cee 697k - college of engineering | umass amherst 6 11 formation of brominated thms acc h cl cl cl c...
TRANSCRIPT
9/4/2013
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CEE 697KENVIRONMENTAL REACTION KINETICS
IntroductionDavid A. Reckhow
CEE 697K Lecture #2 1Updated: 4 September 2013
Print version
Lecture #2
Rate Expressions: Bromide + Chlorine case study & lab projectKumar & Margerum paper
Reactions with Chlorine
HOCl + natural organics
(NOM)
Oxidized NOMand inorganic chloride
•Aldehydes
Chlorinated Organics•TOX•THMs•HAAs
Cl
Cl
Cl C H
Br
Cl
Cl C HBr
Cl
Br C H
Br
Br
Br C H
Chloroform Bromodichloromethane Chlorodibromomethane Bromoform
The THMs
The Precursors!
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The Haloacetic Acids
Cl
Cl
Cl C COOH
Br
Cl
Cl C COOHBr
Cl
Br C COOH
Br
Br
Br C COOH
Trichloroacetic Bromodichloroacetic Chlorodibromoacetic TribromoaceticAcid Acid Acid Acid
(TCAA)
Cl
Cl
H C COOH
Br
Cl
C COOHBr
Br
H C COOH
Dichloroacetic Bromochloroacetic DibromoaceticAcid Acid Acid
(DCAA)
H
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Distribution: Variability within a single system
Example: New Haven Service Area DS model
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chlorine
New HavenDistribution System
Lake SaltonstallWTP
West RiverWTP
LakeGaillard
WTP
Millrock Basins
Maltby Tank
3,400 pipes2,500 junctions
3 MG
8.7 MG
2.0 mg/L DOC (Treated)pH 71.8 mg/L chlorine doseCEE 697K Lecture #2
David A. Reckhow
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22:00
TTHM
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HAA6
CEE 697K Lecture #2
Single Cell Gel Electrophoresis Genotoxicity PotencyLog Molar Concentration (4 h Exposure)
10-6 10-5 10-4 10-3 10-2
IAA
BA
A
CA
A
DIA
A
TB
AA
DB
AA3,
3-D
ibro
mo-
4-ox
ope
nta
noic
Aci
d
2-B
rom
obut
ene
dio
ic A
cid
2-Io
do-
3-br
omop
rop
enoi
c A
cid
2,3-
Dib
rom
opr
ope
noic
Aci
d
DB
NM
BD
CN
MT
BN
M
TC
NM
BN
M
BC
NM
DB
CN
M
DC
NM
CN
M
Bro
mo
ace
tam
ide
Dib
rom
oace
tam
ide
Tri
brom
opyr
role
MX
Bro
ma
te
EM
S +
Co
ntr
ol
Haloacetic Acids
Halo Acids
Haloacetamides
Halonitromethanes
Other DBPs
DBP Chemical Class
Not Genotoxic: DCAA, TCAA, BDCAA, Dichloroacetamide, 3,3-Dibromopropenoic Acid, 3-Iodo-3-bromopropenoic Acid, 2,3,3,Tribromopropenoic Acid July 2006
Ch
loro
ace
tam
ide
Trih
loro
ace
tam
ide
Iodo
ace
tam
ide
Haloacetonitriles Bro
mo
acet
onitr
ile
Dib
rom
oac
eto
nitr
ile
Bro
mo
chlo
roa
ceto
nitr
ile
Ch
loro
ace
ton
itrile
3,3
-Bro
moc
hlor
o-4-
oxo
pent
ano
ic A
cid
Iod
oace
toni
trile
Tric
hlor
oace
toni
trile
Dic
hlor
oace
ton
itrile
BIA
A
CD
BA
A
BC
AA
Work of Michael Plewa Univ. of Illinois
8
Genotoxicity
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9
Bromide: THM Formation
Bromide Concentration (mg/L)
0.0 0.4 0.8 1.2 1.6 2.0
Per
cent
of
TT
HM
0
20
40
60
80
100
CHCl3
CHBrCl2
CHBr2Cl
CHBr3
Data from: Minear & Bird, 198096 hours, pH 7.0
5 mg/L Chlorine Dose1 mg/L Humic Acid
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Impact of Bromide on DHAA Formation
Bromide Concentration (mg/L)
0 1 2 3 4 5
Con
cent
ratio
n ( g
/L a
s C
l- )
0
20
40
60
80
100
CHCl2COOH
CHClBrCOOHCHBr2COOH
pH 7, 25oC, 7 days25 mg/L chlorine dose
2.9 mg/L TOC
From Pourmoghaddas, 1990David A. ReckhowCEE 697K Lecture #2
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Formation of Brominated THMs
A C C
H
ClCl
Cl
C
H
BrCl
Cl
C
H
BrBr
Cl
C
H
BrBr
Br
B
D E
F
HOCl HOCl HOCl
HOCl HOCl
HOCl
HOCl Br HOBr Clk David A. ReckhowCEE 697K Lecture #2
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THM Br/(Cl+Br)
0.0 0.2 0.4 0.6 0.8 1.0
TH
M M
ole
Fra
ctio
n (T
HM
4 o
nly
)
0.0
0.2
0.4
0.6
0.8
1.0
1.2
CHCl3CHBrCl2CHBr2ClCHBr3CHCl3 Lab testsCHBrCl2 Lab testsCHBr2Cl Lab testsCHBr3 Lab tests
Full-scale data (small symbols)
from Weinberg et al., 2002 (All 12 plants)
Lab data (large symbols)
from Hua & Reckhow, 2004
Lines are geometric model
Bromo speciation
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Case study: chlorine + bromide
