master thesis_yang_final revised
TRANSCRIPT
ENHANCEMENT OF PHOTOCATALYTIC ACTIVITY BY SITE POISONING
PLATINUM DOPED TITANIUM DIOXIDE
A Thesis
Presented to
The Graduate Faculty of The University of Akron
In Partial Fulfillment
of the Requirements for the Degree
Master of Science
Yang Chu
December, 2014
ii
ENHANCEMENT OF PHOTOCATALYTIC ACTIVITY BY SITE POISONING
PLATINUM DOPED TITANIUM DIOXIDE
Yang Chu
Thesis
Approved:
_________________________________
Advisor
Dr. Steven S.C. Chuang
_________________________________
Faculty Reader
Dr. Xiong Gong
_________________________________
Department Chair
Dr. Coleen Pugh
Accepted:
_________________________________
Dean of the College
Dr. Eric J. Amis
_________________________________
Interim Dean of the Graduate School
Dr. Rex Ramsier
_________________________________
Date
iii
ABSTRACT
Photoelectrochemical cell (PEC) is a device that could interconvert chemicals and
electricity with the energy of light by the photovoltaic effect1. PEC is widely studied
recently for hydrogen production and waste organics degradation2. The main structure is
composed of photocatalyst, electrolyte, counter electrode and power supply. Water and
organics are converted to hydrogen and carbon dioxide gases by irradiating the
photocatalyst with ultraviolet radiation. The challenge for commercialization is mainly
because of the low efficiency. Extensive research has been directed toward developing
highly active photocatalysts by the doping of platinum. Platinum doped titanium dioxide
(Pt-TiO2) has shown the ability to faster degrade organics than TiO23, 4
. The mechanism is
that the low potential of platinum that functions as a trap for the electrons and thus
reduces the electron-hole recombination. However, there has not been a significant
breakthrough that can lead PEC to commercialization. Recently, we hypothesize that
selectively poisoning the electron generating site could significantly reduce the electron-
hole recombination. Pt-TiO2 was treated with hydrogen sulfur (Pt-TiO2/H2S) at high
temperature and H2S were converted to sulfur and completely covered the platinum.
Characterization of TiO2, Pt-TiO2 and Pt-TiO2/H2S both in powder and thin film format
was done by infrared spectroscopy (IR), ultraviolet-visible spectroscopy (UV-vis), x-ray
diffraction (XRD), scanning electron microscopy (SEM), transmission electron
microscopy (TEM) and energy-dispersive X-ray spectroscopy (EDS). Ethanol and some
other organics are added in electrolyte to increase the current density of the PEC and
iv
produce more hydrogen due to the lower oxidation potential than water5. Comparing the
working electrode of TiO2, Pt-TiO2 and Pt-TiO2/H2S in PEC, we analyzed the different
amount of gaseous products, the current density and the degradation of methylene blue.
The results showed that Pt-TiO2/H2S has the best oxidative activity per unit thickness of
catalyst. This research will lead us to find the applications of PEC in utilization of the
shale gas that can provide the energy with high efficiency and environmental friendly in
the future.
v
ACKNOWLEDGEMENTS
Firstly, I will thank my advisor, Dr. Steven Chuang for giving me this opportunity to do
research in his group. He provided me this project and taught me how to think for the
science and technology. I really appreciate Dr. Xiong Gong to be the reader for my
master thesis. He is so busy but he still squeezes his time to help me improve my writing
skill. I would like to thank the group members of the photocatalyst, who are Mehdi
Lohrasbi, Piyapong Pattanapanishsawat, Dan Huang, Jie Yu. They taught me how to set
up the experiment and the way to analyze the data. They are friends more than the
colleagues.
Secondly, I am very grateful for my parents. They give me all their love and understand
to support me to finish my Master degree. They are always the strongest backup whatever
I meet all the problems. I also need to thank all my friends. They helped me overcome the
hardest time in USA and always encourage me to do my favorite things.
Last, I am thankful to my wise, Yu Zhang. She did everything she could to help me finish
my Master degree. She is the most important people to me and she will always be.
vi
TABLE OF CONTENTS
Page
LIST OF FIGURES ......................................................................................................... viii
LIST OF TALBES ........................................................................................................... xiii
CHAPTER
I. INTRODUCTION ........................................................................................................... 1
II. LITERATURE REVIEW ............................................................................................... 4
2.1. Photocatalysts .......................................................................................................... 4
2.2. Titanium dioxide ...................................................................................................... 4
2.3. Photoelectrochemical cell ........................................................................................ 7
III. EXPERIMENTAL ...................................................................................................... 12
3.1. Preparation and characterization of platinum doped titanium dioxide and platinum
....................................................................................................................................... 12
3.1.1. Preparation of platinum doped titanium dioxide ............................................ 12
3.1.2. Preparation of platinum doped titanium dioxide treated by hydrogen sulfide 13
3.1.3. Preparation of TiO2 thin film, Pt-TiO2 thin film and Pt-TiO2/H2S thin film ... 14
3.1.4 Characterization of catalysts in forms of powder and thin film ....................... 16
3.2. Setup of photoelectrochemical cell ........................................................................ 17
3.3. Characterization of gas products and solution in photoelectrochemical cell ......... 19
3.4. Experimental procedure of photoelectrochemical cell .......................................... 19
IV. RESULTS AND DISCUSSION .................................................................................. 22
4.1. Characterization of TiO2-based catalysts ............................................................... 22
4.1.1 TiO2-based catalysts in powder and thin film form ......................................... 22
vii
4.1.2 TEM analysis of TiO2-based catalyst in powder form ..................................... 23
4.1.3 SEM analysis of TiO2-based catalysts in thin film form.................................. 25
4.1.4 FTIR spectroscopy characterization of TiO2-based catalysts .......................... 25
4.1.5 UV-Vis spectroscopy characterization of TiO2-based catalysts ....................... 30
4.1.6 Two-dimensional wide angle X-ray diffraction spectroscopy of TiO2-based
catalysts. .................................................................................................................... 32
4.1.7 Energy-dispersive X-ray spectroscopy of TiO2-based catalysts ...................... 33
4.2. Results of photoelectrochemical cell ..................................................................... 33
4.2.1 Photoelectrochemical reactions ....................................................................... 33
4.2.2 Electrical experimental results of photoelectrochemical cell .......................... 34
4.2.3 Gas production results of photoelectrochemical cell experiment. ................... 37
4.2.4 Photo oxidation of methylene blue in the photoelectrochemical cell experiment
................................................................................................................................... 39
4.2.5 pH change ........................................................................................................ 42
4.3. Conclusions ............................................................................................................ 45
REFERENCES ................................................................................................................. 46
APPENDICES .................................................................................................................. 51
APPENDIX A DYE-SENSITIZED SOLAR CELLS (DSSC) ..................................... 52
APPENDIX B INTENSITY OF UV LIGHT................................................................ 72
APPENDIX C PHOTO DEGRDATION OF PVC THIN FILMS ................................ 80
APPENDIX D NFPA AND HMIS RATING OF CHEMICALS ................................ 104
viii
LIST OF FIGURES
Figure Page
1. Organization of master project and thesis ....................................................................... 3
2. Band positions of several semiconductors in contact with aqueous electrolyte at pH 1. 5
3. Ball and stick model for three different forms of titanium dioxide. ............................... 6
4. (a) Chemical structure of methylene blue and the IR band assignment. (b) Variations of
the IR intensity of MB bands at 1488 cm-1 during 240 min of the MB photocatalytic
degradation. ................................................................................................................... 7
5. Current-voltage profile of the photoelectrochemical cell.. ............................................. 8
6. Experimental procedure of Pt-TiO2 preparation ........................................................... 13
7. Experimental procedure of Pt-TiO2/H2S preparation .................................................... 14
8. Experimental procedure of TiO2 paste preparation ....................................................... 14
9. Experimental procedure of TiO2 thin film preparation ................................................. 15
10. Schematic (Left) and picture (Right) of DRIFT cell................................................... 17
11. (a) Schematic setup and (b) pictures of photoelectrochemical cell............................. 18
12. First experimental procedure of photoelectrochemical cell. ....................................... 20
13. Second experimental procedure of photoelectrochemical cell. .................................. 21
14. Photograph of TiO2, 0.5 wt.% Pt-TiO2, 1.0 wt.% Pt-TiO2, 3.0 wt.% Pt-TiO2 and 0.5
wt.% Pt-TiO2/H2S powder........................................................................................... 22
15. Photograph of TiO2, 0.5 wt.% Pt-TiO2, 1.0 wt.% Pt-TiO2, 3.0 wt.% Pt-TiO2 and 0.5
wt.% Pt-TiO2/H2S thin film. ....................................................................................... 23
16. TEM pictures of TiO2, 0.5 wt.% Pt-TiO2 ,1.0 wt.% Pt-TiO2, 3.0 wt.% Pt-TiO2 and 0.5
wt.% Pt-TiO2/H2S. ...................................................................................................... 24
17. SEM pictures of TiO2, 0.5 wt.% Pt-TiO2 and 0.5 wt.% Pt-TiO2/H2S in thin film from
top and cross sectional views. ..................................................................................... 25
ix
18. (a) Single beam and (b) absorbance FTIR spectra of TiO2, 0.5 wt.% Pt-TiO2 and 0.5
wt.% Pt-TiO2/H2S in powder form. Absorbance was obtained by absorbance
=log(1/I), where I was the intensity of single beam. .................................................. 28
19. (a) Single beam and (b) absorbance FTIR spectra of TiO2, 0.5 wt.% Pt-TiO2 and 0.5
wt.% Pt-TiO2/H2S in thin film form. Absorbance was obtained by absorbance
=log(1/I), where I was the intensity of single beam. .................................................. 29
20. UV-vis spectroscopy of TiO2, 0.5 wt.% Pt-TiO2 and 0.5 wt.% Pt-TiO2/H2S in (a)
powder and (b) thin film form. ................................................................................... 31
21. XRD spectroscopy of TiO2-based catalysts in powder form. ..................................... 32
22. Schematic representation of the operating principle and reactions of
photoelectrochemical cell. .......................................................................................... 34
23. Time profiles of current density at different forward bias voltage for TiO2, 0.5 wt.%
Pt-TiO2 and 0.5 wt.% TiO2/H2S as working electrode. ............................................... 36
24. Time profiles of MS intensity at different forward bias voltage for TiO2, 0.5 wt.% Pt-
TiO2 and 0.5 wt.% TiO2/H2S as working electrode. H2 and CO2 were detected from
the gas products........................................................................................................... 37
25. Pictures of the CO2 blub formation during the experiment. ....................................... 37
26. Photograph of electrolyte containing methylene blue (a) before and after degradation
by (b) TiO2, (c) 0.5 wt.% Pt-TiO2 and (d) 0.5 wt.% TiO2/H2S. .................................. 40
27. UV-visible spectroscopy of electrolyte containing methylene blue before and after
degradation by TiO2, 0.5 wt.% Pt-TiO2 and 0.5 wt.% TiO2/H2S. ............................... 41
28. The change of pH values and current density during the experiments. ...................... 43
29. Effect of different UV light intensity on the pH change. ............................................ 44
30. Representation of a dye-sensitized TiO2 solar cell and the processes involved in
energy conversion (S represents the dye-sensitizer and I-/I3
- is the charge mediator). 52
31. Experimental procedure for screen printing. .............................................................. 56
32. The instrument and schematic procedure for spin coating. ........................................ 56
33. Photographs of TiO2 thin film corresponding to the 8. ............................................... 57
34. Measurement of the efficiency of DSSC. ................................................................... 59
35. The calculation of the efficiency of DSSC based on the voltage-current profile. ...... 60
36. The chemical structure of N719. ................................................................................. 61
x
37. The chemical structures of (a) Dye1 and (b) Dye2. .................................................... 63
38. The synthetic route of Dye1. ....................................................................................... 64
39. The synthetic route of Dye2. ....................................................................................... 65
40. Pictures of N719, Dye1 and Dye2 in solution. ........................................................... 65
41. The pictures of TiO2 thin films after immersing in Dye1 and Dye2 for 24 h. ............ 66
42. Current-Voltage profile of two DSSCs with and without electrolyte. ........................ 69
43. (a) Single beam IR spectroscopy and (b) Absorbance of the chemicals and the
solution of PEG polymer electrolyte........................................................................... 71
44. Schematic setup of UV light measurement. ................................................................ 72
45. The distribution of UV light intensity at different positions. ...................................... 73
46. The intensity of UV light at different positions with optical fiber. ............................. 74
47. 2D distribution of UV light intensity with optical fiber. Distance between detector and
light source is 17cm. ................................................................................................... 75
48. 2D distribution of UV light intensity with an angle between optical fiber and photo
detector. Distance between detector and light source is 17cm. ................................... 77
49. The UV light intensity at different positions without optical fiber. ............................ 78
50. 2D distribution of UV light intensity without optical fiber. Distance between detector
and light source is 17cm. ............................................................................................ 79
51. Differential absorbance IR spectra of the PVC samples before and after 30 minutes of
UV irradiation (200 mw/cm2, Hg lamp). .................................................................... 81
52. Absorbance vs. time spectra of the PVC 8 mil film samples before and after 30
minutes of UV irradiation (200 mw/cm2, Hg lamp) at 3255cm
-1. .............................. 82
53. Absorbance vs. time spectra of the PVC 8 mil film samples before and after 30
minutes of UV irradiation (200 mw/cm2, Hg lamp) at 2956cm
-1, 2923cm
-1 and
2850cm-1
. .................................................................................................................... 84
54. Absorbance vs. time spectra of the PVC 8 mil film samples before and after 30
minutes of UV irradiation (200 mw/cm2, Hg lamp) at 1784cm
-1. .............................. 85
55. Absorbance vs. time spectra of the PVC 8 mil film samples before and after 30
minutes of UV irradiation (200 mw/cm2, Hg lamp) at 1705cm
-1. .............................. 86
xi
56. Absorbance vs. time spectra of the PVC 4 mil film samples before and after 30
minutes of UV irradiation (200 mw/cm2, Hg lamp) at 3255 cm
-1. ............................. 87
57. Absorbance vs. time spectra of the PVC 4 mil film samples before and after 30
minutes of UV irradiation (200 mw/cm2, Hg lamp) at 1784 cm
-1. ............................. 88
58. (a) Single beam spectra of PVC control sample collected during the UV degradation.
