july 6, 2017 - 北海道大学pcat.cat.hokudai.ac.jp/class/pc2017/20170706_bo_sapporo.pdf ·...
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2017/07/06─Advanced Course in Environmental Catalytic Chemistry 1
July 6, 2017
Advanced Course in Environmental Catalytic Reaction Chemistry I 2
Advanced Course in Environmental Catalytic Chemistry I
understanding chemistry by understanding photocatalysisunderstanding photocatalysis by understanding chemistry
Division of Environmental Material Science, Graduate School of Environmental ScienceThe first semester of Fiscal 201708:45─10:15, Thursday at Lecture Room D103
Bunsho Ohtani (Ewa Kowalska/Mai Takashima)
Institute for Catalysis, Hokkaido University, Sapporo 001-0021, Japan011-706-9132 (dial-in)/011-706-9133 (facsimile)
[email protected]://pcat.cat.hokudai.ac.jp/pcat
Advanced Course in Environmental Catalytic Reaction Chemistry I 3
objectives/goal/keywords
objectivesUnderstanding the mechanism of decomposition of pollutants, methods of photocatalysts preparation, design of practical photocatalytic reaction systems, and strategy for enhancement of photocatalytic activity.
goalTo understand principle of photocatalytic reaction from the standpoint of chemistry and strategy for practical applications. To obtain scientific method for research on functional solid materials.
keywordsPhotocatalyst, Photoinduced oxidative decomposition, Superhydrophilicity, Excited electron-positive hole, Structure-activity correlation, Higher photocatalytic activity, Visible-light response
Advanced Course in Environmental Catalytic Reaction Chemistry I 4
schedule
(1) Apr 13 introduction of photocatalysis(2) Apr 20 interaction between substances and light(3) Apr 27 electronic structure and photoabsorption(4) May 11 thermodynamics: electron and positive hole(5) May 18 adsorption(6) May 25 environmental application of photocatalysis (Professor
Ewa Kowalska)(7) Jun 1 kinetic analysis of photocatalysis(8) Jun 8 steady-state approximation(9) Jun 15 kinetics and photocatalytic activity(10) Jun 22 artificial photosynthesis (Professor Mai Takashima)
Jun 29 (no class)(11) Jul 6 action spectrum analysis (1)(12) Jul 13 action spectrum analysis (2)(13) Jul 20 crystal structure(14) Jul 27 design and development of photocatalysts(15) Aug 3 summary: photocatalysis A--Z
Advanced Course in Environmental Catalytic Reaction Chemistry I 5
comments on this lecture
Please send email in Japanese or English within 48 hours
to: [email protected]: pc2017MMDD-XXXXXXXX
[email protected](full name)(nickname)(comments and/or questions on today's lecture)
Advanced Course in Environmental Catalytic Reaction Chemistry I 6
special report
special report for extra (bonus) score (20 point)report on critical review on "photocatalysis" in Wikipedia, pointing out errors, misunderstanding and speculationsbased on the contents of this lecture.http://en.wikipedia.org/wiki/Photocatalysishttp://ja.wikipedia.org/wiki/光触媒
• Japanese or English• A4 size 2 pages• submission by email attachment• a PDF file is more preferable than a Word file• email title: pc20170727-XXXXXXXX• file name: pc20170727-XXXXXXXX.pdf (or .docx or .doc)• deadline of submission: July 27, 2017 23:59
2017/07/06─Advanced Course in Environmental Catalytic Chemistry 7
kinetics of photoinduced reaction
There are two limits: linear part and saturated part.
concentration of subsrate(s)
rate
of r
eact
ion
proportional to concentration
approaching to the limit, I
keh[S] + krr =
I keh[S]
I
2017/07/06─Advanced Course in Environmental Catalytic Chemistry 8
concentration of substrate
• overall rate of photocatalytic reaction based on steady-state approximation for electron-hole pairs
r = I keh[S] / (keh[S] + kr) or
r = I keh[S] / kr (when keh[S] << kr)
• meaning of keh[S]: rate of SURFACE REACTION with electron-hole pairs with surface-adsorbed substrate
• two possible cases:(1) adsorption equilibrium during the reaction(2) non-equilibrium due to faster consumption of substrate on the surface
= diffusion-limited process
2017/07/06─Advanced Course in Environmental Catalytic Chemistry 9
adsorption and photocatalytic activity
• the larger the adsorbed substrate(s), the higher the activity
• the larger the surface area, the larger the adsorbed amount
an examplelinear relation between the rate and adsorbed silver ion (J. Phys. Chem., 87 (1997) 3550.
