquatic NOM Fractions

Selected Amino Acids

387 89 115

Aspartic acid Histidine

Precursor

W h

  • l

e W a t e r s F u l v i c A c i d H u m i c A c i d W e a k H y d r

  • p

h

  • b

i c A c i d s H y d r

  • p

h

  • b

i c N e u t r a l H y d r

  • p

h

  • b

i c B a s e s H y d r

  • p

h i l i c A c i d s H y d r

  • p

h i l i c N e u t r a l s H y d r

  • p

h i l i c B a s e s M e t h i

  • n

i n e A s p a r t i c a c i d L y s i n e A r g i n i n e H i s t i d i n e A s p a r a g i n e G l u t a m i n e T r y p t

  • p

h a n P h e n y l a l a n i n e T y r

  • s

i n e C y s t e i n e C y s t i n e

Dihaloace

5 10 15 20 25

Asparagine

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Dihaloacetonitriles

Aspartic acid

etonitrile Formation (μg/mg-C)

7 8 9 10 11 12 13 14 15 50 100 150 200 250

Aquatic NOM Fractions

Selected Amino Acids

255 85

Histidine

Precursor

W h

  • l

e W a t e r s F u l v i c A c i d H u m i c A c i d W e a k H y d r

  • p

h

  • b

i c A c i d s H y d r

  • p

h

  • b

i c N e u t r a l H y d r

  • p

h

  • b

i c B a s e s H y d r

  • p

h i l i c A c i d s H y d r

  • p

h i l i c N e u t r a l s H y d r

  • p

h i l i c B a s e s M e t h i

  • n

i n e A s p a r t i c a c i d L y s i n e A r g i n i n e H i s t i d i n e A s p a r a g i n e G l u t a m i n e T r y p t

  • p

h a n P h e n y l a l a n i n e T y r

  • s

i n e C y s t e i n e C y s t i n e

Dihaloace

1 2 3 4 5 6

30

Amino Acids

From: Perdue & Ritchie, 2004

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4/12/2008 16

Amino AA conc

Cl2 Cons.

DBP Formation (µg/mg-C) Acid

(µM/mg-C)

(mg/mg-C)

TOX THM TCAA DCAA HANs Unkn TOX Glycine 0.030 0.0072 0.002 0.000 0.000 0.000 0.000 0.001 Alanine 0.030 0.0046 0.007 0.000 0.000 0.002 0.000 0.006 Valine 0.013 0.0022 0.009 0.002 0.001 0.002 0.000 0.005 Isoleucine 0.011 0.0018 0.004 0.000 0.000 0.002 0.000 0.001 Leucine 0.015 0.0022 0.000 0.000 0.000 0.002 0.000

  • 0.001

Serine 0.028 0.0083 0.001 0.000 0.000 0.000 0.000 0.001 Threonine 0.018 0.0068 0.012 0.000 0.000 0.000 0.000 0.011 Methionine 0.003 0.0010 0.004 0.001 0.000 0.001 0.000 0.003 Aspartic acid 0.026 0.0083 0.849 0.002 0.002 0.491 0.323 0.367 Glutamic acid 0.026 0.0036 0.004 0.000 0.002 0.002 0.000 0.001 Lysine 0.004 0.0013 0.001 0.000 0.000 0.001 0.000 0.000 Ornithine 0.005 0.0017 0.011 0.002 0.000 0.000 0.000 0.009 Arginine 0.019 0.0104 0.032 0.000 0.000 0.003 0.001 0.030 Histidine 0.007 0.0040 0.153 0.002 0.021 0.042 0.040 0.084 Asparagine 0.001 0.0004 0.012 0.000 0.000 0.005 0.000 0.009 Glutamine 0.001 0.0004 0.000 0.000 0.000 0.000 0.000 0.000 Tryptophan 0.006 0.0068 0.432 0.124 0.115 0.050 0.013 0.193 Phenylalanine 0.009 0.0017 0.000 0.000 0.000 0.003 0.001