(b) IR difference spectra obtained by IR difference= -log(I/I0), where I is the single
beam at specified times and I0 is the single beam at 0 min. (c) Top view picture of the
PVC control sample at the end of the UV degradation experiment. (d) Variation in the
intensity of C-O stretch band at 1043 cm-1
. ................................................................ 90
59 (a) IR difference spectra of RX14426 + PVC sample obtained by IR difference= -
log(I/I0), where I is the single beam at specified times and I0 is the single beam at 0
min. (b) Top view picture of RX14426 + PVC sample at the end of UV degradation
experiment. (c) Variation in the intensity of C-O stretch band at 1043 cm-1
. ............. 91
60. (a) IR difference spectra of RX14427 + PVC sample obtained by IR difference= -
log(I/I0), where I is the single beam at specified times and I0 is the single beam at 0
min. (b) Top view picture of RX14427 + PVC sample at the end of UV degradation
experiment. (c) Variation in the intensity of C-O stretch band at 1043 cm-1
. ............. 92
61. (a) IR difference spectra of Tinuvin 328 + PVC sample obtained by IR difference= -
log(I/I0), where I is the single beam at specified times and I0 is the single beam at 0
min. (b) Top view picture of Tinvuin 328 + PVC sample at the end of UV degradation
experiment. (c) Variation in the intensity of C-O stretch band at 1043 cm-1
. ............. 93
62. DRIFT IR spectra of (a) PVC control sample, (b) RX14426 + PVC sample, (c)
RX14427 + PVC sample and (d) Tinuvin 328 + PVC sample. .................................. 94
63. Variation in the intensity of C-O stretch band at 1043 cm-1
of PVC control sample,
RX 14426 + PVC sample, RX14427 + PVC sample and Tinuvin 328 + PVC sample.
..................................................................................................................................... 95
64. Variation in the intensity of IR peaks at (a) 3306 cm-1
, (b) 2851 cm-1
, (c) 1784cm-1
,
(d) 1395 cm-1
of PVC control sample, RX 14426 + PVC sample, RX14427 + PVC
sample and Tinuvin 328 + PVC sample. ..................................................................... 96
65. The locations of Control sample, RX14426, RX14427 and Tinuvin 328 and the scan
area of the focal plane array. ....................................................................................... 97
66. Experimental setup for UV degradation of Control sample, RX14426, RX14427 and
Tinuivn 328 by focal plane array. ............................................................................... 98
67. Photographs of Control sample, RX14426, RX14427 and Tinuvin 328 before and
after UV degradation tested by focal plane array. Single beam spectra were collected.
Red color stands for the high intensity and blue color stands for the low intensity. .. 99
xii
68. IR absorbance spectra of Control sample, RX14426, RX14427 and Tinuvin 328
before and after UV degradation. .............................................................................. 100
69. IR difference spectra of Control sample, RX14426, RX14427 and Tinuvin 328 before
and after UV degradation. Spectra were obtained by IR difference= -log(I/I0), where I
is the single beam at 180 min and I0 is the single beam at 0 min. ............................ 101
70. Statistics results of all the old experiments for variation in the intensity of –OH band
at 3306 cm-1
, -CH and –CH2 band at 2924 cm-1
, C=O band at 1724 cm-1
and C-O
stretch band at 1043 cm-1
. ......................................................................................... 102
xiii
LIST OF TALBES
Table Page
1. Cell current-voltage characteristics for various electrolyte compositions under UVA
(Black light) illumination. ............................................................................................. 9
2. Cell current-voltage characteristics under UVA (Black Light) illumination for various
ethanol contents. ........................................................................................................... 9
3. Cell current–voltage characteristics under UVA (Black Light) illumination for various
reactants in the anode compartment. ............................................................................11
4. Literature results of the performance of photoelectrochemical cell. .............................11
5. Cutting off wavelength and band gap of TiO2-based catalysts. .................................... 31
6. Atomic percentage of Ti, O, Pt and S in thin film TiO2, 0.5 wt.% Pt-TiO2 and 0.5 wt.%
Pt-TiO2/H2S. ................................................................................................................ 33
7. Hydrogen and carbon dioxide production at different forward bias for TiO2, 0.5 wt.%
Pt-TiO2 and 0.5 wt.% TiO2/H2S as catalysts. .............................................................. 38
8. Comparison with the results in literature of the cell performance. ............................... 39
9. Results of the UV-visible spectroscopy of electrolyte containing methylene blue before
and after degradation by TiO2, 0.5 wt.% Pt-TiO2 and 0.5 wt.% TiO2/H2S. ................ 41
10. Quality of TiO2 thin film fabricated by different paste and casting methods. ............ 57
11. Experimental results of the performance of DSSCs. .................................................. 60
12. Experimental results of DSSC with copper-complex dye. ......................................... 67
13. Performance of two dye-sensitized solar cells with and without electrolyte. ............. 68
14. The UV light intensity at different positions............................................................... 73
15. NFPA and HMIS rating of chemicals ....................................................................... 104
1
CHAPTER I
INTRODUCTION
In nowadays, air pollution and water pollution has become a big issue in many countries,
especially in some developing countries. Most of the pollutions are caused by the coal-
fired power plant and oil refinery. Scientists have done many works to look for some
clean energy that will not cause the pollutions. Clean energy usually includes water
energy, wind energy, nuclear energy, geothermal energy and solar energy. Solar energy
has been more and more attractive recently because it is limitless and easy to obtain.
In 1991, Michael Grätzel discovered a new kind of solar cells which is called dye-
sensitized solar cells (DSSCs) 1. DSSC is a kind of inorganic solar cell which contains
titanium dioxide (TiO2) as working electrode, organic dye as initiator, platinum as
counter electrode and I3-/KI as electrolyte. The most important part in DSSC is TiO2
working electrode. TiO2 is a widely used semiconductor in science and also our daily life.
It can be coated on standard steel surgery blade due to its self-sterilization property. 2,3
The clothes and glasses with TiO2 thin film has been commercialized because of its self-
cleaning property.4-8
TiO2 also has the ability to degrade the toxicity and organic
pollution in gas and water. 9-12
All of the applications of TiO2 mentioned above is due to
its unique photocatalytic activity. Firstly, TiO2 has a wide band gap which is 3.2eV. It
helps TiO2 to both absorb the energy from visible light and ultraviolet light. Secondly,
TiO2 can form some reactive oxygen species on the surface when it is irradiated by the
2
light. The reactive oxygen species can oxidize some of the organic wastes and remove
them from water and gases. 13-16
Photoelectrochemical cell is a similar kind of solar cell with dye-sensitized solar cells and
it is firstly invented by Michael Grätzel in 2001.17
Both of them are designed based on
TiO2 as the working electrode. Photoelectrochemical cell can interconvert chemicals and
electricity with the energy of light by the photovoltaic effect.
The advantages of photoelectrochemical cell comparing to dye-sensitized solar cell is that
it can oxidize and degrade the organic wastes and water pollutions while it is producing
energy under sunlight.17
It can tremendously reduce the pollutions and generate limitless
solar energy if it can be successfully commercialized.
The limitation of photoelectrochemical cell is the low conversion efficiency. It is mainly
due to the electrolyte and photocatalyst. Especially for photocatalyst such as TiO2, the
efficiency is limited by the slow electron transfer and fast electron-hole recombination. 18
In this thesis, the modification of TiO2 was done by exposing to hydrogen sulfide after
doping with platinum. The cover of electron generating site on TiO2 by sulfur can
facilitate the interfacial electron to electron acceptors and decrease the fast electron-hole
recombination by serving as electron sink.
3
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4
CHAPTER II
LITERATURE REVIEW
2.1. Photocatalysts
The photoelectric effect has attracted lots of scientists and industries since the French
scientist Edmond Becquerel discovered it in 1839.19
This breakthrough makes people
believe that the energy convention from sunlight to electricity is possible. Photovoltaics
have the advantages to generate the electricity by separating the electron-hole pair in
semiconductor under sunlight. Semiconductor plays the significant role in this circulation
to generate electricity. More and more work have be done to discover more efficient
semiconductor which can be used as photocatalyst and generate electricity more and
faster. The energy levels of some common semiconductors were shown in figure 2.17
A
good photocatalyst is not only a semiconductor, it also requires an appropriate band gap
and energy level. Titanium dioxide is a good semiconductor which has been widely used
for photocatalyst.20
2.2. Titanium dioxide
TiO2 has a wide distribution on earth. It has three different forms which are called rutile,
anatase and brookite, respectively. The different crystal structures of each form are shown
in figure 3. The different crystal structures result in the different band gap. Since the
5
photocatalytic activity is strongly depended on the band gap of semiconductor, each form
of TiO2 has quite different behavior. Anatase has the highest photocatalytic activity and
brookite has the lowest. A commercialized TiO2 is named P25, which is a mixture of 20%
rutile and 80% anatase. In some literatures, it has a better performance than pure anatase.
21, 22 It is explained that adding of rutile will break the ordered crystal structure of anatase
and slow down electron hole recombination.
Figure 2. Band positions of several semiconductors in contact with aqueous electrolyte at
pH 1.
6
Figure 3. Ball and stick model for three different forms of titanium dioxide.
Although TiO2 is a good photocatalyst in many fields, it is still far away from the
practical use in solar cells. The disadvantages of TiO2 are the slow electron transfer and
fast electron hole recombination. To develop a practical TiO2-based photocatalytic
process, majority of studies on TiO2 focused on either enhancing its photocatalytic
activity or extending its absorption spectrum from UV to the visible range by adding a
second element to the TiO2 bulk structure.23-25
Platinum doped titanium dioxide had been
studied that platinum was useful to increase the performance of TiO2.26
The mechanism
was (i) to increase the •OH and oxidized species generated on Pt and (ii) slow down the
electron-hole recombination by serving as an electron sink.27-30
Zhiqiang Yu from our group studied the effect of Pt on the photocatalytic degradation
pathway of methylene blue over TiO2 under ambient conditions. From figure 4, we can
Rutile
Band gap: 3.0 eV
Anatase
Band gap: 3.2 eV
Brookite
Band gap: 3.4 eV
Ti atoms are gray
O atoms are red
7
clearly see that the degradation rate of methylene blue was faster over 0.5 wt.% Pt-TiO2
than that over TiO2. 3 wt.% Pt-TiO2 decreased the degradation rate because too much
platinum had covered the surface of TiO2 and decreased the amount of high active •OH
group.
Figure 4. (a) Chemical structure of methylene blue and the IR band assignment. (b)
Variations of the IR intensity of MB bands at 1488 cm-1 during 240 min of the MB
photocatalytic degradation.
2.3. Photoelectrochemical cell
Ever since the concept of photoelectrochemical cell was proposed by Michael Grätzel in
2001, it had been a hot topic for many years. People were attracted by the idea of
generating hydrogen as fuel and decomposing organic wastes at the same time. A lot of
work has been done to make it commercialized. Dr. Panagiotis Lianos’s group studied the
effect of electrolyte to the cell performance and proposed the possible reactions during
the photoelectrochemical procedure. 31-33
Methylene blue
(MB)
(a) (b)
8
The efficiency of the photoelectrochemical cell can be obtained by the current-voltage
profile which is measured by ampere meter.
Figure 5. Current-voltage profile of the photoelectrochemical cell.
The calculation of the efficiency is based on the equation below:
where Jsc is short circuit current density, Voc is open circuit voltage, Pmax is maximum
power, Pin is power of UV light and η is efficiency of photoelectrochemical cell.
Table 1 showed that the higher concentration of NaOH and H2SO4 could increase the
open circuit voltage (Voc) and short circuit current density (Jsc)31
. These two values were
directly related to the performance of the photoelectrochemical cell. Higher the Voc and
Jsc, the efficiency of the cell was higher. It was explained that the difference of pH value
between two electrolytes applied a chemical bias to the system and increased the
performance. The relationship between pH value and chemical bias could be expressed
by the equation:
∆V=0.059 ∆pH
9
where ∆V is the chemical bias and ∆pH is the difference of pH value.
Table 1. Cell current-voltage characteristics for various electrolyte compositions under
UVA (Black light) illumination.
Table 1 also showed that adding of ethanol to the base electrolyte had significantly
enhanced the performance of the photoelectrochemical cell. The author studied the
different contents of ethanol affected the efficiency of the cell. From table 2, we could see
1% of ethanol had already enhanced the performance 7 times. When the ethanol content
reached 20%, the maximum performance was obtained.
Table 2. Cell current-voltage characteristics under UVA (Black Light) illumination for
various ethanol contents.
The enhancement of performance by adding ethanol was explained by the reactions taken
place during the photoelectrochemical procedure. Reaction 1 showed that the TiO2 could
generate electron -hole pair under the UV light. The hole could oxidize water in reaction
10
2 or it could oxidize ethanol to carbon dioxide in reactions 3-5. However, the oxidized
potential for ethanol was much lower than that of water, so ethanol was preferred to be
oxidized first. The low oxidized potential resulted in the higher efficiency.32
The author also studied several kinds of organic waste which could be decomposed
during the photoelectrochemical reactions. The results were shown in table 3. We can see
that most of the organic wastes had enhanced the performance of the
photoelectrochemical cell compared to pure water. 34
Short circuit current density is the most important parameter to determine the
performance of the photoelectrochemical cell. Some results from the literature were listed
in table 4. Comparison between the literature results and my results will be discussed in
Chapter IV.
After achieving the goal to decompose the organic wastes and generate the hydrogen for
fuel, the main question was raised. How to further modify the photoelectrochemical cell
to get good enough performance for our daily life? This is what I try to solve in this
thesis.
(1)
(2)
(3)
(4)
(5)
(6)
11
Table 3. Cell current–voltage characteristics under UVA (Black Light) illumination for
various reactants in the anode compartment.
Table 4. Literature results of the performance of photoelectrochemical cell.
No. Working electrode Working electrolyte Jsc
(mA/cm2)
Literature
1 Nanocrystalline TiO2
film 0.2 M NaOH/ 20% EtOH 0.79 31
2 Nanocrystalline TiO2
film 1.0 M NaOH/ 20% EtOH 0.89 32
3 Nanocrystalline TiO2
film
1.0 M NaOH/
20% Glycerol 1.12 33
4 Titania nanotube 1 M KOH 0.112 34
5 Nanocrystalline TiO2
film Not memtioned 0.55 35
12
CHAPTER III
EXPERIMENTAL
3.1. Preparation and characterization of platinum doped titanium dioxide and platinum
doped titanium dioxide treated by hydrogen sulfide
Platinum doped titanium dioxide (Pt-TiO2) and platinum doped titanium dioxide treated
by hydrogen sulfide (Pt-TiO2/H2S) were prepared by photo deposition. Titanium dioxide
(TiO2) was used as a control sample. Catalysts were characterized by Fourier transform
infrared spectroscopy (FTIR), 2D wide angle X-ray diffraction (WAXD), UV-Vis
spectroscopy, transmission electron microscopy (TEM), scanning electron microscope
(SEM) and energy-dispersive X-ray spectroscopy (EDS).
3.1.1. Preparation of platinum doped titanium dioxide
Platinum doped titanium dioxide (Pt-TiO2) was prepared by photo deposition method in
figure 6.18
0.5g titanium dioxide (P25, Degussa) and 66.6mg/133.3mg/399.9mg
chloroplatinic acid hexahydrate(IV) (99.9%, Alfa-Aesar) were added to the mixture of
28g deionized water and 2g ethanol (100%, Decon Labs, Inc.) in a quartz tube. The air in
the solution was removed by flowing the argon gas (Industrial Grade, Praxair) for ten
minutes. The tube was sealed well and stirred vigorously when it was exposed to UV-
visible light (Newsport, 350W Mercury lamp) for three hours. The solid was separated
from the solution by centrifuge and washed by DI water for three times. The solid was
dried in the oven at 300 0C for one hour and grounded to small powder. More platinum
13
was doped, the color was darker for the three samples. Products made by 66.6mg/
133.3mg/ 399.9mg chloroplatinic acid hexahydrate(IV) were marked as 0.5 wt.% Pt-
TiO2/ 1.0 wt.% Pt-TiO2/ 3.0 wt.% Pt-TiO2, respectively.