Sr
eh kkIr
2017/07/06─Advanced Course in Environmental Catalytic Chemistry 10
first-order kinetics
• two possible cases:(1) adsorption equilibrium during the
reaction in Henry fashion (or low-concentration part of Langmuirian fashion) for the equation
r = I keh[S]/ kr = (aI keh/kr)C
(2) non-equilibrium due to faster consumption of substrate on the surface= diffusion-limited process: The reaction rate is determined by the rate of diffusion with a constant a.
[S] ~ 0r = aC = bSC
S: specific surface area
light-intensity dependence
first order
vs.
at higher intensity region
zeroth order
2017/07/06─Advanced Course in Environmental Catalytic Chemistry 11
Fick's law of diffusion
• rate (flux; J) of diffusion
• diffusion constant D include area of "hypothetical wall".
• J = DC if surface concentration is zero.
• for particles,
hypothetical wall = thin diffusion layer surrounding the surface
hypotheticalwall
x axis
xCDJ
lowconcentration
side
hypothetical wall high concentration
side
2017/07/06─Advanced Course in Environmental Catalytic Chemistry 12
photocatalytic activity
• Assuming the definition of "photocatalytic activity" to be INTRINSIC ability of a photocatalyst to drive photocatalytic reaction, what is(are) the term(s) showing photocatalytic activity?
• C, I: reaction condition adjusted freely• S, K, : properties of solid (extrinsic ability)• keh, kr (or their ratio, keh/kr): intrinsic ability
Can we measure keh and kr from experimental results?
KC
SKCkkI
r r
1
eh
2017/07/06─Advanced Course in Environmental Catalytic Chemistry 13
data analysis for photocatalysis
0 2 4 6 8 100
5x106
1x107
1.5x107
2x107
1/r
1/C
kSCkKSr1111
0 0.2 0.4 0.6 0.8 10
2x106
4x106
6x106
8x106
C/r
C
kKSC
kSrC 11
r = I kehSKC/ kr(1 + KC) = I (keh/kr)SKC/ (1 + KC)1/r = (1/kKS)(1/C) + 1/kS, where k = I (keh/kr)
• Plots (left and right) may give K and kS, but not k or kr, ke-h.
2017/07/06─Advanced Course in Environmental Catalytic Chemistry 14
Langmuir-Hinshelwood mechanism
• bimolecular reaction: reaction of two substrates, A and B adsorbed on surface with a reaction rate constant k.
• Common surface cites adsorb substrates A and B with equilibrium constants, KA and KB, respectively.
• Both A and B are adsorbed on the surface in Langmuirian fashion, with a total (saturated) concentration of the surface sites, S.
• Assuming the bulk concentration of A and B, CA and CB, respectively, rate r is proportional to surface concentrations of A and B, and then:
2BBAA
BBAA2
1 CKCKCKCKkSr
2017/07/06─Advanced Course in Environmental Catalytic Chemistry 15
Eley-Rideal mechanism
• bimolecular reaction: reaction of two substrates, A and B, adsorbed on surface and coming from the bulk, respectively, with a reaction rate constant k.
• Surface cites adsorb substrates A with equilibrium constants, KA.• A is adsorbed on the surface in Langmuirian fashion, with a total
(saturated) concentration of the surface sites, S.• Assuming the bulk concentration of A and B, CA and CB, respectively,
rate r is proportional to surface concentration of A and B in the bulk, and then:
AA
BAA
1 CKCCkSKr
2017/07/06─Advanced Course in Environmental Catalytic Chemistry 16
action spectrum analysis
action spectrum analysisstatistical analysis
action spectrum analysis 17
super hydrophilicity & oxidative decomposition
Photoirradiation onto titania surface induces super hydrophilicity to make water-contact angle to be almost zero.1
Photoirradiation onto titania film decomposes adsorbed methylene blue.
titania-coated : ordinary glass
action spectrum analysis 18
photocatalytic reaction
Photocatalytic reaction is a kind of photoreaction and therefore cannot be a series reaction: a parallel reaction initiated by photoabsorption with short-live species, e.g., photoexcited electrons and positive holes
electron-holepair
recombi-nation
photo-absorption
redox(chemical)reaction
1
2
3
action spectrum analysis 19
necessary conditions for photocatalytic reactions
reaction initiated by photoabsorption of photocatalyst• (generally accepted) blank test: Copresence of 3 requisites, photoirradiation,
photocatalyst (solid material) and reaction substrate(s) is indispensable.• Photoreaction initiated by photoabsorption of a compound adsorbed by a solid
surface and subsequent electron injection also requires 3 requisites.• action spectrum analyses: possible sole technique to prove what absorbs light to
initiate the photoreaction• checking product(s): adsorption can decrease the amount of substrate(s);
stoichiometry
photoabsorber (= photocatalyst) remaining unchanged• checking turnover frequency: molar ratio of product(s) to photocatalyst to be
more than unity
20
juice16 juice 16
beer 33beer33
逆converse
裏inverse
裏inverse
逆converse
対偶contra-positive
beer16killer
21
対偶contra-positive
PClight &solid &S
逆converse
notPC
light ||solid ||S
notPC
light ||solid ||S
逆converse
裏inverse
裏inverse
photo-cataly-sis (PC)
light &solid &subst-rate (S)
&: AND||: OR__: NOT
notPC
light &solid & Skiller e.g. dye-sensitized
reaction
22
対偶contra-positive
PClight ||solid ||Skiller
PClight &solid &S
逆converse
notPC
light ||solid ||S
notPC
light ||solid ||S
逆converse
裏inverse
裏inverse
photo-cataly-sis (PC)
light &solid &subst-rate (S)
&: AND||: OR__: NOT
action spectrum analysis 23
visible-light responsive photocatalyst
white titania (TiO2) absorbing only ultraviolet light giving color by SOME treatment(s)activity under visible-light irradiation?