  • 0.002

Tyrosine 0.006 0.0053 0.257 0.069 0.065 0.021 0.006 0.138 Total FAA 0.259 0.0780 1.789 0.201 0.207 0.626 0.385 0.856 Upper Limit 3.454 1.0403 23.855 2.677 2.765 8.340 5.131 11.418 Whole Waters 1.89 185 48.2 60 33.1 1.8 129.7 Total FAA 4.1% 1.0% 0.4% 0.3% 1.9% 21.4% 0.7% Upper Limit 55.0% 12.9% 5.6% 4.6% 25.2% 285.0% 8.8% N

C R1 H R4 R3 R2

N

C R1 X R4 R3 R2

N

C X X R4 R3 R2 R1=H X+ Nu X+ Nu

Degradation pathways

R2=H or COOH R4=H HX (CO2) R2=H or COOH

C

N R3 X R4

I II III IV C

N R3 R1 R4 NH2X R1=H X+ Nu HX (CO2) General scheme for carbonyl

and cyano formation from chlorination of amines and amino acids

C

O R4 R3

R1NH2 C

N R3

V VI

NH2X HX

Monohalamine Pathway Dihalamine Pathway

amino acids

  • (adapted from Nweke and

Scully, 1989, and Armesto et al., 1998).

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N-chloro-organics

Reactions of chlorine with organic amines

P i i

Primary amines Secondary amines Inorganic chloramines can transfer their active 2 2

NCl R NHCl R NH R

HOCl HOCl

− ⎯ ⎯ → ⎯ − ⎯ ⎯ → ⎯ − NCl R NH R

HOCl

− ⎯ ⎯ → ⎯ −

2 2

chlorine in a similar fashion

LFERs

HOCl (M-1s-1)

6 7 8 9 Amino Acids 1o Amines 2o Amines 3o Amines Polypeptides Relationship between

basicity and 2nd order rate constants for reaction of HOCl with N-compounds

  • Data Sources: Friend, 1956; Hussain et

al., 1972; Isaac et al., 1983; Armesto et al., 1993; Armesto et al., 1994; Antelo et al., 1995; Abia et al., 1998 pKa

7 8 9 10 11 12

Log kH

2 3 4 5

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Degradation of Organic Chloramines

1

Parent Amine kobs (s-1) t½ (min)

Alanine 1.3E-04 86 Glycine 1.4E-06 8400 Histidine 2.7E-04 43 Leucine 1.6E-04 72 Phenylalanine 2.2E-04 52 Serine 2.4E-04 49 Creatinine 3.5E-06 3300 Glycine N acetyl 6.0E-07 19000 Glycine ethyl ester 2.3E-04 50 Glycylglycine 1.0E-05 1100 Sarcosine 5.3E-05 210

Analysis of Organic N-chloramines

Approach

S ll i d LC

Seems well suited to LC Prior efforts with GC were not very successful e.g., tosyl derivatization Proposal Fast analysis with UPLC Parallel detection and analysis by Post-column reaction with I and absorbance LC/MS/MS

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4/12/2008 19

Research needs

Conclusions: from QSTR

Research needs

Group Example Occurrence Toxicology Haloquinones 2,6-dichloro-3-methyl-1,2- benzoquinone (DMBQ) 1 2 Organic N- haloamines Prioritize on range of stabilities and mutagenic activity 2 1 Alkaloidal nitrosamines N-nitrosonornicotine 1-N-

  • xide

1 2 Cyclopentenoic acids & MX-related 3,5-dichloro—1-hydroxy-4- ketocyclopent-2-enoic acid CMCF 1 2 2 1 Halonitriles 2,3-Dichloropropenal (Carc) 2,3-dibromopropionitrile (DT) 1 1

Summary

There is a broad range of nitrogenous organic compounds in natural waters There is a broad range of nitrogenous organic compounds in natural waters

that are reactive with chlorine and produce both regulated and non- regulated DBPs

Amino acids are generally reactive High Chlorine demand Very high DHAN formation Moderate to high DiHAAs; low to moderate THMs & TriHAAs Proteins

  • Rapid degradation at reactive sites
  • Rapid degradation at reactive sites
  • Then slow degradation, leading to similar DBP profiles

Toxic compounds that may be regulated could include

  • Organic chloramines
  • Halonitriles
  • Alkaloidal nitrosamines
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39

To next lecture

David A. Reckhow

CEE690K Lecture #16