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Observed reaction Nucleophilic attack of bromide on oxygen in
hypochlorous acid k2 = 2.95 x103 M-1s-1 at 25ºC
Note that HOCl deprotonates at elevated pHs
From Farkas et al., 1949
Transfer of Cl+ to form intermediate (BrCl)
From Kumar & Margerum, 1987
ClHOBrBrHOCl k2
BrClOHABrHOClHA k 2
3
ClBrBrBrCl fast2
32 BrBrBr fast
Background
Absorbance for monitoring reaction
Known equilibria
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Alkaline Experiments
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Pseudo-1st order Bromide in great excess
Slow reactions Could be monitored directly by
conventional UV spectrophotometer 292 nm peak for hypochlorite
(OCl-) Followed for 4 half-lives Complete from: 1.1 sec – 4 hr
Plot ln(At-A∞) vs time Slope is kobs
Kobs is a linear function of Bromide
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pH dependency
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Overall pH dependence
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How to explain pH effect on 2nd order rate constant? See also, Brezonik, pg 230; figure 4-20
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Buffer Tests
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Low pH
High pH
Buffer Effect
Proposed dependence on HA
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CEE 697K Lecture #2
][][][0 BrHAkHkkk HAHobs
][
][
1
1][
][
0
HK
CHCCHA
a
TT
HKT
a
][
][
][
][ 0
HK
bufferkk
H
kBr
k
a
THAH
obs
12210)15.025.1( sMxkHA
123.19.8 sMkHA
HPO4-2
HCO3-
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High pH only
More generally
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CEE 697K Lecture #2
][][][0 BrHAkHkkk HAHobs
][]][[][][)]([
0
BrOClHAkHOClkOClk
dt
ICldHAHOCl
]][[][][][
0
BrOClHAkHkkdt
OCldHAH
Acidic Experiments
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Pseudo-1st order Bromide in great excess
Fast reactions Required high-speed setup Stopped-flow spectrophotometer
Could monitor 2º product 266 nm peak for tribromide (Br3
-)
Followed for 4 half-lives Complete from 0.40-0.01 sec
Plot ln(At-A∞) vs time Slope is kobs
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Stopped-flow
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Principle
Commercial instruments
Limitations Correct for slow mixing speed (km) For Durrum instrument: km = 1700 s-1
m
obsk
kobs
obs
kk
1
Kobs is still linear with Br-
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No difference in mechanism?
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Acidic data: impact of acids
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General and specific acid
Overall pH dependence
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Three effective zones See also, Brezonik, pg 230; figure 4-20
HOCl
OCl-
H+ + HOCl
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Catalysis: comparison with pKa
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Bronsted catalysis
Indicates that HA engages in greater donation of proton to OCl- than to HOCl
H3O+
HCO3-
HPO4-2
CH3COOH
CH2ClCOOH
H2O
aAHA KGk
27.075.0
Mechanisms
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Proposed mechanism
Alternative Less likely
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Temperature: Arrhenius Equation
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Arrhenius Equation
Where R is the universal gas constant
Transforms to:
/aE RTk Ae8.3145
o
JR
M K
1( ) ( ) a
TELn k Ln A R T
Ln(k)
1/T
1 1a
b a
E
R T TTb Tak k e
Or:
Pizza Kinetics
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Leenson, 1999 What are the kinetics of
pizza spoilage?
Do they conform to Arrhenius?
J. Chem Ed., 76:4:504-505
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Pizza II
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Arrhenius plot t~k
Time (min)
0 20 40 60 80 100
Abs
orba
nce
at 2
92 n
m (
cm-1
)
0.00
0.05
0.10
0.15
0.20
0.25
0.30
0.35
Lab Project Example Data #I
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0.1 M NaOH
What is the Absinf ?