titaniawithcolor
titaniavisible lightresponsive
titania=/
24
対偶contra-positive
VIS-in-ducedPC
VIS photoabsorptionkiller
VIS-in-ducedPC
VIS photo-absorption
逆converse
notVIS-PC
VIS photo-absorption
notVIS-PC
VIS photo-absorption
逆converse
裏inverse
裏inverse
VIS-in-ducedPC
VIS photo-absorption
&: AND||: OR__: NOT
action spectrum analysis 25
photoreaction/photocatalytic
reaction
wavelength 1
wavelength 2
wavelength 3
wavelength 4
response (product, current...)
・・・
measurement of action spectrum
• plots of apparent quantum efficiency (response normalized by number of incident photons) versus wavelength
wavelength
appa
rent
qua
ntum
effic
ienc
y
1 23
4
5
6
action spectrum analysis 26
action spectrum
wavelength/nm wavelength/nm
wavelength/nm
photoabsorptionefficiency
appa
rent
qua
ntum
effic
ienc
y
quantumefficiency
example: discrimination of active crystalline phase in anatase-rutile mixtures
T. Torimoto, et al., Phys. Chem. Chem. Phys., 4, 5910-5914 (2002).
action spectrum= apparent quantum
efficiency
action spectrum analysis 27
action spectrum analysis
J. Chem. Soc., FaradayTrans.1, 81, 2467 (1985).
appa
rent
action spectrum analysis 28
action spectrum measurement (1)
light source / monochromator / reaction cell
reaction cell
monochromator
xenon arc
cell holder
ca. 0.1 mW cm-2
FWHM: ca. 20 nm
action spectrum analysis 29
simultaneous irradiation
action spectrum measurement (2)
power meter
irradiation port
thermopile
wavelength adjustment
xenon arc
cell holders
0.1-18 mW cm-2
FWHM ca. 20 nm
action spectrum analysis 30
methylene blue as a substrate
Proving that MB is inappropriate as a test compound for the reaction under visible-light irradiation by action spectrum analyses.
cited 180 times by March 2016
action spectrum analysis 31
diffuse reflectance spectra in the unit of absorption normalized at 350 nm
1/2: wavelength giving half value to that at 350 nm
anatase-rutile mixture
fanataseanatase content estimated from XRD patterns
0
0.2
0.4
0.6
0.8
1
350 360 370 380 390 400 410 420
abso
rptio
n (n
orm
aliz
ed)
Wavelength / nm
Merck P-25
Wako(A)+CR-EL
CR-ELTIO-5
CR-EL(1473 K)360
370
380
390
400
0 0.2 0.4 0.6 0.8 1
1/
2/ n
m
fanatase
Merck
HombikatTIO-2
P-25
Wako(A)Merck+CR-EL
Wako(A)+CR-EL
TIO-5Aldrich(A<R)
Wako(R)CR-EL
CR-EL(1473K)
P-25(1473K)
0.5
skip
action spectrum analysis 32
test photocatalytic reactions for 35 titanias
(a) oxygen evolution along with silver metal deposition
4Ag+ + 2H2O = 4Ag + O2 + 4H+
(b) methanol dehydrogenation
CH3OH = HCHO + H2
(c) oxidative decomposition of acetic acid in water
CH3COOH + 2O2 = 2CO2 + 2H2O
(d) oxidative decomposition of acetaldehyde in air
CH3CHO + 5/2O2 = 2CO2 + 2H2O
(e) synthesis of pipecolinic acid from L-lysine
L-lysine = PCA + NH3
action spectrum analysis 33
CH3OH HCHO + H2
4Ag+ + 2H2O 4Ag + O2 + 4H+
CH3COOH + 2O2 2CO2 + 2H2O
action spectra of photocatalytic reaction
app
(nor
mal
ized
)0.5
00.2
0.40.60.8
1 (a)
00.2
0.40.60.8
1 (b)
0
0.2
0.4
0.6
0.8
1
350 360 370 380 390 400 410
Wavelength / nm
(c)
action spectrum analysis 34
360
370
380
390
400
410
0 0.2 0.4 0.6 0.8 1
1/2
/ nm
fanatase