Figure 6. Experimental procedure of Pt-TiO2 preparation
3.1.2. Preparation of platinum doped titanium dioxide treated by hydrogen sulfide
0.5 wt.% Pt-TiO2 was used to prepare platinum doped titanium dioxide treated by
hydrogen sulfide (Pt-TiO2/H2S). 0.5 wt.% Pt-TiO2 was put in a quartz tube and heated at
450 0C for three hours in the hydrogen sulfide flow. The flow rate for hydrogen sulfide
was 10mL/min. After that, the solid was taken out and grounded to small powder (0.5
wt.% Pt-TiO2/H2S, figure 7).
14
Figure 7. Experimental procedure of Pt-TiO2/H2S preparation
3.1.3. Preparation of TiO2 thin film, Pt-TiO2 thin film and Pt-TiO2/H2S thin film
0.27g Polyethylene glycol (MW=20,000) and 1.8 mL deionized water were added into
the vial and mixed with hand. After all the PEG was dissolved, 0.9g TiO2/ Pt-TiO2/ Pt-
TiO2/H2S was added. Sonicator was applied to make them mix well. After adding 0.03
mL Triton X-100 (Laboratory grade, Sigma-Aldrich) and 0.06 mL acetylacetone (>99%,
Sigma-Aldrich), solution was sonicated for 30 min and stirred by magnetic bar for 2 days.
(Figure 8)
Figure 8. Experimental procedure of TiO2 paste preparation
15
Fluorine doped tin oxide coated glass slide (~7 Ω/sq, Sigma-Aldrich) was cut into
5cm*3.3cm and sonicated in water and ethanol three times alternatively. The pastes were
coated on the FTO glass by tape casting with a certain size (1cm*1cm). The thin films
were kept at room temperature for 30 min and sintered at both 150 0C and 450
0C for 30
min. (Increasing rate: 50/min). (Figure 9)
Figure 9. Experimental procedure of TiO2 thin film preparation
16
3.1.4 Characterization of catalysts in forms of powder and thin film
The morphology of the TiO2/ Pt-TiO2/ Pt-TiO2/H2S powders were characterized by TEM
(T12T/STEM, Tecnai) and the thin films were characterized by SEM (TM3030, Hitachi).
The samples of TEM were prepared by dipping a drop of catalysts mixed in DI water to a
carbon coated copper grids (SPI, 200 meshes). The thin films were characterized by SEM
without any further treatments. The absorption light and energy band gap of catalysts
were measured by UV-visible spectroscopy (U-3900, Hitachi). Fourier transform infrared
spectroscopy (Nicolet iS50R, Thermo scientific) was applied to detect the change of the
functional groups in catalysts. The catalysts were put in a diffuse reflectance infrared
Fourier transform spectroscopy (DRIFTS) cell (Figure 10). Two-dimensional wide angle
X-ray diffraction (2D WAXD) experiments were conducted on a Rigakua 18 kW rotating
anode X-ray generator using Cu Ka radiation (0.1542 nm) in transmission mode. The
attached detector was an R-AXIS-IV image plate system. The exposure time to obtain
high-quality patterns was 15 min. The peak positions were calibrated using silicon
crystals. Background scattering was subtracted from the sample pattern. 2D pattern was
integrated into one dimensional powder pattern. EDS was used to characterize the
distribution of elements in the TiO2-based catalysts.
17
Figure 10. Schematic (Left) and picture (Right) of DRIFT cell.
3.2. Setup of photoelectrochemical cell
The photoelectrochemical cell is a two component cell separated by a Nafion membrane
(0.180mm thick, ≥0.90 meq/g exchange capacity, Alfa Aesar) as shown in figure 11. The
top part has two gas ports which can allow the carrier gas to take out all the gas products
generated during the experiments. Platinum foil was used as a cathode which is also
known as counter electrode. The solution in top part is 0.1 mol/L sulfuric acid. Two pH
meters in both sides can monitor the pH change during the experiments. In the bottom
part, there are also two gas ports which allow us to take the gas products by syringe and
tested them in mass spectroscopy. FTO glass with catalysts coated on it was used as
anode which is also called working electrode. The solution in bottom part is 0.1 mol/L
sodium hydroxide water solution with 20 wt.% ethanol and 0.1 wt.% methylene blue
(≥82%, Sigma-Aldrich). The anode and cathode were connected by a galvanometer and a
power supply which can adjust the output voltage. The galvanometer was connected to a
computer which can record the change of current and voltage during the experiments.
The intensity of UV light was measured by photodiode sensor (818-UV/DB, Newport).
Sample
18
Figure 11. (a) Schematic setup and (b) pictures of photoelectrochemical cell
(b)
(a)
19
3.3. Characterization of gas products and solution in photoelectrochemical cell
The gas products generated during the experiments in photoelectrochemical cell were
characterized by mass spectroscopy (MS, Balzers QMG 112). The mass/charge responses
(i.e., m/z = 2, 28, 32 and 44 from H2, CO or N2, O2 and CO2) were analyzed to determine
the amount of the produced gases. Scotty gas (analytical standard, Supelco) was used to
calibrate the MS for H2 and CO2.
The oxidation rate of solution was monitored by UV-visible spectroscopy (Hitachi U-
3900). Methylene blue shows two peaks at 278.5 nm and 597.1 nm and the height was
proportional to the amount of methylene blue in the solution.
3.4. Experimental procedure of photoelectrochemical cell
Two experimental procedures were applied in this thesis. The first one focused on the
electrical measurement and gas products analysis. (Figure 12). The experiment was
started by applying a zero voltage power supply. The UV light was turned on at the
second minute. After waiting for 5 min, UV light was turned off. Increase the power
supply to 0.5 V and start to push the internal gas to MS by argon. After pushing for 3 min,
put the system into batch and turn on the UV light. Wait for another 5 min, turn off the
UV light and increase the voltage to 1.0V. Open the flow gas and push the gas products to
MS for analysis. After all the experiment, decrease the voltage to 0V again and stop the
measuring. The current and voltage were kept monitoring during the whole experiment.
Two pH values were also recorded.
The second experimental procedure focused on the pH change during the experiments. It
was designed with short time period and higher power supply voltage. It was shown in
figure 13.
20
Adjust the voltage to 0 V and
remove the air by argon
Wait for 2 min and put the system
into batch
Turn on UV light and wait for 15
min
Turn off UV light, open the gas flow
and carry the gas products to MS.
Increase the voltage to 0.5 V
Turn on UV light and wait for 15
min
Turn off UV light, open the gas flow
and carry the gas products to MS.
Increase the voltage to 1.0 V
Turn on UV light and wait for 15
min
Turn off UV light, open the gas flow
and carry the gas products to MS.
Decrease the voltage to 0 V
Wait for 2 min and stop the program
Figure 12. First experimental procedure of photoelectrochemical cell.
21
Adjust the voltage to 0V and remove the air by argon
Wait for 2 min and put the system into batch
Turn on UV light and wait for 3 min
Turn off UV light, open the gas flow and carry the gas products
to MS. Increase the voltage to 0.5 V.
Turn on UV light and wait for 3 min
Turn off UV light, open the gas flow and carry the gas products
to MS. Increase the voltage to 1.0 V.
Turn on UV light and wait for 3 min
Turn off UV light, open the gas flow and carry the gas products
to MS. Increase the voltage to 1.5 V.
Turn on UV light and wait for 3 min
Turn off UV light, open the gas flow and carry the gas products
to MS. Increase the voltage to 2.0 V.
Turn on UV light and wait for 3 min
Turn off UV light, open the gas flow and carry the gas products
to MS. Decrease the voltage to 0 V.
Wait for 2 min and stop the program.
Figure 13. Second experimental procedure of photoelectrochemical cell.
22
CHAPTER IV
RESULTS AND DISCUSSION
4.1. Characterization of TiO2-based catalysts
The characterizations of TiO2-based catalysts were both done in powder and thin film
format by IR, UV-vis, TEM and so on.
4.1.1 TiO2-based catalysts in powder and thin film form
The darkness of the color for TiO2, 0.5 wt.% Pt-TiO2, 1.0 wt.% Pt-TiO2, 3.0 wt.% Pt-TiO2
and , 0.5 wt.% Pt-TiO2/H2S increased step by step in figure 14. It shows that the doping
platinum was uniformly attached to TiO2 and the doping rate increased with the increase
amount of H4PtCl6. The color of 0.5 wt.% Pt-TiO2/H2S was darker than 0.5 wt.% Pt-TiO2
even 3.0 wt.% Pt-TiO2. It means that hydrogen sulfide treatment had some certain effect
to change the morphology of Pt-TiO2.
Figure 14. Photograph of TiO2, 0.5 wt.% Pt-TiO2, 1.0 wt.% Pt-TiO2, 3.0 wt.% Pt-TiO2
and 0.5 wt.% Pt-TiO2/H2S powder.
23
The thin film of TiO2, 0.5 wt.% Pt-TiO2 and 0.5 wt.% Pt-TiO2/H2S was shown in figure
15. The color also changed from white to dark grey. The high temperature calcine could
not change the color to white, which meant that the doping platinum and sulfur were not
removed in high temperature.
Figure 15. Photograph of TiO2, 0.5 wt.% Pt-TiO2, 1.0 wt.% Pt-TiO2, 3.0 wt.% Pt-TiO2
and 0.5 wt.% Pt-TiO2/H2S thin film.
4.1.2 TEM analysis of TiO2-based catalyst in powder form
The TEM picture of TiO2 in figure 16 showed the size of TiO2 was around 15~30 nm,
which matched the reported size in literature. 19
Platinum particles could be found in 0.5
wt.% Pt-TiO2 ,1.0 wt.% Pt-TiO2, 3.0 wt.% Pt-TiO2 and 0.5 wt.% Pt-TiO2/H2S. The size of
platinum is around 3~5nm. It further confirmed that platinum was successfully doped
into TiO2. Sulfur was not seen from the TEM pictures because sulfur was too small to
see.
TiO2
0.5 wt.%
Pt-TiO2
0.5 wt.% Pt-
TiO2/H
2S
24
Figure 16. TEM pictures of TiO2, 0.5 wt.% Pt-TiO2 ,1.0 wt.% Pt-TiO2, 3.0 wt.% Pt-TiO2
and 0.5 wt.% Pt-TiO2/H2S.
25
4.1.3 SEM analysis of TiO2-based catalysts in thin film form
The top view SEM pictures in figure 17 showed that TiO2 was much less porous than Pt-
TiO2 and Pt-TiO2/H2S. Hydrogen sulfide treatment increased the size of aggregates and
generated lager holes. The cross sectional view SEM pictures could show the thickness of
each thin film. From figure 17, the thickness of TiO2 was 22µm, which was much larger
than Pt-TiO2 and Pt-TiO2/H2S. The optimal thickness for photocatalyst was between 10 to
20 µm20
. The efficiency of Pt-TiO2/H2S was assumed to be significantly reduced by the
small thickness.
Figure 17. SEM pictures of TiO2, 0.5 wt.% Pt-TiO2 and 0.5 wt.% Pt-TiO2/H2S in thin
film from top and cross sectional views.
4.1.4 FTIR spectroscopy characterization of TiO2-based catalysts
The FTIR spectra of TiO2, Pt-TiO2 and Pt-TiO2/H2S in powder form were compared in
figure 18. The difference was the peaks at 3677 cm-1
, 3650 cm-1
and 3629 cm-1
increased
in Pt-TiO2 and Pt-TiO2/H2S compared to those in TiO2. These three peaks were assigned
26
to hydroxyl group attached to catalysts in three different ways. The hydroxyl groups can
interact with water or organics in the electrolyte and increase the rate of reaction. The
more the hydroxyl group, the photocatalytic activity was higher.
27
4000 3500 1500 10000.0
0.5
1.0
1.5
Pt-TiO2/H
2S
Pt-TiO2
Sin
gle
bea
m i
nte
nsi
ty (
a.u
.)
Wavenumber (cm-1)
TiO2
3650
3629
3677
3414
H2 O
(a)
28
Figure 18. (a) Single beam and (b) absorbance FTIR spectra of TiO2, 0.5 wt.% Pt-TiO2
and 0.5 wt.% Pt-TiO2/H2S in powder form. Absorbance was obtained by absorbance
=log(1/I), where I was the intensity of single beam.
The FTIR spectra of TiO2, Pt-TiO2 and Pt-TiO2/H2S in thin film form were also compared
in figure 19. Same with the powder, three peaks at 3677 cm-1
, 3650 cm-1
and 3629 cm-1
also increased in Pt-TiO2 and Pt-TiO2/H2S compared to those in TiO2. The assignment
was still the same. The only difference was the peak at 3711 cm-1
, which significantly
decreased in Pt-TiO2 and Pt-TiO2/H2S. The band at 3711 cm-1
was assigned to the free
hydroxyl group. More free hydroxyl group in TiO2 showed that the assembly of hydroxyl
group in TiO2 was better.
4000 3500 1500 10000
2
4
Pt-TiO2/H
2S
Pt-TiO2
Abso
rban
ce (
a.u
.)
Wavenumber (cm-1)
TiO2
3650
3629
3677
3414
H2 O
(b)
29
Figure 19. (a) Single beam and (b) absorbance FTIR spectra of TiO2, 0.5 wt.% Pt-TiO2
and 0.5 wt.% Pt-TiO2/H2S in thin film form. Absorbance was obtained by absorbance
=log(1/I), where I was the intensity of single beam.
4000 3500 1500 10000.0
0.5
1.0
1.5 3711
Pt-TiO2/H
2S
Pt-TiO2
Sin
gle
beam
inte
nsit
y (a
.u.)
Wavenumber (cm-1)
TiO2
3650
3629
3677
3414
H2 O
O
4000 3500 1500 10000.0
0.5
1.0
1.5
2.0 3711
Pt-TiO2/H
2S
Pt-TiO2
TiO2
Sin
gle
bea
m i
nte
nsi
ty (
a.u
.)
Wavenumber (cm-1)
3650
3629
3677
3414
H2 O
(a)
(b)
30
4.1.5 UV-Vis spectroscopy characterization of TiO2-based catalysts
The UV-vis spectra of TiO2-based catalysts were shown in figure 20. The baseline of Pt-
TiO2 and Pt-TiO2/H2S were higher than TiO2 because dark color could absorb visible
light. The cutting off wavelength was shifted from 388nm for TiO2 to 434nm for Pt-TiO2
and 442nm for Pt-TiO2/H2S. It was exactly the same both in powder and thin film form.
Cutting off wavelength was a very useful valve which could calculate the band gap based
on it. The equation was shown below:
band gap= /h C 21 (7)
where h is Planks constant, 6.626× 10−34 Joules sec. C is the speed of light, 3.0 x 108
meter/sec, λ is the cut off wavelength.
Based on the equation 7, the band gap of three catalysts could be calculated and listed in
table 5.
200 300 400 500 600 700 8000.0
0.5
1.0
1.5
2.0
Pt-TiO2/H
2S
Ab
sorb
ance
(a.
u.)