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Time (min)
0 20 40 60 80
Ln (
A2
92-A
29
2in
f)
-6
-5
-4
-3
-2
-1
b[0] -1.5509712892 b[1] -0.0400283854
Lab Project Example Data #II
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0.1 M NaOH
Set Absinf = 0.085
time vs ln(A-Ainf) Plot 1 Regr
Time (min)
0 20 40 60 80
Abs
orb
an
ce a
t 2
92 n
m (
cm-1
)
0.00
0.05
0.10
0.15
0.20
0.25
0.30
0.35
Lab Project Example Data #III
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0.05 M NaOH
Set Absinf = ?
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Time (min)
0 20 40 60 80
Ln
(A
292
-A29
2inf
)
-9
-8
-7
-6
-5
-4
-3
-2
-1
b[0] -1.4076822953 b[1] -0.0862394216
Lab Project Example Data #IV
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0.05 M NaOH
Set Absinf = 0.094
Maybe too high ?Downward curvature
time vs ln(A-Ainf) Plot 1 Regr
Time (min)
0 20 40 60 80
Ln (
A2
92-A
292i
nf)
-7
-6
-5
-4
-3
-2
-1
b[0] -1.6667372496 b[1] -0.0679233226
Lab Project Example Data #V
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0.05 M NaOH
Set Absinf = 0.092
Looks better, except for final data where relative error is high,Use only earlier data?
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Time (min)
0 10 20 30
Ln
(A
292
-A29
2in
f)
-4.5
-4.0
-3.5
-3.0
-2.5
-2.0
-1.5
-1.0
b[0] -1.5462593144 b[1] -0.0744460114
Lab Project Example Data #VI
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0.05 M NaOH
Set Absinf = 0.092
Using only earlier data where relative error is low,Better linearity and estimate of kobs?
Related systems
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CEE 697KENVIRONMENTAL REACTION KINETICS
IntroductionDavid A. Reckhow
CEE 697K Lecture #2 39Updated: 4 September 2013
Print version
Lecture #2b
Introduction: Simple Rate Laws Brezonik, pp.31-39
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Variable Kinetic Order
Any reaction order, except n=1
nnck
dt
dc
11
111
1
nnon
o
tckncc
tkncc nn
on
111
11
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Half-lives
Time required for initial concentration to drop to half, i.e.., c=0.5co
For a zero order reaction:
For a first order reaction:
c c kto 2
15.0 ktcc oo k
ct o5.0
21
c c eokt 2
1
5.0kt
oo ecc
k
kt
693.0
)2ln(2
1
Example: Benzyl Chloride
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Use: Manufacture of benzyl compounds, perfumes,
pharmaceuticals, dyes, resins, floor tiles
Toxicity Intensely irritating to skin, eyes, large doses can cause
CNS depression
Emission 45,000 lb/yr
Fate Benzyl chloride undergoes slow degradation in water to
benzyl alcohol
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Benzyl chloride II
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25ºC
Sources:•Schwarzenbach et al., 1993, Env. Organic Chemistry•1972, J. Chem.Soc. Chem. Comm. 425-6•1967, Acta Chem. Scand. 21:397-407•1961, J. Chem. Soc. 1596-1604
][][
Akdt
Ad
Benzyl chloride to benzyl alcohol
Nucleophilic substitution SN1 or SN2?
How to distinguish?
Salt effects
CH2Cl CH2OHH2O
HCl
Temperature
0.1ºC 25ºC
K 0.042x10-5 s-1 1.38x10-5s-1
T1/2 19.1 d 0.58 d
Mixed Second Order
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Two different reactants
Initial Concentrations are different; [A]0≠[B]0 The integrated form is:
Which can be expressed as:
productsBA k 2
dt
Ad
dt
d
Vrate
A
][11
xBxAk
BAkdt
dx
002
2
][][
]][[
tkBA
AB
BA 20
0
00 ][][
][][ln
][][
1
0
0002 ][
][log][][43.0
][
][log
A
BtBAk
B
A
][
][log
B
A
t0
0
][
][log
B
A
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Mixed Second Order
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Initial Concentrations are the same; [A]0=[B]0
The integrated form is:
Which can be integrated:
productsBA k 2
xAxAk
AAkdt
dx
002
2
][][
]][[
02 ][
12
][
1
Atk
A
][
1
A
t0][
1
A
xBxABA 00 ][][][][
dtkA
AdA 22][
][ tkAA 2
0
2][
1
][
1
David A. ReckhowCEE 697K Lecture #2
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Pseudo first order
For most reactions, n=1 for each of two different reactants, thus a second-order overall reaction
112 BAcck
dt
dc
115 min109.3 Lmgxk
Many of these will have one reactant in great excess (e.g., B) These become “pseudo-1st
order in the limiting reactant, as the reactant in excess really doesn’t change in concentration
Bc
Ac
productsBA k 2
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0102030405060708090
0 20 40 60 80
Time (min)
Co
nc
en
tra
tio
n
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Pseudo-1st order (cont.)
