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Chapter 12 Environmental Chemical Reactions and Transformations There are more than 70,000 synthetic chemicals that are in daily use. solvents components of detergents dyes and varnishes additives in plastics and textiles chemicals used for construction antifouling agents herbicides insecticides fungicides The US EPA in the 1990 Clean Air Amendments estimates that there are ~2000 excess deaths in the US each year due to exposures to hazardous chemicals 1
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Page 1: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

Chapter 12 Environmental Chemical Reactions and Transformations

There are more than 70,000 synthetic chemicals that are in daily use.

solventscomponents of detergentsdyes and varnishesadditives in plastics and textileschemicals used for constructionantifouling agentsherbicidesinsecticidesfungicides

The US EPA in the 1990 Clean Air Amendments estimates that there are ~2000 excess deaths in the US each year due to exposures to hazardous chemicals

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Page 2: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

Chapter 12 Environmental Chemical Reactions and Transformations

Photochemical Biological-Microbial Dark reactions

1.kinetics order of a reaction Arrhnenius temperature -rate const rate limiting steps steady-state approximation Hammett relationships and rate constants Langmiurian rate constants kinetic simulations

2.mechanisms hydrolysis organics in the environment

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Page 3: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

Kinetics: the rate law of a reaction must be verified by experimentation

1st order reactions

A ---> B

-d [A] /dt = krate [A]

- d [A]/[A] = kratedt

[A]t= [A]0 e-kt

typically to get a 1st order fit, 70% of A needs to react ifthe rate constant is independent of concentration

-CH2- Cl + H2O---> -CH2- OH + H+ + Cl-

benzyl chloride benzyl alcohol

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Page 4: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

Figure 12.1 page 470 Fig. 12.2

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Page 5: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

t1/2 = time it takes for [A] to decrease by a factor of 2

ln [A]/[A]o=-k t1/2 ; ln2 /k =t1/2

life times are define slightly differentlyln e = -k

1/k =

1/k = time scale for the reaction

Pseudo first order rate constants

A. The reaction of benzyl chloride to produce benzyl alcohol water reacts with benzyl chloride

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Page 6: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

d[benz-Cl]/dt= -k [benz-Cl] [H2O]k here is a second order rate const. in L mol-1sec-1

If we assume that the reaction is run in dilute solutions as we could say that the [H2O] is constant

kpseudo = k[H2O]

d[benz-Cl]/dt= -kpseudo [benz-Cl]

B. Consider the reaction of methyl mercaptan in water to produce dimethyl disulfide

2CH3 SH + ½ O2 ----> H3 C-S-S-CH3

d[CH3 SH]/dt = k [CH3 SH]2 [O2]1/2

if we assume that O2 is constant

d[CH3 SH]/dt = kpseudo [CH3 SH]2

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Page 7: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

For the special case of [A] reacting with [A]

A + A products

Since A is reacting with A

and

for this type of simple second order reaction, plot of 1/[A]t

vs. t gives a straight line with a slope of...??? and an intercept of....?

the half-life is when [A]t = ½ [A]o

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Page 8: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

More on second order reactions

if A + B----> productsand x is the amount of A and B reacted

the differential equation that describes a second order rate law for the change in x with respect to time

dx/dt = - k[A] [B]or

dx/dt = - k [Ao-x] [Bo-x]

this has an exact solution

so if we measure the amount reacted, x, over time and plot the left side of the equation vs time, the rate constant, k can be measured

Rate Constants and Temperature

1850 - Wilhelmy related rate constant to temperature

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Page 9: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

1862 - Bertholet proposed k = A eDT

1889 - Arrhenius showed that the rate constant increases exponentially with 1/temp.