Wavelength (nm)
Pt-TiO2
TiO2
388 (TiO2)
434 (Pt-TiO2)
442 (Pt-TiO2/H
2S)
(a)
31
200 300 400 500 600 700 8000.0
0.5
1.0
Ab
sorb
ance
(a.
u.)
Wavelength (nm)
Pt-TiO2/H
2S
Pt-TiO2
TiO2
Figure 20. UV-vis spectroscopy of TiO2, 0.5 wt.% Pt-TiO2 and 0.5 wt.% Pt-TiO2/H2S in
(a) powder and (b) thin film form.
Table 5. Cutting off wavelength and band gap of TiO2-based catalysts.
TiO2 Pt-TiO2 Pt-TiO2/H2S
Cutting off wavelength 388 nm 434 nm 442 nm
Band gap 3.2 eV 2.9 eV 2.8 eV
The band gap decreased from 3.2 eV to 2.9 eV for Pt-TiO2 and 2.8 eV for Pt-TiO2/H2S.
The small band gap indicated that it would be easier to generate electron-hole pair and
slow down the recombination. The efficiency of Pt-TiO2/H2S was assumed to be the best
based on the small band gap.
(b)
32
4.1.6 Two-dimensional wide angle X-ray diffraction spectroscopy of TiO2-based
catalysts.
The XRD patterns of the three TiO2-based catalysts in powder form were shown in figure
21. All of them have the peaks of anatase and rutile, which matched the peaks in P25.
There were not many differences between these three samples. It indicated that the
neither of platinum doping and hydrogen sulfide treatment affected the crystal structure
of TiO2. The peak of platinum around 400 was hardly to see which meant the amount of
platinum was very little.
15 20 25 30 35 40 45
R
AR
A
R
2
Co
un
ts (
a.u
.)
Pt-TiO2/H
2S
Pt-TiO2
TiO2
Pt (111)
Figure 21. XRD spectroscopy of TiO2-based catalysts in powder form.
33
4.1.7 Energy-dispersive X-ray spectroscopy of TiO2-based catalysts
EDS was used to characterize the distribution of element in the TiO2-based catalysts in
thin film form. The results were listed in table 6.
The atomic percentage of Ti to O was around 1:2 in all the catalysts, which matched the
composition of TiO2. 0.1% platinum in Pt-TiO2 shows the platinum doping had
successfully introduced platinum into TiO2. Pt-TiO2/H2S has 0.26% sulfur which was
almost the same with platinum. It indicated that sulfur atoms were enough to cover all the
platinum atoms.
Table 6. Atomic percentage of Ti, O, Pt and S in thin film TiO2, 0.5 wt.% Pt-TiO2 and 0.5
wt.% Pt-TiO2/H2S.
Atom %
Ti O Pt S
TiO2 30.89 69.11 0 0
Pt-TiO2 35.02 64.87 0.1 0
Pt-TiO2/H2S 34.55 64.99 0.2 0.26
4.2. Results of photoelectrochemical cell
The results of photoelectrochemical cell were obtained by the voltammetry, pH meter and
MS results.
4.2.1 Photoelectrochemical reactions
The setup of photoelectrochemical cell had been talked about in the experimental part.
The reactions might happen during the experiment were shown in figure 22. When TiO2
were exposed to UV light, electron-hole pairs were generated inside TiO2. Electrons
34
would go through the out circuit and reduced the proton to hydrogen gas. Holes would
diffuse to the surface of TiO2 and oxide the organics such as the ethanol and methylene
blue to carbon dioxide. During the whole experimental process, hydrogen was generated
and organic wastes were decomposed.
h+
e-
Conduction band
Ec= -0.2V
Valance band
Ev= 3.0V
UV lightH2O
EtOH
e-
CO2
H2
Working
electrodeElectrolyte
Counter
electrode
3.2 V
Figure 22. Schematic representation of the operating principle and reactions of
photoelectrochemical cell.
4.2.2 Electrical experimental results of photoelectrochemical cell
All the catalysts of Pt-TiO2 and Pt-TiO2/H2S were referred to 0.5 wt.% Pt-TiO2 and 0.5
wt.% Pt-TiO2/H2S. First experimental procedure was used to collect the data below.
Figure 23 showed the results of current density collected during the experiment. Once the
V light was turned on, the current density suddenly increased from 0 mW/cm2 to around
0.5 mW/cm2. This result indicated that the UV light had a significant effect on the current
density of photoelectrochemical cell. This phenomenon was repeaand reproducible.
When the power supply provided 0V to the system, Pt-TiO2 has the highest current
35
density. Pt-TiO2/H2S was almost the same with TiO2. When the voltage increased to 0.5V,
Pt-TiO2 was still the highest. TiO2 was higher than Pt-TiO2/H2S at 0.5V. After the voltage
was increased to 1.0V, TiO2 has the highest current density. The results showed that Pt-
TiO2 has a better efficiency at low voltage than TiO2. It matched the literature results.18
At high voltage, hydrolysis played an important role in the reactions and the better
arrangement of TiO2 leaded to a higher performance. Pt-TiO2/H2S was not as good as the
other two catalysts due to the much thinner thickness. The effect of thickness was more
important than the performance of catalyst itself.
H2 and CO2 were all detected by MS during the experiment in figure 24. The areas of the
peaks were intergraded and the value was proportional to the amount of gases. The
amount of H2 increased with the increase of power supply voltage. However, the amount
of CO2 decreased with the increase of power supply voltage. It could be explained by that
hydrolysis dominated the reactions in the high voltage. If the hydrolysis was more than
photocatalytic reaction, ethanol was less reacted and less CO2 was produced. In the
opposite, H2 could always be produced either by hydrolysis and photocatalytic reaction. It
could also be proved by the pictures in figure 25. More CO2 bulb was formed at the lower
power supply voltage with the same TiO2-based catalyst. When the voltage was 0V, Pt-
TiO2/H2S produced most CO2. CO2 bulb could not be seen with TiO2. This result strongly
indicated that platinum doped TiO2 had much better performance than TiO2 in
decomposing organics. Hydrogen sulfide treatment could further increase the
performance.
36
0 10 20 30 40 50 60
0.0
0.5
1.0
1.5
UV
on
UV
off
UV
off
UV
on
UV
off
UV
on
TiO2
Pt-TiO2
Pt-TiO2/H
2S
Cu
rren
t d
en
sit
y (
mW
/cm
2)
Time (min)
1.0 V
0.5 V
0.0 V
Figure 23. Time profiles of current density at different forward bias voltage for TiO2, 0.5
wt.% Pt-TiO2 and 0.5 wt.% TiO2/H2S as working electrode.
37
4.2.3 Gas production results of photoelectrochemical cell experiment.
0 10 20 30 40 50 60
1.0 V0.5 V
H2
CO2
CO2
H2
0 V
H2
CO2
TiO2
Pt-TiO2
Pt-TiO2/H
2S
Ion
in
ten
sity
(a.
u.)
Time (min)
8.88E-13 1.14E-12 1.57E-12
7.71E-13 8.33E-13 1.24E-12
1.53E-12 1.85E-12
7.54E-13 6.65E-13 5.12E-13
8.47E-13 6.56E-13 4.90E-13
3.43E-13 3.15E-13
Figure 24. Time profiles of MS intensity at different forward bias voltage for TiO2, 0.5
wt.% Pt-TiO2 and 0.5 wt.% TiO2/H2S as working electrode. H2 and CO2 were detected
from the gas products.
Figure 25. Pictures of the CO2 blub formation during the experiment.
38
All the data of the photoelectrochemical cell experiment were organized in table 7. The
reaction produced similar hydrogen with TiO2 and Pt-TiO2/H2S. As we mentioned above,
the thickness of Pt-TiO2/H2S was much less than that of TiO2. If the thickness of Pt-
TiO2/H2S could be similar to TiO2, the hydrogen production of Pt-TiO2/H2S must be
much more than the other catalysts. More experiment would be done to verify this
conclusion. On the other hand, Pt-TiO2 and Pt-TiO2/H2S produced significant more CO2
than TiO2 which further confirmed the platinum doped TiO2 has better performance in
degradation of organic wastes. Considering the effect of thickness, Pt-TiO2/H2S was
supposed to be the best catalyst in hydrogen production and organic decomposing.
Table 7. Hydrogen and carbon dioxide production at different forward bias for TiO2, 0.5
wt.% Pt-TiO2 and 0.5 wt.% TiO2/H2S as catalysts.
39
Table 8. Comparison with the results in literature of the cell performance.
No
.
Working
electrode
Working
electrolyte
Jsc
(mA/cm2)
Current density
under 0.5V
forward bias
(mA/cm2)
Literat
ure
1 Nanocrystalline
TiO2 film
0.2 M NaOH/
20%EtOH 0.79 0.8 31
2 Nanocrystalline
TiO2 film
1.0 M NaOH/
20% EtOH 0.89 0.91 32
3 Nanocrystalline
TiO2 film
1.0 M NaOH/
20% Glycerol 1.12 - 33
4 Titania nanotube 1 M KOH 0.112 - 34
5 Nanocrystalline
TiO2 film Not mentioned 0.55 - 35
6 Nanocrystalline
TiO2 film
1.0 M NaOH/
20% EtOH 0.41 0.89
This
work
7 Nanocrystalline
Pt-TiO2 film
1.0 M NaOH/
20% EtOH 0.51 1.16
This
work
8 Nanocrystalline
Pt-TiO2/H2S film
1.0 M NaOH/
20% EtOH 0.38 0.64
This
work
From the comparison between the results of literature and my work in table 8, we can see
that the Jsc of my photoelectrochemical cell were lower than Dr. Lianos’s work.
However, the current density under 0.5V forward bias of my cell was higher than the
literature results. It indicated that my cell could work better under 0.5V forward bias.
4.2.4 Photo oxidation of methylene blue in the photoelectrochemical cell experiment
Methylene blue is a very excellent pigment in industry and academic. It is widely used as
an indicator in biology and chemistry to represent the organic wastes. In this
photoelectrochemical cell experiment, methylene blue was used to monitor the organic
degradation during the process. Figure 26 showed that all of the three solutions with
TiO2, Pt-TiO2 and Pt-TiO2/H2S have decomposed more or less methylene blue after the
reactions. For further observation, Pt-TiO2 decomposed the most methylene blue and the
color of the solution was lightest.
40
Figure 26. Photograph of electrolyte containing methylene blue (a) before and after
degradation by (b) TiO2, (c) 0.5 wt.% Pt-TiO2 and (d) 0.5 wt.% TiO2/H2S.
In order to get a more reliable and quantified results, UV-vis spectroscopy was used to
characterize the amount of residual methylene blue in the solutions. Figure 27 showed
that all of the methylene blue solutions had two peaks, which were located at 278.5nm
and 597.1nm. It was confirmed by the literature results.22, 23
200 300 400 500 600 700 8000.0
0.5
1.0
597.1278.5
Abso
rban
ce (
a.u
.)
Wavelength (nm)
Before degradation
After degradation by TiO2
After degradation by Pt-TiO2
After degradation by Pt-TiO2/H
2S
(b) (a) (c) (d)
41
Figure 27. UV-visible spectroscopy of electrolyte containing methylene blue before and
after degradation by TiO2, 0.5 wt.% Pt-TiO2 and 0.5 wt.% TiO2/H2S.
By comparing the peak height at 278.5 nm and 597.1 nm of all samples, the results were
obtained in table 9. The percentage of degradation of methylene blue showed that Pt-TiO2
had the best performance to decompose the methylene blue. This result matched the color
change in figure 26. Pt-TiO2/H2S had a much better performance than TiO2 even it has a
significantly less thickness. The conclusion could be drawn that the performance of
decomposing organic wastes was significantly increased by doping platinum to TiO2 in
photoelectrochemical cell.
Table 9. Results of the UV-visible spectroscopy of electrolyte containing methylene blue
before and after degradation by TiO2, 0.5 wt.% Pt-TiO2 and 0.5 wt.% TiO2/H2S.
278.5 nm 597.1 nm Average
Methylene blue
Peak
height
Degradation
percentage
Peak
height
Degradation
percentage
Degradation
percentage
Before degradation 0.265 0.00% 0.514 0.00% 0.00%
After degradation
by TiO2
0.194 26.79% 0.376 26.85% 26.82%
After degradation
by Pt-TiO2
0.098 63.02% 0.206 59.92% 61.47%
After degradation
by Pt-TiO2/H2S
0.142 46.42% 0.289 43.77% 45.09%
42
4.2.5 pH change
The second experimental procedure was used to collect the pH change during the
photoelectrochemical reactions. The two pH meters had kept monitoring the pH change
during the experiments. Figure 28 showed that the pH change of the acid electrolyte
strongly depended on the UV on and off. The pH increased once the UV light was turned
on and it decreased as soon as the UV light was turned off. The change of pH value was
similar to the change of current density. For the pH of base electrolyte, it didn’t change
much in the whole experiment.
The intensity of UV light also had a significant effect on the pH change. Figure 29
showed that pH didn’t change when the intensity of UV light was 10 mW/cm2. When the
intensity increased to 100 mW/cm2 and 1000 mW/cm
2, the pH increased once the UV
light was turned on. If the UV light was turned off, the pH decreased immediately. Both
the pH values in acid electrolyte and base electrolyte has the same trend. In addition, the
pH value had a larger increase or decrease with the larger intensity of UV light. The pH
value vibrated with the largest amplitude when the intensity of UV light was 1000
mW/cm2.
The mechanism of the pH change was still unknown. The future work will be done by
other students in this group.
43
0
2
4
0.8
0.9
0 5 10 15 20 25
12.3
12.4
UV
on
UV
on
UV
on
UV
on
UV
off
UV
off
UV
off
UV
off
UV
off
UV
on
2.0V1.5V
1.0V0.5V
Cu
rren
t d
ensi
ty
(m
A/c
m2)
0V
Base
Acid
Time (min)
pH
pH
Figure 28. The change of pH values and current density during the experiments.
44
0 5 10 15 20 251.30
1.35
1.40
1.45
1.50
1.55
1.60
2.0 V
1.5 V
1.0 V
0.5 V0.0 V
pH
Time (min)
1000 mW/cm2
100 mW/cm2
10 mW/cm2
0 5 10 15 20 2512.60
12.64
12.68
12.72
12.76
12.80
pH
Time (min)
2.0 V1.5 V1.0 V0.5 V0.0 V
Figure 29. Effect of different UV light intensity on the pH change.
45
4.3. Conclusions
Pt-TiO2 and Pt-TiO2/H2S has been successfully synthesized by photo deposition and
thermal deposition methods. A series of characterization have been done to confirm the
crystal structures and the distribution of elements. Two experiments of
photoelectrochemical cell were done to compare the photocatalytic activity of TiO2, Pt-
TiO2 and Pt-TiO2/H2S. Pt-TiO2 has a good performance both in hydrogen production and
organic wastes decomposition. Pt-TiO2/H2S is good at decomposing organic wastes but
worse than TiO2 in hydrogen production. It is likely due to the small thickness of thin
film. More experiments will be done to prove the effect of thickness to the cell
performance.