Merck
CR-EL
Merck+CR-ELP25TIO-5
Aldrich(A<R)
Wako(A)+CR-EL
Wako(R)
Hombikat
CR-EL(1473 K)
P25 (1473 K)
TIO-2Wako(A)
370
380
390
400
410
0 0.2 0.4 0.6 0.8 1
1/2
/ nm
fanatase
MerckP25
Wako(A)
Merck+CR-EL
Aldrich(A<R)TIO-5
CR-EL
Wako(R)Wako(A)+CR-EL
CR-EL(1473 K)P25 (1473 K)
TIO-2
360
370
380
390
400
410
0 0.2 0.4 0.6 0.8 1
1/2
/ nm
fanatase
Wako(R)CR-EL
Hombikat
Merck
Wako(A)
Merck+CR-EL(1:1)Aldrich(A<R)
TIO-5
TIO-2
CR-EL(1473 K)P25 (1473 K)
P25
dehyderogenation of methanol1/2 versus fanatase
absorption edge wavelengthanatase: ca. 370 nmrutile: ca. 410 nm
R >> A
R A
A >> R
oxygen evolution & silver metal deposition
decomposition of acetic acid
inner-filter effectby rutile
action spectrum analysis 35
action spectra of anatase/rutile/P25
oxidative decomposition of acetic acid in an aqueous solution: carbon dioxide liberation
0
0.005
0.01
0.015
0.02
0.025
360 390 420 450
appa
rent
qua
ntum
effi
cien
cy (%
)
wavelength/nm
0
50
100
150
P25pure anatase pure rutile
reconstructed mixture
CH3COOH(CO2)
CH3CHO(CO2)
CH3OH(H2) <Pt>
Ag+
(Ag/O2)
amorphous
91
100
120 56
anatase
rutile
P25
skip
Ohtani, B.; Prieto-Mahaney, O. O.; Li, D.; Abe, R. J. Photochem. Photobiol. A Chem.216 (2010) 179-182.
action spectrum analysis 36
hydrogen evolution from methanol
isolated anatase: Aisolated rutile: Rplatinization:
photodeposition (0.2 or 2wt% loading)
• negligible activity of all bare samples
• 0.2wt%-Pt loaded P25 ~ A + Pt/R (85:15)
• 2wt%-Pt loaded P25 ~ Pt/A + Pt/R (85:15)
comparable activity of Rwith A when platinized
photodeposition occurs preferentially on rutile particles
0
0.2
0.4
0.6
0.8
1
360 390 420
appa
rent
qua
ntum
effi
cien
cy
wavelength/nm
2wt%Pt/R
0.2wt%Pt/P25
2wt%Pt/P25
A + Pt/R(85:15)
A/Pt + Pt/R(85:15)
2wt%Pt/A
0
0.2
0.4
0.6
0.8
1
360 390 420
2wt%Pt/R
0.2wt%Pt/P25
2wt%Pt/P25
A + Pt/R(85:15)
A/Pt + Pt/R(85:15)
2wt%Pt/A
0
0.2
0.4
0.6
0.8
1
360 390 420
2wt%Pt/R
0.2wt%Pt/P25
2wt%Pt/P25
A + Pt/R(85:15)
A/Pt + Pt/R(85:15)
2wt%Pt/A
action spectrum analysis 37
action spectrum: case 2
wavelength/nm wavelength/nm
wavelength/nm
photoabsorptionefficiency
action spectrum
appa
rent
qua
ntum
effic
ienc
y
quantumefficiency
Change of (intrinsic) quantum efficiency, i.e., efficiency of electron-hole utilization depending on the irradiation wavelength
may induce
shift of action spectrum
skip
action spectrum analysis 38
wavelength dependence100% anatase titania powders
dehydrogenation of methanol<platinum-loaded/under argon>
mineralization of acetic acid<under air>
CH3COOH + 2O2
2CO2 + 2H2OCH3OH
HCHO + H2
2017/07/06─Advanced Course in Environmental Catalytic Chemistry 39
comments on this lecture
Please send email in Japanese or English within 48 hoursto: [email protected]: pc20170706-XXXXXXXX
[email protected]<full name><nickname><comments on this lecture><question(s) if any>
2017/07/06─Advanced Course in Environmental Catalytic Chemistry 40
subject: pc20170706-12345678
pc20170706-12345678
大谷文章
某教授
光触媒の応用例について知り,その基本が化学であることを学びました.光と物質のかかわりについてさらに知りたいので本を調べてみます.
絶版になっている「光触媒標準研究法」はどこかで入手可能ですか.
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