1884 - van’t Hoff Equation

where Kc= “concentration equilibrium constant”U = ‘standard internal energy changeand

Kc = k1/k-1

so

van’t Hoff proposed two energy factors, so that

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Page 10: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

U = E1 - E-1

It follows that: ln k1 = - E1/RT +const

or k1 = A e-E1 /RT (Arrhenius Equation)

There are other equations relating temp and rate constants

1898 van’t Hoff rate equation usually give very good empirical fits

The Arrhenius equation is most widely used because it provides insight into how reactions proceed

k1 = A e-Ea/RT ln k1 = ln A - Ea/RT

(see Table 12.2 page 349- old book) effect of temp on rate constants (new book does not have this table)

krate (Ti/T2) = eEa (1/T2-1/T1)/R

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Page 11: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

krate relative to 25oC x 100 (%)EakJ/mol

10oC 20oC 30oC Avg increase in krate

40 42 76 130 1.850 34 71 139 2.060 28 43 149 2.3

Theory of Arrhenius

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Page 12: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

Consider the reaction of B +C ---> D + E

dB/dt = -k [B] [C]

to react B and C have to collide, and the rate should depend

1. on the frequency of encounters of B and C which is proportional to the conc. of B and C and how fast B and C move (diffuse) toward each other.

2. the orientation of B and C

3. the fraction of the collisions that will have sufficient energy to break the bonds of B and C.

The fraction of reaction species with an energy greater than the activation energy is given by the Botlzmann distribution of energies

e-Ea/RT

hence in rate = A e-Ea/RT[B] [C]

the coef A must include frequency and orientation factors

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Page 13: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

Activated Complex or transition state theory

the reaction of B + C ---> on its way to products goes though an activated intermediate called [BC]

B + C ---> [BC]‡--> [D] + [E]

it is assumed that there is an equilibrium between the reactants and the activated complex [B-C]

and that [B-C] decomposes to products with a rate constant of

kT/h

where k = Boltzmann const1.38 x10-23 J K-1

h= Plancks const, 1.63 x10-34 J/sec

k T/h assumes that the rate constant is directly proportional to the vibrating frequency of the transition state and the energy associated with this is proportional to kT

= kT/h

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Page 14: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

[BC] ‡--> [D] + [E]

rate = kT/h [BC]‡

since we said

B + C --> <-- [B-C]‡

substituting for [BC]* in: rate = kT/h [BC]‡

rate = kT/h K‡ [B] [C]

The equilibrium const. is related to the free energy of activation by

K‡= e-G‡/RT

and G‡ = H‡-TS‡

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Page 15: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

for a bimolecular reaction H‡ = Ea - RT

this looks like k= A e-Ea / RT

the entropy term in A --> orientation probability

and temp in A may be related to the frequency of encounters; # collisions ~ (RT)1/2

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Composite Reactions

Simultaneous Reactions

A--> Y

A---> Z

Competition reactions

A + B --> Y

A + C --> Z

Opposing Reactions

A + B Z

Consecutive reactions

A--> X--> Y-->Z

FeedbackA--> X--> Y---> Z

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Page 17: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

Consecutive Reactions

k1 k2

A ---> X---> Z

-d[A]/dt = k1 [A] [A] = [A]o e-k1t

+d[X]/dt = k1[A]

d[X]/dt = +k1[A] - k2[X]

d[X]/dt = +k1[A]oe-k1t +- k2[X]

solution

[X] =[A]ok1/(k2-k1) (e-k1t- e-k2t)

[Z] =[A]o/(k2-k1) [k1(1-e-k1t) -k1(1- e-k2t)

These types of expressions are cumbersome

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Page 18: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

(Steady- state approximation)

“The rate of change of the concentration of an intermediate, to a good approximation, can be set equal to zero whenever the intermediate is formed slowly and disappears rapidly” -D.L. Chapman and L.K. Underhill, 1913

Use of the Steady-State Assumption

(Consecutive Reactions with an Opposing Reaction as the 1st step)

Consider the reaction of OH radicals in the atmosphere with SO2 to form sulfuric acid particles.

k1

OH + SO2 HOSO2‡

k-1

k3

HOSO2‡ + M ---> HOSO2 + M

for the rate of formation of HOSO2‡, we would write

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Page 19: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

d [HOSO2]‡/dt = +k1[OH][SO2]

for the loss we have-k-1[HOSO2] ‡

and-k3[HOSO2]‡

so the total rate expression is

d [HOSO2]‡/dt = +k1[OH][SO2]-k-1 [HOSO2]‡ -k3[HOSO2]‡

at steady state d[HOSO2]‡/dt = zero

0=+k1[OH][SO2] -k-1[HOSO2]‡ -k3[HOSO2] ‡

for the formation of product HOSO2

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Page 20: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