46
REFERENCES
1. O’regan, B.; Grätzel, M. A low-cost, high-efficiency solar cell based on dye-
sensitized. nature 1991, 353, 24.
2. Chung, C.-J.; Lin, H.-I.; Tsou, H.-K.; Shi, Z.-Y.; He, J.-L. An antimicrobial TiO2
coating for reducing hospital-acquired infection. Journal of Biomedical Materials
Research Part B: Applied Biomaterials 2008, 85B, 220-224.
3. Yu, J. C.; Ho, W.; Lin, J.; Yip, H.; Wong, P. K. Photocatalytic Activity,
Antibacterial Effect, and Photoinduced Hydrophilicity of TiO2 Films Coated on a
Stainless Steel Substrate. Environmental Science & Technology 2003, 37, 2296-
2301.
4. Paz, Y.; Luo, Z.; Rabenberg, L.; Heller, A. Photooxidative self-cleaning
transparent titanium dioxide films on glass. Journal of Materials Research 1995,
10, 2842-2848.
5. Miyauchi, M.; Nakajima, A.; Fujishima, A.; Hashimoto, K.; Watanabe, T.
Photoinduced Surface Reactions on TiO2 and SrTiO3 Films: Photocatalytic
Oxidation and Photoinduced Hydrophilicity. Chemistry of Materials 2000, 12, 3-5.
6. Miyashita, K.; Kuroda, S.; Ubukata, T.; Ozawa, T.; Kubota, H. Enhanced effect of
vacuum-deposited SiO2 overlayer on photo-induced hydrophilicity of TiO2 film.
Journal of Materials Science 2001, 36, 3877-3884.
7. Uddin, M. J.; Cesano, F.; Scarano, D.; Bonino, F.; Agostini, G.; Spoto, G.;
Bordiga, S.; Zecchina, A. Cotton textile fibers coated by Au/TiO2 films: Synthesis,
characterization and self-cleaning properties. Journal of Photochemistry and
Photobiology A: Chemistry 2008, 199, 64-72.
8. Wu, D.; Long, M. Enhancing visible-light activity of the self-cleaning TiO2-
coated cotton fabrics by loading AgI particles. Surface and Coatings Technology
2011, 206, 1175-1179.
9. Vorontsov, A. V.; Savinov, E. V.; Davydov, L.; Smirniotis, P. G. Photocatalytic
destruction of gaseous diethyl sulfide over TiO2. Applied Catalysis B:
Environmental 2001, 32, 11-24.
47
10. Vorontsov, A. V.; Savinov, E. N.; Lion, C.; Smirniotis, P. G. TiO2 reactivation in
photocatalytic destruction of gaseous diethyl sulfide in a coil reactor. Applied
Catalysis B: Environmental 2003, 44, 25-40.
11. Li, X. Z.; Li, F. B. Study of Au/Au3+-TiO2 Photocatalysts toward Visible
Photooxidation for Water and Wastewater Treatment. Environmental Science &
Technology 2001, 35, 2381-2387.
12. Ryu, J.; Choi, W. Substrate-Specific Photocatalytic Activities of TiO2 and
Multiactivity Test for Water Treatment Application. Environmental Science &
Technology 2007, 42, 294-300.
13. Carraway, E. R.; Hoffman, A. J.; Hoffmann, M. R. Photocatalytic Oxidation of
Organic Acids on Quantum-Sized Semiconductor Colloids. Environmental
Science & Technology 1994, 28, 786-793.
14. Hoffmann, M. R.; Martin, S. T.; Choi, W.; Bahnemann, D. W. Environmental
Applications of Semiconductor Photocatalysis. Chemical Reviews 1995, 95, 69-96.
15. Kormann, C.; Bahnemann, D. W.; Hoffmann, M. R. Photocatalytic production of
hydrogen peroxides and organic peroxides in aqueous suspensions of titanium
dioxide, zinc oxide, and desert sand. Environmental Science & Technology 1988,
22, 798-806.
16. Hoffman, A. J.; Carraway, E. R.; Hoffmann, M. R. Photocatalytic Production of
H2O2 and Organic Peroxides on Quantum-Sized Semiconductor Colloids.
Environmental Science & Technology 1994, 28, 776-785.
17. Grätzel, M. Photoelectrochemical cells. Nature 2001, 414, 338-344.
18. Yu, Z.; Chuang, S. S. The effect of Pt on the photocatalytic degradation pathway
of methylene blue over TiO2 under ambient conditions. Applied Catalysis B:
Environmental 2008, 83, 277-285.
19. Bequerel, E. Recherches sur les effets de la radiation chimique de la lumière
solaire, au moyen descourants électriques. C.R. Acad. Sci. 1839, 9, 145–149.
20. Fujishima. A.; Honda, K. Electrochemical photolysis of water at a semiconductor
electrode. Nature 1972, 238, 37–38.
21. Hurum, D. C.; Agrios, A. G.; Gray, K. A. Explaining the Enhanced Photocatalytic
Activity of Degussa P25 Mixed-Phase TiO2 Using EPR J. Phys. Chem. B 2003,
107, 4545-4549
48
22. Kanna, M.; Wongnawa, S. Mixed amorphous and nanocrystalline TiO2 powders
prepared by sol–gel method: Characterization and photocatalytic study Mater.
Chem. Phys. 2008, 110, 166-175.
23. Zhao, W.; Ma, W.; Chen, C.; Zhao, J.; Shuai, Z. Efficient Degradation of Toxic
Organic Pollutants with Ni2O3/TiO2-xBx under Visible Irradiation J. Am. Chem.
Soc 2004, 126 , 4782–4783.
24. Lee, J.; Choi, W.; Photocatalytic Reactivity of Surface Platinized TiO2: Substrate
Specificity and the Effect of Pt Oxidation State J. Phys. Chem. B 2005, 109,
7399–7406.
25. Asahi, R.; Morikawa, T.; Ohwaki, T.; Aoki, L.; Taga, Y. Visible-Light
Photocatalysis in Nitrogen-Doped Titanium Oxides Science 2001, 293, 269–271.
26. Park, H.; Lee, J.; Choi, W. Study of special cases where the enhanced
photocatalytic activities of Pt/TiO2 vanish under low light intensity Catal. Today
2006, 111, 259–265.
27. Zhao, W.; Chen, C.; Li, X.; Zhao, J.; Hidaka, H.; Serpone, N. Photodegradation of
Sulforhodamine-B Dye in Platinized Titania Dispersions under Visible Light
Irradiation: Influence of Platinum as a Functional Co-catalyst J. Phys. Chem. B
2002, 106, 5022–5028.
28. Hwang, S.; Lee, M. C.; Choi, W. Highly enhanced photocatalytic oxidation of CO
on titania deposited with Pt nanoparticles: Kinetics and mechanism Appl. Catal. B
2003, 46, 49–63.
29. Kim, S.; Choi, W. Dual Photocatalytic Pathways of Trichloroacetate Degradation
on TiO2: Effects of Nanosized Platinum Deposits on Kinetics and Mechanism J.
Phys. Chem. B 2002, 106, 13311–13317.
30. Haick, W.; Paz, Y. Long-Range Effects of Noble Metals on the Photocatalytic
Properties of Titanium Dioxide J. Phys. Chem. B 2003, 107, 2319–2326.
31. Lianos, P. "Production of electricity and hydrogen by photocatalytic degradation
of organic wastes in a photoelectrochemical cell: the concept of the photofuelcell:
a review of a re-emerging research field." Journal of Hazardous Materials 2011,
185, 575-590.
32. Antoniadou, M.; Kondarides, D.; Lianos, P., Photooxidation Products of Ethanol
During Photoelectrochemical Operation Using a Nanocrystalline Titania Anode
and a Two Compartment Chemically Biased Cell. Catal. Lett. 2009, 129, 344-349.
49
33. Antoniadou, M.; Kondarides, D. Ι.; Labou, D.; Neophytides, S.; Lianos, P., An
efficient photoelectrochemical cell functioning in the presence of organic wastes.
Solar Energy Materials and Solar Cells 2010, 94 (3), 592-597.
34. Li, Y.; Yu, H.; Song, W.; Li, G.; Yi, B.; Shao, Z., A novel photoelectrochemical
cell with self-organized TiO2 nanotubes as photoanodes for hydrogen generation.
International Journal of Hydrogen Energy 2011, 36, 14374-14380.
35. Li, X.; Gao, C.; Duan, H.; Lu, B.; Pan, X.; Xie, E., Nanocrystalline TiO2 film
based photoelectrochemical cell as self-powered UV-photodetector. Nano Energy
2012, 1, 640-645.
36. Joseph, R.; Viswanathan, B. Effect of surface area, pore volume and particle size
of P25 titania on the phase transformation of anatase and rutile. Indian J. Chem.
2009, 48, 1378-1382.
37. Kang, M. G.; Ryu, K. S.; Chang, S. H.; Park, N.G.; Hong, J. S.; Kim, K. J.
Dependence of TiO2 Film Thickness on Photocurrent-Voltage Characteristics of
Dye-Sensitized Solar Cells Bull. Korean Chem. Soc. 2004, 25, 742-744.
38. H.H. Perkampus: Encyclopedia of Spectroscopy, VCH, Weinheim, New York,
Basel, Cambridge, Tokyo, ISBN 3-527-29281-0, 1995. Berichte der
Bunsengesellschaft für physikalische Chemie 1995, 99, 787-787.
39. Jockusch, S.; Turro, N. J.; Tomalia, D. A. Aggregation of Methylene Blue
Adsorbed on Starburst Dendrimers Macromolecules 1995, 28, 7416-7418.
40. Yan, M.; Zhang, M.; Gong, K.; Su, L.; Guo, Z.; Mao, L. Adsorption of Methylene
Blue Dye onto Carbon Nanotubes: A Route to an Electrochemically Functional
Nanostructure and Its Layer-by-Layer Assembled Nanocomposite Chem. Mater.
2005, 17, 3457-3463.
41. Longo, C.; Paoli, M.-A. D. Dye-sensitized solar cells: a successful combination of
materials J. Braz. Chem. Soc. 2003, 14, 889-901.
42. Suwanchawalit, C.; Wongnawa, S. Triblock copolymer-templated synthesis of
porous TiO2 and its photocatalytic activity J. Nanoparticle Res. 2010, 12, 2895-
2906.
43. Japanese Industrial Standards (JIS) K 5400, Chapter 8: Test methods for
resistance of film. Japanese Standards Assoc 1991.
44. Kalaignan, G. Paruthimal, and Moon-Sung Kang. "Effects of compositions on
properties of PEO–KI–I2 salts polymer electrolytes for DSSC." Solid State Ionics
2006, 177, 1091-1097.
50
45. A. F. Nogueira1, J. R. Durrant, M. A. De Paoli1 Dye-Sensitized Nanocrystalline
Solar Cells Employing a Polymer Electrolyte Chem. Commun., 2004, 40, 1662
46. Nogueira, Ana F., James R. Durrant, Marco A. De Paoli. "Dye‐Sensitized
Nanocrystalline Solar Cells Employing a Polymer Electrolyte." Advanced
Materials 2001, 13, 826-830.
47. Stergiopoulos, Thomas, et al. "Binary polyethylene oxide/titania solid-state redox
electrolyte for highly efficient nanocrystalline TiO2 photoelectrochemical cells."
Nano Letters 2002, 2, 1259-1261.
48. Moon-Sung Kang, Jong Hak Kim, Jongok Won, Yong Soo Kang Dye-sensitized
solar cells based on crosslinked poly(ethylene glycol) electrolytes J. Photochem.
Photobio. A: Chem. 2006, 183, 15
49. Wu, Jihuai, et al. "An all-solid-state dye-sensitized solar cell-based poly (N-alkyl-
4-vinyl-pyridine iodide) electrolyte with efficiency of 5.64%." Journal of the
American Chemical Society 2008, 130. 11568-11569.
50. S. Ganesan, B. Muthuraaman, Vinod Mathew, J. Madhavan,P. Maruthamuthu, , S.
Austin Suthanthiraraj Performance of a new polymer electrolyte incorporated
with diphenylamine in nanocrystalline dye-sensitized solar cell Solar Energy
Mater. & Solar Cells, 2008, 92, 1718
51. Bai, Yu, et al. "High-performance dye-sensitized solar cells based on solvent-free
electrolytes produced from eutectic melts." Nature materials 2008, 7, 626-630.
52. Benedetti, João E., et al. "A polymer gel electrolyte composed of a poly (ethylene
oxide) copolymer and the influence of its composition on the dynamics and
performance of dye-sensitized solar cells." J. Power Sources 2010, 195, 1246-
1255.
53. Roh, Dong Kyu, et al. "Amphiphilic poly (vinyl chloride)-g-poly (oxyethylene
methacrylate) graft polymer electrolytes: Interactions, nanostructures and
applications to dye-sensitized solar cells." Electrochimica Acta 2010, 55, 4976-
4981.
54. Yao, Yu, et al. "Carbon-coated SiO2 nanoparticles as anode material for lithium
ion batteries." Journal of Power Sources 2011, 196, 10240-10243.
55. Kuan-Chieh Huang, Po-Yen Chen, R. Vittal, Kuo-Chuan Ho Enhanced
performance of a quasi-solid-state dye-sensitized solar cell with aluminum nitride
in its gel polymer electrolyte Solar Energy Mater. & Solar Cells, 2011, 95, 1990
51
APPENDICES
52
APPENDIX A
DYE-SENSITIZED SOLAR CELLS (DSSC)
As mentioned in the introduction, DSSC is a kind of inorganic solar cell which is
composed by semiconductor, organic dye, electrolyte and metal electrode. As shown in
figure 30, the organic dye S absorbs the light and activated to the higher energy level. The
electron from the dye injects to the semiconductor which is usually TiO2 and transfer
through the out circuit to the metal electrode. Then the electron reduces I- to I3
- and
completes the circulation. 41
Figure 30. Representation of a dye-sensitized TiO2 solar cell and the processes involved
in energy conversion (S represents the dye-sensitizer and I-/I3
- is the charge mediator).
TiO2 is the most significant part in DSSC. A lot work has been done to modify the TiO2
thin film to make the efficiency higher. In this thesis, different TiO2 structures and
coating methods were tested. The organic dye is usually Di-tetrabutylammonium cis-bis
(isothiocyanato) bis (2, 2’-bipyridyl-4, 4’-dicarboxylato) ruthenium (II) (N719), which is
53
extremely expensive. In the second part of this appendix, the cheap copper-complex dye
is discussed to compare with the commercialized N719.
I. Modification of TiO2 thin film and casting method
1. Preparation of TiO2 paste
1.1. Sol-gel recipe
1.1.1. 1% Sol-gel recipe
HCl solution (400 mL 0.1M, pH=1) was prepared by diluting 3.33mL of concentrated
HCl to achieve 400 ml solution. 5.0 g TiCl4 was added to the solution in a dropwise
manner under magnetic stirring (900 RPM, 0 oC).TiCl4 should also be kept at 0
oC before
adding. The solution was left stirred for 2h (0 oC). NH4OH was added to the solution
until pH reaches 8 (pH was determined by pH meter). The color of the gel became ivory
immediately and the viscosity increased a lot (like white cake) indicating the formation of
hydrated titanium oxide gel Ti(OH)4. After aging for 2h under magnetic stirring, the
white precipitate was separated by Buchner funnel and washed with distilled water for
several times until no Cl- ion was detected (use Ag
+ to detect).