Since C2 changes little from its initial 820 mg/L, it is more interesting to focus on CA
CA exhibits simple 1st
order decay, called pseudo-1st order The pseudo-1st order rate
constant is just the “observed rate” or kobs
112 BAcck
dt
dc
tkAoA
obsecc
1
52
min032.0
)820(109.3
xckk Bobs
Example: O3 & Naphthalene
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How long will it take for ozone (4.8 mg/L dose) to reduce the concentration of naphthalene by 99%?
Used in moth balls and as a chemical intermediate
2nd order reaction; k2 = 3000 M-1s-1
Table 1 in Hoigne & Bader, 1983 [Wat. Res. 17:2:173]
Industrial WW with 0.1mM naphthalene Both reactants are at same (0.1mM)
concentration Therefore, this reduces to a simple 2nd
order reaction
tkAA 2
0][
1
][
1
t300010
1
10
146
min5.5
sec330
000,9903000
t
t
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O3 & Naphthalene (cont.)
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Contaminated river water (0.001 mM) Now ozone is in great molar excess, so this is a pseudo-1st
order reaction tBkeAA 02 ][0][][
sec4.15
3.0605.4
10300010
10ln
][][][ln
46
8
020
t
t
t
tBkAA
Molecularity of three: 3rd order kinetics
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Quite improbably, but sometimes happens Three different reactants
Complicated integrated form exists
Two different reactants
Integrated form:
productsCBA k 3
xCxBxAkCBAkdt
dx 00033 ][][][]][][[
productsBA k 32
xBxAkBAkdt
dx 0
203
23 ][2][][][
tkABBA
AB
AA
ABAA3
200
0
0
0
000 ][][2][][
][][ln
][][
][][2][][
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3rd Order (cont.)
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Only one reactant or Initial Concentrations are the same
The integrated form is:
Which can be integrated:
productsA k 33
xAxAxAk
AAAkdt
dx
0003
3
][][][
]][][[
20
32 ][
16
][
1
Atk
A
2][
1
A
t
20][
1
A
dtkA
AdA 33][
][ tktkAA A 332
02
62][
1
][
1
3rd Order (cont.)
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Pseudo-2nd order reactionsWhen one of the reactants has a fixed concentration
E.g., present in excess or buffered, or acts catalytically
Like a regular 2nd order reaction with two reactants but observed constant is fundamental rate constant times concentration of the 3rd reactant.
The integrated form:
tCkBA
AB
BA][
][][
][][ln
][][
13
0
0
00
obsk
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Example: chlorate formation
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Formation of chlorate in concentrated hypochlorite solutions Concern: chlorate is toxicMCLG=0.2 mg/L
Stoichiometry
Is this 3rd order? Be skeptical!
Observed kinetics
So, why is it 2nd order?
ClClOOCl 23 3
23 ][
OClkdt
ClOdobs
Chlorate example (cont.)
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Answer: this is a reaction pathway composed of two elementary reactions Step #1 Step #2
In multi-step reactions such as these, we say that the overall rate is determined by the slowest step
Called the “rate-limiting step” or RLS
Rate law is written based on the RLS Subsequent steps are ignored Prior steps are incorporated as they determine the
concentrations of the RLS reactants
ClClOOCl slow22
ClClOClOOCl fast32
Homework #2 is based on this reaction
H
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Reversible reaction kinetics
For a general reversible reaction:
k
qQ + pP bB + aA
k
r
f
And the rate law must consider both forward and reverse reactions:
where,kf = forward rate constant, [units depend on a and b]kb or kr = backward rate constant, [units depend on a and b]CP = concentration of product species P, [moles/liter]CQ = concentration of product species Q, [moles/liter]p = stoichiometric coefficient of species Pq = stoichiometric coefficient of species Q
pPr
bB
aAf CCkCCkrate
David A. ReckhowCEE 697K Lecture #2
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Stumm & MorganFig. 2.10Pg. 69][][ 21 BkAk
dt
dB
eqKk
k
A
B
BkAkdt
dB
2
1
21
][
][
][][0
Kinetic law
Eventually the reaction slows and, Reactant concentrations
approach the equilibrium values
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Reversible 1st order (cont.)
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Solution to non-equilibrium reaction period See Brezonik, pg 37-38 for details
Where k* = kf + kr
And:
Where:
tkfr ekkA
kA
*
0*][
1][
k
P A
k
r
f
tk
equ
equ eAA
AA *
][][
][][
equ
equequ
r
f
A
PK
k
k
][
][
Linearized version
David A. ReckhowCEE 697K Lecture #2
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