HOSO2‡ + M ---> HOSO2 + M

d[HOSO2]/dt = +k3[HOSO2]‡

Substituting [HOSO2]‡

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Page 21: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

In the atmosphere the formation of ozone can be represented as

hNO2 -------> NO + O. k1= 0.4xTSR

MO. + O2 ----> O3 k2 = fast,fast

O3 + NO -----> NO2 k3

a. derive a steady state relationship for O3 as a function of NO2, NO, k1 and k3; assume that dNO2/dt is at ss..

b. calculate the equilibrium ozone for the following conditions

time 7:00 9:00 12:00 15:00

NO (ppm) 0.1 0.05 0.03 0.005NO2 (ppm) 0.03 0.14 0.15 0.10Temp (oC) 25 27 35 34TSR(cal cm-2min-1) 0.05 0.2 0.5 0.3

plot your results for NO, NO2, and O3 and if this was a real atmosphere explain.

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Page 22: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

Rate determining steps

k1 k3

A + B X Z k-1

if k3 >> k1

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Page 23: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

The Hammett Equation and rates constants

In 1940 Hammett recognized for substituted benzoic acids the effects of substituent groups on the dissociation of the acid group

COOH

R

COO-

R

+H+

Go= GoH + Go

i

Effect on the free energy change from dissociation could be represented as the sum of the free energy change by the unsubstituted benzoic acid and the contributions from the various R groups.

we know that

Go = -2.303 RT log Ka

and Go

H = -2.303 RT log KaH

Goi = -2.303 RTi

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Page 24: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

-2.303 RT log Ka=-2.303 RT log KaH +-2.303 RTi

log (Ka / KaH )= i

when considering other compound classes, like phenyl acetic acids the values developed for benzoic acid can be used

log (Ka / KaH) = i

Figure 8.7 page 174

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Page 25: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

if an aromatic reaction is going through a transition state

B + C ---> [BC]‡--> [D] + [E]

we said that the rate

rate = (kT/h) K‡ [B] [C]

the rate constant is (kT/h) K‡

log krate= log (kT/h)+ log K‡

since -2.303 RT log K‡= G‡o

Using the Hammett argument that

G‡o= G‡oH + G‡o

i

show that log(krate) = log krateH + m,p

or log(krate/krateH) = m,p

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Page 26: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

Figure 12.2 page 354 (old book) new book does not have this figure

Different rates are obtained in different solvents, so reaction rates are not directly applicable to water if in another solvent

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Page 27: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

The Taft Relationship

Attempts to extend Hammett type LFERs to aliphatic compounds.

G‡= G‡ref + G‡

i,electronic+G‡i,steric

= polar effects Es= steric effects and are fitting parameters to a reference system

Taft chose the hydrolysis of carboxylic acid ester system because he could use different R groups with different steric and inductive effects

By varying R1 but keeping R2, solvent and temp. constant, Taft proposed that the steric effects of R1 as compared to a methyl group and can be derived

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Page 28: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

directly from the rate constant kA for the acid-catalyzed hydrolysis reaction.

Es = log (ka/ kA, ref)

This implies that the acid-catalyzed reaction compared to the base catalyzed reaction does not have inductive effects (when we look at this we will see why in about two lectures).

To determine inductive effects (*)the reaction is run under a basic catalyzed regime and when both inductive and steric effects are operative.

* = log (kB/kB,ref) – log (ka/ kA, ref )

In the literature, you will sometimes see *’ = * /2.48 ,to put it on the same scale as the Hammett values.The direction and tends of * values, is similar to Hammett values; ie withdrawing groups (Fl, Cl, NO2) are positive and donating slightly positive or negative (C2H5)

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Page 29: Chapter 12 Environmental Chemical Reactions and ... · Web viewChapter 12 Environmental Chemical Reactions and Transformations Photochemical Biological-Microbial Dark reactions kinetics

page 356 Table 12.4

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