The precipitate was put into a conical flask and dispersed in 100 mL DI under magnetic
stirring. 17.9g Hydrogen peroxide solution and 90mL DI water were added into the slurry
at 5 oC. The solution was kept stirring for 2h. After that, the solution was heated at 90
oC
for 8 h with a reflux condenser pipe.
Yellow transparent solution was gained at last.
1.1.2. 5% sol-gel recipe
After we gained the 1% TiO2 sol-gel, I left it on hot plate and turned it to 70 oC. The
weight of beaker and solution were measured. The solvent evaporated and solution was
54
concentrated. The weight of the solution remained was measured again. When the weight
was only one fifth of the original weight, the concentration was 5%. The solution became
highly viscous from solution to gel. The color was still yellow.
1.2. Normal TiO2 paste
1.8g TiO2(Anatase or P25), 3.6mL DI water, 0.54g PEG, 0.0642g Triton X-100 and
0.117g acetylacetone. PEG and DI water were added into the bottles first and mixed with
hand. TiO2 was added and sonicator was applied to make them mix well. After adding
Triton X-100 and acetylacetone, solution was sonicated for 30 min and stirred by
magnetic bar for 2 days.
1.3. Porous TiO2 paste
1.3.1. Method I42
In a typical preparation, a 0.4-g/L Pluronic P123 aqueous solution was mixed with
titanium ethoxide in pH=1 with stirring for 2h. The resulting solution was then treated
with ammonia solution until the pH was 7 and maintained at the same temperature for a
day. The white precipitate formed was extracted with dichloromethane twice then filtered
and washed with distilled water until no sulfate ion was found by BaCl2 solution test (0.1
M BaCl2). The washed samples were dried at 105 0C for a day and ground to fine powder
to give final products designated as P123–TiO2. P123-TiO2 was mixed with PEG, water,
Trion X-100 and acetylacetone to give a fine paste.
1.3.2. Method II43
1.6g Pluronic P123 was dissolved in 20 g ethanol. 3.4 g of titanium ethoxide and 0.3 mL
of concentrated HCl were added into the solution. The synthesized solution was dried at
55
room temperature to form a gel. Degussa P25 nanoparticles (Aerosil, ∼30 nm, BET 56
m2 /g) were added into the mesoporous TiO2 gel at 5% concentration by weight to obtain
mesoporous/P25 mixture films.
1.3.3. Method III
Directly mix commercial anatase with P123, water, Trion X-100 and acetylacetone and
stir for two days.
2. Preparation of TiO2 thin film
2.1. Tape casting
Magic tape was cut by a self-made model and stick to glasses. Use credit card to force the
air between glass and tape come out and make it flat. Some paste was put at one side of
the tape and a metal column was used to cast paste on glass as flat as possible. (Figure 9)
2.2. Screen printing
The screen characteristics are as follows: material, polyester; mesh count, 90T mesh/cm;
mesh opening, 60 μm; thread diameter, 50 μm; open surface, 29.8%; fabric thickness, 83
μm. The procedure was shown in figure 31.
2.3. Spin coating
The TiO2 paste was dropped on the FTO glass and spin coated. After it was dried, coat
another layer of TiO2 thin film. It was repeated five times for each sample. The RPM is
2000.
56
Figure 31. Experimental procedure for screen printing.
Figure 32. The instrument and schematic procedure for spin coating.
57
3. Results of TiO2 thin film
Table 10. Quality of TiO2 thin film fabricated by different paste and casting methods.
No
. TiO2 paste
Casting
method
Thickne
ss
Flexibilit
y*
Adhesio
n
Hardne
ss
1 1% Sol-gel TiO2 Spin coating 200 ~
400 nm Very good
Very
good
Very
good
2 1% Sol-gel TiO2 Screen
printing ~500 nm Very good
Very
good
Very
good
3 5% Sol-gel TiO2 Spin coating 200nm
~2 µm Normal Bad Normal
4 5% Sol-gel TiO2 Screen
printing 1~3 µm Good Good Normal
5 Normal TiO2 Screen
printing
10~20
µm Good Good Good
6 Normal TiO2 Tape casting 10~20
µm Good Good Good
7 Porous TiO2:
Method I Tape casting 5~10 µm Normal Bad
Very
bad
8 Porous TiO2:
Method II Tape casting 1~5 µm Bad Bad
Very
bad
9 Porous TiO2:
Method III Tape casting 1~5 µm Bad Bad
Very
bad
10 Dyesol** Screen
printing 15 µm Good Good Good
*The method for determining the thin film quality was based on the literature.43
** Dyesol is a commercialized DSSC product from Dyesol Company.
Figure 33. Photographs of TiO2 thin film corresponding to the 8.
58
From the results in table 10, 1% sol-gel TiO2 has the best quality. However, the thickness
for 1% sol-gel TiO2 is less than 1 µm which is much less than the optimal thickness for
DSSC. For all the porous TiO2, the thin films are all bad. They didn’t stick to the glass
hard and was easy to be scratched by fingers. Considered the thickness and other
properties of the TiO2 thin films, the normal TiO2 thin film may be the best for DSSC.
4. DSSC assembling
After the preparation of TiO2 thin films, the adsorption of dye was carried out by soaking
the film in 0.5 mM dye solutions at 80 0C. The dye, Di-tetrabutylammonium cis-bis
(isothiocyanato) bis (2, 2’-bipyridyl-4, 4’-dicarboxylato) ruthenium (II) (N719), was
obtained from Aldrich. The dye was allowed to soak at room temperature for 24 hours in
a mixture solution of tert-butyl alcohol and acetonitrile (1:1). Thereafter, the dye-
adsorbed TiO2 electrodes were taken out and rinsed with dry ethanol. The rinsing process
was repeated several times to completely remove unbound dyes. Finally, the dye-
adsorbed TiO2 films were dried in air. A counter electrode was prepared by sputtering
(Hitachi E-1045 ion sputter) a thin platinum layer on an FTO substrate 20 nm. The dye-
adsorbed TiO2 electrode and Pt counter electrode were assembled into a sandwich-sealed
type cell by heating with hot-melt Surlyn film (25 μm thickness, 1702, DuPont) as a
spacer. A drop of electrolyte solution (0.05 M I2, 0.5 M LiI, 0.5 M 4-tert-butylpyridine (t-
BPy) in acetonitrile) was injected through a hole in the counter electrode, which was then
sealed with the glass cement. The working area of the electrode is 0.25 cm2.
59
5. Efficiency test of DSSC
The efficiency of DSSC is measured by an advanced current-voltage meter. The light is
generated by a solar simulator (Newport, 94023A) with a 150 mW Xe lamp. The light
intensity is 100mW/cm2 which is AM 1.5 standard sunlight. The schematic setup is
shown in figure 34. The calculation of the efficiency is based on the equation below:
where Jsc is short circuit current density, Voc is open circuit voltage, Pmax is maximum
power of DSSC, Pin is power of UV light and η is efficiency of DSSC. Jsc and Voc can be
obtained from the voltage-current profile in figure 35.
Figure 34. Measurement of the efficiency of DSSC.
Power supply
150
150 mW Xe lamp
Cell
Measurement of Cell Perfromance
AM 1.5 simulated
sunlight
100 mW/cm2
Filter
Volt/Amp Meter
60
Figure 35. The calculation of the efficiency of DSSC based on the voltage-current profile.
Table 11. Experimental results of the performance of DSSCs.
No. TiO2 paste Casting
method
Voc
(V)
Jsc
(mA/cm2)
FF Efficiency
(%)
1 1% Sol-gel TiO2 Spin coating 0.163 0.0152 0.25 0.00063
2 1% Sol-gel TiO2 Screen printing 0.256 0.0072 0.26 0.00047
3 5% Sol-gel TiO2 Spin coating / / / /
4 5% Sol-gel TiO2 Screen printing 0.056 0.128 0.31 0.0022
5 Normal TiO2 Screen printing 0.724 5.216 0.64 2.4
6 Normal TiO2 Tape casting 0.733 8.068 0.69 4.1
7 Porous TiO2: Method I Tape casting / / / /
8 Porous TiO2: Method II Tape casting / / / /
9 Porous TiO2: Method III Tape casting / / / /
10 Dyesol Screen printing 0.730 10.88 0.65 5.2
From the results in table 11, the efficiency of 5% sol-gel TiO2 is higher than that of 1%
sol-gel TiO2. It indicates that the thickness is more important than the other properties for
the cell performance. For comparison the results of sample 5 and 6 in 10, we can see that
tape casting is better than screen printing. This is due to the arrangement of TiO2 and also
the thickness.
61
6. Conclusions
1% sol-gel TiO2 has the best adhesion and hardness properties among all the TiO2 thin
films. The efficiency of DSSC is strongly dependent on the thickness of TiO2 thin film.
II. Copper-complex dye
Di-tetrabutylammonium cis-bis (isothiocyanato) bis (2, 2’-bipyridyl-4, 4’-dicarboxylato)
ruthenium (II) (N719) is the most widely used organic dye in DSSC. It has a good
performance and already be commercialized. The only problem is that this N719 organic
dye is too expensive. It costs $316 per gram. It is an urgent problem needed to be solved
that another cheaper dye can replace N719.
Figure 36. The chemical structure of N719.
62
Based on the chemical structure of N719 in figure 36, we can see that there are two SCN
groups and two 2, 2’-bipyridyl-4, 4’-dicarboxylato groups. As my group member
accidently found that when the copper salt was mixed with tetraethylenepentamine
(TEPA) and aniline, the solution became dark blue. This inspired me to design the
copper-complex dye with TEPA and aniline and tested in DSSC.
Figure 37 shows the chemical structures of Cu(TEPA)(Aniline)2Cl2 (Dye1) and
Cu(TEPA)2(NO3)2 (Dye2). The synthetic route is shown in figure 38 and 39. All the
precursors used in the synthesis are very cheap. The approximate price for Dye1 and
Dye2 is just $1 per gram which is much cheaper than that of N719.
63
Figure 37. The chemical structures of (a) Dye1 and (b) Dye2.
(a)
(b)
64
10 mL H2O
0.002 mol CuCl2 0.002 mol TEPA+
Copper aqueous solution
Dye1
Dissolved
Stirring for 1 h
Auto clave at 403K for 2 h
0.004 mol anilineDissolved
Figure 38. The synthetic route of Dye1.
The synthesis for Dye1 and Dye2 were very easy. Copper precursors were just simply
mixed with TEPA and aniline and stirred for 1h. The colors of the both solution were
suddenly changed to dark blue when TEPA were added. It indicated that the TEPA had a
quite strong interaction with copper. The solutions were treated in auto clave at 403K for
2h in order to enhance the stability of Dye1 and Dye2. The blue color didn’t change after
the treatment, which indicated that the copper complexes were very stable.
The pictures of Dye1 and Dye2 were shown in figure 40. N719 was also included for the
comparison.
65
10 mL H2O
0.002 mol Cu(NO3)2 0.004 mol TEPA+
Copper aqueous solution
Dye2
Dissolved
Stirring for 1 h
Auto clave at 403K for 2 h
Figure 39. The synthetic route of Dye2.
Figure 40. Pictures of N719, Dye1 and Dye2 in solution.
N719 Dye1 Dye2
66
From the pictures in figure 40, the color of N719 was dark purple. Dye1and Dye2 both
had the dark blue color. From more specific observation, the color of Dye2 was darker
than Dye1. The reason might be the TEPA was replaced by aniline in Dye1.
Figure 41. The pictures of TiO2 thin films after immersing in Dye1 and Dye2 for 24 h.
After immersing in Dye1 and Dye2 for 24 h, the TiO2 thin films became blue. However,
the adsorption dye was not as strong as N719. It could be washed by ethanol. The reason
might be the solvent of Dye1 and Dye2 was water, which had a worse adhesion to TiO2
thin film.
The TiO2 thin films with Dye1 and Dye2 were assembled to DSSC and tested the
efficiency.
Dye1
Dye2
67
Table 12. Experimental results of DSSC with copper-complex dye.
Dye TiO2 Name Voc (V) Jsc (mA) FF Efficiency
(%)
Dye1
Sol-gel
TiO2
1 0.00016 0.014 0.41 2.60E-07
2 0.00017 0.0112 0.48 2.99E-07
3 0.00012 0.0108 0.48 1.54E-07
3 0.00012 0.0108 0.48 1.54E-07
Dyesol
1 0.559 0.048 0.24 6.40E-03
2 0.528 0.084 0.28 1.20E-02
Washed
dye 0.0099 0.0124 0 0
Normal
TiO2
1 0.465 0.028 0.46 5.70E-03
2 0.528 0.052 0.31 8.30E-03
Dye2 1 0.434 0.0196 0.39 3.30E-03
2 0.372 0.028 0.41 4.10E-03
N719 1 0.733 8.068 0.69 4.1
From the results in table 12, the Voc and Jsc for sol-gel TiO2 were both very low. It
indicated that the sol-gel TiO2 didn’t perform well in DSSC. It matched the results in the
first part of appendix. Compared the DSSC with washed dye and with dye, the results
were very obvious. The efficiency of the DSSC without dye was just 0 which indicated
that the dye were completely washed away. The DSSC with Dye1 had a good Voc which
was close to that with N719. The performance of DSSCs with Dye1 and Dye2 were
close, both of them had a good Voc. However, the Jsc of the DSSCs with Dye1 and Dye2
were significantly lower than that of N719, which resulted in the low efficiency of cells.
Conclusions
Copper-complex dyes were much cheaper than N719. The synthetic route was easy and
the dyes were quite stable. TiO2 thin films didn’t have a good adsorption of them, which
68
resulted in the low current and efficiency. However, the DSSCs with copper-complex dye
had a close voltage to that of N719 which might have some specific applications related
to high voltage.
III. Polymer electrolyte
1. P123 polymer electrolyte
Electrolyte is also an important part in dye-sensitized solar cells. The I-/I3
- redox pair can
be oxidized by the electron from counter electrode and completed the whole circulation.
However, the liquid electrolyte used in most of the DSSCs had a short lifetime. The
solvent in the liquid electrolyte was acetonitrile and it was easy to evaporate. As soon as
the solvent was gone, the DSSC was dead. So polymer electrolyte became a hot topic in
nowadays. 44-55
In this thesis, P123 was used as the polymer in polymer electrolyte.
Table 13. Performance of two dye-sensitized solar cells with and without electrolyte.
Cell No. Electrolyte Voc (V) Isc (mA) FF (%) Efficiency
(%)
1
No
electrolyte 0.59 0.00095 0.58 0.0013
Only P123 0.652 0.0058 0.49 0.0074
Polymer
electrolyte 0.59 0.194 0.53 0.24
2
No
electrolyte 0.776 0.00026 0.28 0.00022
Only P123 0.745 0.0016 0.30 0.0015
Polymer
electrolyte 0.559 0.12 0.47 0.13
The results in table 13 showed that DSSC without electrolyte still could work. It had the
high open circuit voltage around 0.6 V but very low short circuit current. It indicated that
69
electrolyte only affected the current and had nothing to do with the voltage. The results of
DSSC only with P123 had a better current compared to that without P123. It suggested
that the P123 could separate the working electrode and counter electrode and prevented
the short circuit. If the I-/I3
- redox couple were added in P123, it further increased the
current of DSSC. The results in 11 showed that DSSC with polymer electrolyte had the
efficiency more than 0.1%, which was not far away from that of DSSC with liquid
electrolyte.
0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7
0.00
0.05
0.10
0.15
0.20
0.25
Cu
rre
nt (m
A)
Voltage (V)
Cell 1_No electrolyte
Cell 1_P123
Cell 1_polymer electrolyte
Cell 2_No electrolyte
Cell 2_P123
Cell 2_polymer electrolyte
Figure 42. Current-Voltage profile of two DSSCs with and without electrolyte.
2. Crosslinking PEG polymer electrolyte.
70
PEG is most widely used polymer electrolyte for DSSC. The performance of crosslinking
PEG has been studied by a Korean scientist.48
The preparation method for the polymer
electrolyte was followed by the literature. HCl is used to initiate the cross-linking
reaction. GA is short for glutaraldehyde, which is a cross linking reagent.
From the IR results in figure 43a, the peak of –OH group shifted from 3467 cm-1
to 3495
cm-1
after crosslinking reaction. This indicated that the –OH group from PEG had been
changed due to the crosslinking reaction. This also matched the reported result in the
literature48
. From the absorbance spectra in figure 43b, some small peaks appeared
between 1400 cm-1
and 900 cm-1
after adding HCl. These small peaks could be assigned
to the new ether bonds which were generated after crosslinking. Both the evidences
proved that the PEG had been cross-linked in the polymer electrolyte.
The performance of the DSSCs with cross-linked PEG polymer electrolyte was tested.
The Voc was 0.68V and the Jsc was 0.006mV/cm2. The voltage was quite close to the
DSSC with liquid electrolyte in table 12. But the current was too low to get a good
efficiency.
71
4000 3500 3000 2500 2000 1500 1000 5000.0
0.5
1.0
1.5
2.0
Sin
gle
Be
am
In
ten
sity (
a.u
.)
Wavenumber (cm-1)
PEG
GA
PEG+GA
PEG+GA+HCl
3467cm-1
3495cm-1
4000 3500 3000 2500 2000 1500 1000
0.0
0.5
1.0
Ab
so
rba
nce
Wavenumber (cm-1)
PEG
GA
PEG+GA
PEG+GA+HCl
Figure 43. (a) Single beam IR spectroscopy and (b) Absorbance of the chemicals and the
solution of PEG polymer electrolyte.
(a)
(b)
72
APPENDIX B
INTENSITY OF UV LIGHT
All the TiO2 samples are very sensitive to the UV light, so the distribution of UV light is
significant to the results of the cell performance. In this chapter of appendix, the one-
dimension and two-dimension of the distribution of UV light were discussed.
150 mm
140 mm
12 mm
Detector
Move every 5 mm
Optical fiber
Figure 44. Schematic setup of UV light measurement.
73
The diameters of the photo detector and the optical fiber were 12mm and 10mm. Because
all the area of the detector had to be covered by UV light, it had to be a long distance
between the optical fiber and the detector. The setup was showed in figure 44. I write
down the intensity of the UV light at the certain position and move the detector in one-
dimension every 5 mm. The results were shown in table .
Table 14. The UV light intensity at different positions.
Distance (mm) 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70
Power (mW) 12 12 12 11 10 8 7 4 4 3 2 1 1 1 0
Table 14 showed that the intensity of UV light was the strongest in the center of the light,
which was easy to understand. The intensity decreased rapidly when the detector moved
away from the center. The results were plotted in figure 45 and the distribution was also
stimulated by Gauss equation.
-60 -40 -20 0 20 40 60
0
2
4
6
8
10
12
14
Po
we
r (m
W)
Distance (mm)
Equation y=y0+A*exp(-0.5*((x-xc)/w)^2)
Adj. R-Square 0.98969
Value Standard Error
Power y0 -0.13113 0.22414
Power xc 1.60281E-14 0.4398
Power w 26.34781 0.75705
Power A 12.76479 0.24891
Figure 45. The distribution of UV light intensity at different positions.
74
The simulated curve in figure 45 was quite sharp which indicated that the distribution of
the UV light was not uniform.
In order to get the better understanding of the distribution of the UV light, two-dimension
distribution was also obtained. In this experiment, the detector moved in the whole area
of the light spot and every point was 5mm away.
-9.0 -7.5 -6.0 -4.5 -3.0 -1.5 0.0 1.5 3.0 4.5 6.0 7.5 9.0
-9.0
-7.5
-6.0
-4.5
-3.0
-1.5
0.0
1.5
3.0
4.5
6.0
7.5
9.0 0.2
0.4 0.5 0.6 0.5 0.3
0.6 1.9 3 3.2 2.6 1.3 0.3
0.3 1.9 5.9 12 14 12 6.2 1.4 0.3
0.7 4.4 19 27 31 25 14 5 0.8
1.3 7.5 25 33 37 31 21 9.7 1.7
1.5 88 24 29 35 30 21 11 2.4
1.3 7.6 20 24 26 23 17 9.5 1.8
0.9 5.3 11 17 17 15 12 5.8 0.7
0.3 2.6 7.1 10 11 10 6.5 2 0.3
0.6 2.5 4.3 4.5 3.5 1.4 0.3
0.4 0.6 0.7 0.5 0.3
0.2
UV light intensity (mW/cm2)
Y-a
xis
(cm
)
X-axis (cm)
Figure 46. The intensity of UV light at different positions with optical fiber.
Figure 46 showed that the intensity of every point was recorded. The maximum intensity
was 37 mW/cm2 of the center point.
75
Figure 47. 2D distribution of UV light intensity with optical fiber. Distance between
detector and light source is 17cm.
76
Figure 47 clearly showed that the intensity of UV light decreased rapidly away from the
center.
I also did the experiment when there was an angle between the detector and the light
source. In most of my photo degradation experiment, the angle was 450.
The intensity distribution of UV light in figure 48 showed a sharper circular cone. It
indicated that the light was much less uniform when there was an angle between the light
source and photo detector.
77
Figure 48. 2D distribution of UV light intensity with an angle between optical fiber and
photo detector. Distance between detector and light source is 17cm.
78
-7.5 -6.0 -4.5 -3.0 -1.5 0.0 1.5 3.0 4.5 6.0 7.5-7.5
-6.0
-4.5
-3.0
-1.5
0.0
1.5
3.0
4.5
6.0
7.5
9.0
0.7 0.31
26 20 4202
60 50 37 45334
99 77 65 24994611
120 99 84 42 11206825
110 85 79 36 0.71097224
66 62 56 14 0.3674811
41 39 20 0.74227
14 8 0.3151.5
0.50.3
UV light intensity (mW/cm2)
Y-a
xis
(cm
)
X-axis (cm)
Figure 49. The UV light intensity at different positions without optical fiber.
The optical fiber also had some effect on the distribution of UV light intensity. So I
directly shined the UV light of light source to the photo detector and did the same
experiment above.
In figure 49, the intensity of each point was shown. Compared to the intensity in figure
46, it increased three times. It indicated that the optical fiber had cut off some part of the
UV light and decreased the light intensity.
The 2D distribution was also shown in figure 50. Compared to the distribution of UV
light in figure 48, there was no significant difference between them. It indicated that the
optical fiber could only introduce the light direction but not change the distribution of
light intensity.
79
Figure 50. 2D distribution of UV light intensity without optical fiber. Distance between
detector and light source is 17cm.
80
APPENDIX C
PHOTO DEGRDATION OF PVC THIN FILMS
Photo degradation of organics or polymers was also an interesting project that our group
was working on. Due to the cooperation with Hallstar Company, they sent us several
samples of PVC thin films with different additives and asked as test the UV resistance of
each PVC thin film.
The sample named Control Sample didn’t have any additives in the PVC film. The
sample named RX14426 and RX14427 both had the UV resistance additives from
Hallstar Company. Another sample named Tinuvin 328 had the commercialized additives.
Most of the experiments were tested by in-situ DRIFT IR spectroscopy. UV light was
applied to accelerate the degradation rate of the samples in air. Samples with 4 mil and 8
mil thickness were both tested for comparing the effect of thickness.
I. In-situ DRIFT IR spectroscopy of each sample at 100 mW/cm2 UV light intensity
within 30 min.
Figure 51 showed that the several IR peaks were increased or decreased within 30 min
UV degradation. The peak at 3255 cm-1 was assigned to –OH group. The peaks at 2956
cm-1
, 2922 cm-1
and 2850 cm-1
were all assigned to –CH3 group. The peaks at 1784 cm-1
and 1705 cm-1
were assigned to –C=O group. The increase of –OH and –C=O groups
meant the generation of PVC degradation product. The decrease of –CH3 indicated the
81
disappearance of PVC. The slower increase or decrease of the reacting rate, the better UV
resistance of the PVC samples.
4000 3500 3000 2500 2000 1500 1000
2956 cm-1
2922 cm-1
2850 cm-1
1705 cm-1
1784 cm-1
PVC + Tinuvin 328
PVC + RX14427
30 min UV15 min UV0 min UV
PVC Control Sample
Wavenumber (cm-1)
0 min UV
15 min UV
30 min UV
Ab
so
rba
nce
(a
.u.)
0 min UV
15 min UV
30 min UV
0.1
3255 cm-1
Figure 51. Differential absorbance IR spectra of the PVC samples before and after 30
minutes of UV irradiation (200 mw/cm2, Hg lamp).
The increase of the intensity of the band at 3255 cm-1
and 1784 cm-1
indicted that the
PVC sample was oxidized.
82
0 5 10 15 20 25 30
0.00
0.01
0.02
0.03
0.04
0.05
0.06
0.07
0.08
0.09
0.10
UV on
PVC 8 mil film samples
3255 cm-1 wavenumber
Ab
so
rba
nce
(a
.u.)
Time (minutes)
Tinuvin 328_2
RX14427_7RX14427_6
RX14427_5
RX14427_4
RX14427_3RX14427_1
Control sample_3
Control sample_2
Tinuvin 328_1
Control sample_1
Figure 52. Absorbance vs. time spectra of the PVC 8 mil film samples before and after 30
minutes of UV irradiation (200 mw/cm2, Hg lamp) at 3255cm
-1.
In figure 52, the increasing rate of –OH group were shown. RX14427 increased the
slowest among the three samples. It indicated that RX14427 samples had the best
resistance to UV light from the –OH group.
83
0 5 10 15 20 25 30
-0.08
-0.06
-0.04
-0.02
0.00
0.02
Tinuvin 328
RX14427
PVC 8 mil film samples
2956 cm-1 wavenumber
Ab
so
rba
nce
(a
.u.)
Wavenumber (cm-1)
Control sample
0 5 10 15 20 25 30
-0.10
-0.08
-0.06
-0.04
-0.02
0.00
PVC 8 mil film samples
2923 cm-1 wavenumber
Wavenumber (cm-1)
Ab
so
rba
nce
(a
.u.)
Tinuvin 328
RX14427
Control sample
84
0 5 10 15 20 25 30
-0.08
-0.06
-0.04
-0.02
0.00
PVC 8 mil film samples
2850 cm-1 wavenumber
Wavenumber (cm-1)
Ab
so
rba
nce
(a
.u.)
Tinuvin 328
RX14427
Control sample
Figure 53. Absorbance vs. time spectra of the PVC 8 mil film samples before and after 30
minutes of UV irradiation (200 mw/cm2, Hg lamp) at 2956cm
-1, 2923cm
-1 and 2850cm
-1.
All of these three bands were assigned to –CH3 group. From the results in figure 53, there
was no big difference among the three samples. The PVC was all reacted with a similar
degradation rate.
85
0 5 10 15 20 25 30
0.00
0.01
0.02
0.03
0.04
0.05
0.06
0.07
UV on
PVC 8 mil film samples
1784 cm-1 wavenumber
Ab
so
rba
nce
(a
.u.)
Time (minutes)
Tinuvin 328_2
RX14427_7RX14427_6
RX14427_5
RX14427_4
RX14427_3
Control sample_2
Control sample_3
RX14427_1
Control sample_1
Tinuvin 328_1
Figure 54. Absorbance vs. time spectra of the PVC 8 mil film samples before and after 30
minutes of UV irradiation (200 mw/cm2, Hg lamp) at 1784cm
-1.
The reacting rate of the band at 1784 cm-1
showed that RX14427 had a much slower
degradation rate than Tinuvin 328. It indicated that RX14427 was better than Tinuvin 328
for UV resistance in the –C=O group.
86
0 5 10 15 20 25 30
0.00
0.05
0.10
0.15
0.20
0.25PVC 8 mil film samples
1705 cm-1 wavenumber
Wavenumber (cm-1)
Ab
so
rba
nce
(a
.u.)
Tinuvin 328
RX14427
Control sample
Figure 55. Absorbance vs. time spectra of the PVC 8 mil film samples before and after 30
minutes of UV irradiation (200 mw/cm2, Hg lamp) at 1705cm
-1.
The results in figure 55 showed that both RX14427 and Tinuvin 328 had a slower
degradation rate than the control sample.
87
0 5 10 15 20 25 30
0.000
0.005
0.010
0.015
0.020
0.025
0.030
0.035
0.040
0.045
0.050
0.055PVC 4 mil film samples
3255 cm-1 wavenumber
RX14427_4
RX14427_3
RX14427_2
RX14427_1
Control sample_4
Control sample_3
Control sample_2
Control sample_1
Tinuvin 328_2
Ab
so
rba
nce
(a
.u.)
Time (minutes)
UV on
Tinuvin 328_1
Figure 56. Absorbance vs. time spectra of the PVC 4 mil film samples before and after 30
minutes of UV irradiation (200 mw/cm2, Hg lamp) at 3255 cm
-1.
For the samples with 4 mil thickness, the reproducibility of RX14427 was not good. It
was not reliable to raise a conclusion based on this result.
88
0 5 10 15 20 25 30
0.000
0.005
0.010
0.015
0.020
0.025
0.030
0.035
0.040
UV on
Ab
so
rba
nce
(a
.u.)
Tinuvin 328_2
Tinuvin 328_1
RX14427_4RX14427_3
RX14427_2
RX14427_1
Control sample_4
Control sample_3Control sample_2
Control sample_1
Time (minutes)
PVC 4 mil film samples
1784 cm-1 wavenumber
Figure 57. Absorbance vs. time spectra of the PVC 4 mil film samples before and after 30
minutes of UV irradiation (200 mw/cm2, Hg lamp) at 1784 cm
-1.
The reproducibility of RX14427 was better in figure 57. The degradation rate of control
sample was the slowest, which didn't match the results in the previous experiment.
Conclusions
1. The reproducibility for the Tinuvin 328 film samples was the best. We didn’t test it
many times because it always gave the stable signals and repeatable results.
2. The reproducibility for the RX14427 film samples was the worst. Even we tested it
more than four times, the results were still not convinced. The reason may be the
uniformity in the edge was not good. We cut a small piece (0.5cm*0.5cm) from the
edge of the aluminum foil every time and maybe the samples were not all the same at
that scale.
3. The reason why Tinuvin 328 had the worst UV resistance was due to several reasons:
a. The thickness of Tinuvin 328 had a big difference compared to the others.
b. Tinuvin 328 was not uniform in the PVC samples. The pieces we ran the
experiment didn’t have much Tinuvin 328 inside.
c. 30 minutes was not enough to determine the final oxidized rate under UV light.
89
II. In-situ DRIFT IR spectroscopy of each sample at 1000 mW/cm2 UV light intensity
within 180 min.
In order to study the IR difference when the samples were mostly degraded by UV light,
higher UV light intensity and longer time were applied in this experiment.
All of the four Hallstar samples were coated on aluminum foil, which the thickness is 20
mil. They were heated to 50 0C by a heating element during the in situ IR test for 3 hours.
350 W Mercury lamp was applied to provide the UV irradiation (1000mW/cm2).
90
PVC control sample
4000 3500 3000 2500 2000 1500 1000
1.0
Wavenumber (cm-1)
Sin
gle
bea
m i
nte
nsi
ty (
a.u
.)
180 min60 min
30 min10 min0 min
4000 3500 3000 2500 2000 1500 1000
89
8
10
43
12
83
13
95
17
84
17
05
18
04
33
06
29
71
29
10
28
51
IR d
iffe
ren
ce (
a.u
.)
Wavenumber (cm-1)
0.1
35
00
180 min - 0 min
60 min - 0 min
30 min - 0 min
10 min - 0 min
0 min - 0 min
(a) (b)
0 30 60 90 120 150 180
Time (min)
IR i
nte
nsi
ty a
t 1
04
3 c
m-1
(a.
u.)
0.05
0.5cm
(c)(d)
Figure 58. (a) Single beam spectra of PVC control sample collected during the UV
degradation. (b) IR difference spectra obtained by IR difference= -log(I/I0), where I is the
single beam at specified times and I0 is the single beam at 0 min. (c) Top view picture of
the PVC control sample at the end of the UV degradation experiment. (d) Variation in the
intensity of C-O stretch band at 1043 cm-1
.
The single beam IR spectra of PVC control sample in figure 58a didn't change much at
variation of time. So the difference IR spectra were used to distinguish the change during
the reaction. Figure 58b showed that PVC bands at 3500 cm-1
, 1804 cm-1
, 1359 cm-1
,
1283 cm-1
, 1043 cm-1
and 898 cm-1
were increased and bands at 2971 cm-1
, 2910 cm-1
and
2851 cm-1
were decreased during the UV degradation. (All the peaks from PVC were
marked red in all the figures). It indicated that the new –OH band and C=O band were
formed and CH2 and CH bands were disappeared. The other peaks like 3306 cm-1
, 1784
91
cm-1
and 1705 cm-1
were from the degradation of plasticizer (Paraplex G59). Figure 58c
showed that the color of PVC control sample was turned to dark brown at 50 0C after UV
degradation. In figure 58d, the intensity of peak at 1043 cm-1
was plotted versus the time
during the UV degradation. Due to the strong effect from the peak of plasticizer, the
peaks of PVC at 3500 cm-1
, 1804 cm-1
, 1359 cm-1
, 1283 cm-1
, 2971 cm-1
, 2910 cm-1
and
2851 cm-1
were not accurate to represent the degradation rate of PVC. So the C-O stretch
band at 1043 cm-1
was selected to show the degradation rate of PVC.
RX14426 + PVC sample
0 30 60 90 120 150 180
Time (min)
IR i
nte
nsi
ty a
t 10
43
cm
-1 (
a.u.)
0.05
4000 3500 3000 2500 2000 1500 1000
1804
Wavenumber (cm-1)
IR d
iffe
ren
ce (
a.u
.)
0.1 898
1043
1395
3306
2971
2910
2851
3500
1784
1705
180 min - 0 min
60 min - 0 min
30 min - 0 min
10 min - 0 min
0 min - 0 min
0.5cm
(c)
(a) (b)
Figure 59 (a) IR difference spectra of RX14426 + PVC sample obtained by IR
difference= -log(I/I0), where I is the single beam at specified times and I0 is the single
beam at 0 min. (b) Top view picture of RX14426 + PVC sample at the end of UV
degradation experiment. (c) Variation in the intensity of C-O stretch band at 1043 cm-1
.
92
Figure 59a showed that all the peaks at 3500 cm-1
, 1804 cm-1
, 1359 cm-1
, 1283 cm-1
, 2971
cm-1
, 2910 cm-1
, 2851 cm-1
, 1043 cm-1
and 898 cm-1
were increased or decreased because
of the degradation of PVC. Figure 59b and figure 59c are similar to figure 58c and figure
58d except that RX14426 + PVC sample degraded much slower than PVC control
sample.
RX14427 + PVC sample
4000 3500 3000 2500 2000 1500 1000
Wavenumber (cm-1)
IR d
iffe
ren
ce (
a.u
.)
0.1 18
04
89
8
10
43
13
95
33
06
29
71
29
10
28
51
35
00
17
84
17
05
180 min - 0 min
60 min - 0 min
30 min - 0 min
10 min - 0 min
0 min - 0 min
0 30 60 90 120 150 180
IR i
nte
nsi
ty a
t 10
43
cm
-1 (
a.u.)
Time (min)
0.05
(a) (b)
0.5cm
(c)
Figure 60. (a) IR difference spectra of RX14427 + PVC sample obtained by IR
difference= -log(I/I0), where I is the single beam at specified times and I0 is the single
beam at 0 min. (b) Top view picture of RX14427 + PVC sample at the end of UV
degradation experiment. (c) Variation in the intensity of C-O stretch band at 1043 cm-1
.
Figure 60a and figure 60b are similar to figure 59a and figure 59b which indicated that
RX14427+PVC sample were degraded after 3 hours under 1000 mW/cm2 UV irradiation.
93
In figure 60c, the signal was not stable and it made a lot of noise. However, it still
showed the increase at 1043 cm-1
of PVC degradation.
Tinuvin 328 + PVC sample
0 30 60 90 120 150 180
Time (min)
IR i
nte
nsi
ty a
t 10
43
cm
-1 (
a.u.)
0.05
4000 3500 3000 2500 2000 1500 1000
180 min - 0 min
60 min - 0 min
30 min - 0 min
10 min - 0 min
0.1
IR d
iffe
ren
ce (
a.u
.)
Wavenumber (cm-1)
1804
898
1043
1395
3306
2971
2910
2851
3500
1784
1705
0 min - 0 min
(a) (b)
(c)
0.5cm
Figure 61. (a) IR difference spectra of Tinuvin 328 + PVC sample obtained by IR
difference= -log(I/I0), where I is the single beam at specified times and I0 is the single
beam at 0 min. (b) Top view picture of Tinvuin 328 + PVC sample at the end of UV
degradation experiment. (c) Variation in the intensity of C-O stretch band at 1043 cm-1
.
In figure 61b, the color of Tinuvin 328+PVC sample slightly turned into brown which
were much lighter than the other three samples. It indicated that Tinuvin 328+PVC had
better UV resistance than others. Figure 61c also showed that the degradation rate of
Tinuvin 328+PVC increased much slowly.
94
4000 3500 3000 2500 2000 1500 1000
(a) PVC control sample
898
1043
1283
13951784
1705
1804
3306
2971
2910
2851
0.1 3500
180 min - 0 min
30 min - 0 min
0 min - 0 min
(c) RX14427 + PVC
(b) RX14426 + PVC
180 min - 0 min30 min - 0 min
0 min - 0 min
180 min - 0 min
30 min - 0 min
0 min - 0 min
(d) Tinuvin 328 + PVC
180 min - 0 min
30 min - 0 min
IR d
iffe
ren
ce (
a.u
.)
Wavenumber (cm-1)
0 min - 0 min
Figure 62. DRIFT IR spectra of (a) PVC control sample, (b) RX14426 + PVC sample, (c)
RX14427 + PVC sample and (d) Tinuvin 328 + PVC sample.
In figure 62, all the peaks of PVC at 3500 cm-1
, 1804 cm-1
, 1359 cm-1
, 1283 cm-1
, 2971
cm-1
, 2910 cm-1
, 2851 cm-1
, 1043 cm-1
and 898 cm-1
were increased or decreased during
the UV degradation. It indicated that all the PVC were degraded under strong UV
irradiation within enough time at 50 0C.
95
0 30 60 90 120 150 180
Tinuvin 328 + PVC
RX14426 + PVC
RX14427 + PVC
IR
inte
nsi
ty a
t 1043 c
m-1
(a.
u.)
Time (min)
0.05
PVC control sample
Figure 63. Variation in the intensity of C-O stretch band at 1043 cm-1
of PVC control
sample, RX 14426 + PVC sample, RX14427 + PVC sample and Tinuvin 328 + PVC
sample.
Figure 63 showed that four samples were all degraded but the degraded rates were quite
different. PVC control sample was degraded fastest after the first 30 min. The
degradation rates of RX14426+PVC sample and RX14427+PVC sample were almost the
same, which were slower than PVC control sample and faster than Tinuvin 328+PVC
sample. Tinuvin 328+PVC had the slowest rate which indicated it had the best UV
degradation.
96
0 30 60 90 120 150 180
Tinuvin 328+PVC
RX14426 + PVC
RX14427 + PVC
IR
in
ten
sity
at
33
06
cm
-1 (
a.u
.)
Time (min)
0.05
PVC control sample
0 30 60 90 120 150 180
Tinuvin 328+PVC
RX14426 + PVC
RX14427 + PVC
IR
in
ten
sity
at
28
51
cm
-1 (
a.u
.)
Time (min)
0.05
PVC control sample
0 30 60 90 120 150 180
Tinuvin 328+PVC
RX14426 + PVC
RX14427 + PVC
IR i
nte
nsi
ty a
t 1
78
4 c
m-1
(a.
u.)
Time (min)
0.05
PVC control sample
0 30 60 90 120 150 180
Tinuvin 328+PVC
RX14427 + PVC
IR
in
ten
sity
at
13
95
cm
-1 (
a.u
.)Time (min)
0.05
PVC control sample
(a) (b)
(c) (d)
Figure 64. Variation in the intensity of IR peaks at (a) 3306 cm-1
, (b) 2851 cm-1
, (c)
1784cm-1
, (d) 1395 cm-1
of PVC control sample, RX 14426 + PVC sample, RX14427 +
PVC sample and Tinuvin 328 + PVC sample.
The peaks at 3306 cm-1
and 1784 cm-1
were mainly from the degradation of plasticizer in
figure 64b and figure 64c. They were not very useful for judging the UV resistance of the
additives.
Figure 64d indicated that there was no big difference among RX14426, RX14427 and
Tinuvin 328 for the UV resistance. However, they were much better than the PVC control
sample.
Conclusion
97
The UV resistance of these four samples: Tinuvin 328>RX14427=RX14426>PVC
control sample.
III. Focal plane array IR spectroscopy.
An aluminum plate with four small holes in the middle was used as a cover to study the
focal plane array for Hallstar samples. The diameter of the aluminum plate was around 30
mm and the diameter of four holes are all 0.5 mm. Control sample, RX14426, RX14427
and Tinuvin 328 were put behind the aluminum plate and only a part of the sample can be
scanned by infrared. The locations of the four samples were shown in figure 65.
Figure 65. The locations of Control sample, RX14426, RX14427 and Tinuvin 328 and
the scan area of the focal plane array.
98
Figure 66. Experimental setup for UV degradation of Control sample, RX14426,
RX14427 and Tinuivn 328 by focal plane array.
99
Figure 67. Photographs of Control sample, RX14426, RX14427 and Tinuvin 328 before
and after UV degradation tested by focal plane array. Single beam spectra were collected.
Red color stands for the high intensity and blue color stands for the low intensity.
From figure 67, we can see that RX14426 can be seen clearly at 1724 cm-1
after degraded
by UV for 10 min. It also happens to Control sample at 180 min. This is due to the
sample lost during the experiments. The RX14426 and Control sample moved out of the
hole and we could not see them from the focal plane array. It can be proved by the IR
spectra below.
100
4000 3500 3000 2500 2000 1500 1000
Ab
sorb
ance
(a.
u.)
Control sample
RX14426
RX14427
180 min30 min10 min
Wavenumber (cm-1)
0 min
Tinuvin 328
180 min30 min10 min0 min
180 min30 min10 min0 min
180 min30 min10 min0 min
1043172429243306
Figure 68. IR absorbance spectra of Control sample, RX14426, RX14427 and Tinuvin
328 before and after UV degradation.
101
4000 3500 3000 2500 2000 1500 1000
1043172429243306
Control sample
180 min30 min10 min0 min
180 min30 min10 min
0 min
180 min30 min10 min0 min
180 min30 min10 min0 min
RX14426
RX14427
IR d
iffe
rence
(a.
u.)
Wavenumber (cm-1)
Tinuvin 328
Figure 69. IR difference spectra of Control sample, RX14426, RX14427 and Tinuvin 328
before and after UV degradation. Spectra were obtained by IR difference= -log(I/I0),
where I is the single beam at 180 min and I0 is the single beam at 0 min.
Figure 69 shows that control sample was not detected at 180min. RX14426 was not
detected after 10 min. It indicates that our setup has some problem with the sample fix.
Samples would be moved by the gravity or the heating of UV light. From the present
results, RX14427 was degraded the slowest at all the four wavenumbers.
102
Figure 70. Statistics results of all the old experiments for variation in the intensity of –OH
band at 3306 cm-1
, -CH and –CH2 band at 2924 cm-1
, C=O band at 1724 cm-1
and C-O
stretch band at 1043 cm-1
.
From all the old results, we can say that RX14426 and RX14427 always had better UV
resistance at hydroxyl group, and C-O band. They are similar to Control sample and
Tinuvin at –CH, –CH2 band and C=O band. The reproducibility of RX14426 and
RX14427 are worse than control sample and Tinuvin 328.
Conclusions
1. RX14427 was degraded slowest at all of the four wavenumbers which are 3306 cm-1
(hydroxyl group), 2924 cm-1
(alkyl group), 1724 cm-1
(carbonyl group) and 1043 cm-1
(C-
O stretch) from the present results.
103
2. Control sample and Tinuvin 328 has better reproducibility than RX14426 and
RX14427 from the statistical results. But RX14426 and RX14427 had better UV
resistance to –OH band and C-O band.
104
APPENDIX D
NFPA AND HMIS RATING OF CHEMICALS
Tab
le 1
5. N
FPA
and H
MIS
rat
ing o
f ch
emic
als
1.
Nat
ion
al F
ire
Pro
tect
ion
Ass
oci
atio
n (
NF
PA
) ra
tin
g i
s ob
tain
ed f
rom
htt
p:/
/ww
w.n
fpa.
org
/
2.
Haz
ard
ou
s M
ater
ials
Id
enti
fica
tion
Syst
em (
HM
IS)
rati
ng i
s obta
ined
fro
m h
ttp
://w
ww
.sci
ence
lab
.com
/