SlideShare a Scribd company logo
1 of 29
Photocatalytic Degradation
of Synthetic Wastewaters
Containing Stain
Berat KARATAŞ
Seher Elif MEKİK
THE GOAL OF THE PROJECT
In our project, it was aimed to purify wastewaters containing methylene blue
component and harmful to environment from methylene blue. For this purpose,
synthetic methylene blue waste water was formed and chemically treated by
photocatalysis.
METHOD
• Photocatalysis
Photocatalytic means, in words, self-cleaning with light. Photocatalysis is also a generic term for all of the
methods used in photocatalytic reactions. These methods involve the conversion of the catalysts activated
by ultraviolet light and the harmful substances in the waste water to harmless substances in the
environment in which they are contained.
• Preparation of Standard Solutions
• In order to examine the opening of the methylene blue in the spectrophotometer, a graph of the
absorption and concentration of the methylene blue is needed. For this plot, 7 different standard
solutions were prepared with molarities of 0.005 mM, 0.0075 mM, 0.01 mM, 0.015 mM, 0.02 mM,
0.03 mM, 0.04 mM.
Absorption of these solutions in 660 nm spectrophotometer
it was measured. As a result of this measurement,
and a chart of constants was obtained.
According to the Beer Lambert Act,
the concentration linear equation is as follows
it was found.
y = 40735x + 0,0017
R² = 0,9972
Concentrations using absorption data were obtained by the following example calculation.
y=1.2 (measured absorption)
𝑦 =
(1.2 − 0.0017)
40735
= 2.94 × 10−5
𝑀
• Preparation of Experimental Groups
After removal of the concentration and absorption graph, different experimental groups were prepared and
time-dependent absorption measurements were made. In these experimental groups, pH value is 5 and
temperature is 30-33 oC. There are three variable effects in the preparation of experimental groups; The
choice of light used for catalyst activation, the amount of catalyst and the pollution of the water were
investigated. Four different experimental groups were constructed to measure the effect of these variables on
the photocatalytic reaction.
A) 0.04 mM Methylene Blue + 1 g / L TiO2 Experimental Group
One solution was prepared with 0.04 mM methylene blue and 1 g of TiO2. This solution was left
under the ultraviolet lamp and the photocatalytic reaction was observed.
B) 0.04 mM Methylene Blue + 1 g / L TiO2 Experimental Group
One solution was prepared with 0.04 mM methylene blue and 1 g of TiO2. This solution was left
under the daylight LED lamp and the photocatalytic reaction was observed.
C) 0.08 mM Methylene Blue + 1 g / L TiO2 Experimental Group
One solution was prepared with 0.08 mM methylene blue and 1 g of TiO2. This solution was left
under the ultraviolet lamp and the photocatalytic reaction was observed.
D) 0.04 mM Methylene Blue + 0.5 g / L TiO2 Experimental Group
One solution was prepared with 0.04 mM methylene blue and 0.5 g TiO2. This solution was left
under the ultraviolet lamp and the photocatalytic reaction was observed.
RESULTS
• Finding Speed Equation
In order to have a velocity equation, the reaction reaction grade was separately taken as zero and one
was plotted. Zero and first order reaction reactions were also tried for the three experimental groups
performed under ultraviolet light. Zero and first order reaction equations are given below.
Zero Order Reaction
First Order Reaction
• Parameters to be Compared
Four different experimental groups were constructed to measure the effect of the three variables on
the reaction. The first and second experimental groups were prepared to measure the effect of
ultraviolet light on TiO2 activation. In the first and third experimental groups, the effect of the
amount of methylene blue, that is, the pollution of the water, on the cleaning time was compared. In
the first and fourth experimental groups, the effect of catalyst amounts on cleaning times was
compared.
A) The Impact of the Light Culet
In order to compare the synthetic wastewater prepared with 0.04 mM of methylene blue and 1 g of
TiO2 according to the effect of the light used in the experiment, one was observed under the
ultraviolet light lamp and the other was observed under the daylight LED lamp. Later, time-
dependent graphs were drawn with absorbance and concentration values obtained to compare
ultraviolet light with daylight LED lamp.
Time (min.) Ultraviolet Light - Absorption Ultraviolet Light - Concentration (M) Daylight - Absorption Daylight - Concentration (M)
0 1,627 3,99E-05 1,89 4,64E-05
15 1,336 3,28E-05 1,54 3,78E-05
30 0,602 1,47E-05 1,58 3,87E-05
45 0,45 1,10E-05 1,529 3,75E-05
60 0,449 1,10E-05 1,567 3,84E-05
75 0,312 7,62E-06 1,503 3,69E-05
90 0,328 8,01E-06 1,46 3,58E-05
105 0,246 6,00E-06 1,45 3,56E-05
120 0,098 2,36E-06 1,452 3,56E-05
135 - - 1,347 3,30E-05
150 - - 1,357 3,33E-05
165 - - 1,342 3,29E-05
180 - - 1,369 3,36E-05
195 - - 1,245 3,05E-05
210 - - 1,335 3,27E-05
225 - - 1,274 3,12E-05
240 - - 1,231 3,02E-05
Absorption and concentration values of daylight versus ultraviolet light.
Absorption Chart Concentration Chart
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
2
0 50 100 150 200 250 300
Absorption
Time (min.)
UV Lamp
• Zero-Order Reaction Assumption
Since the obtained equation gives the slope
velocity constant, the velocity constant is
subtracted from the following equation to find
0.3 × 10−6
𝑀 𝑚𝑖𝑛−1
.
𝑦 = −3 × 10−7
𝑥 + 3 × 10−5
• First-Order Reaction Assumption
Since the obtained equation gives the slope
velocity constant, the velocity constant is
found to be 0.02 𝑚𝑖𝑛−1 from the equation
below.
𝑦 = 0.02𝑥 + 0.1071
B) Effect of Methylene Blue Concentration
Synthetic wastewater containing 0.04 mM and 0.08 mM methylene blue was added to 1 g of
TiO2 to effect methylene blue concentration treatment. Then the wastewater was treated
with ultraviolet light. Later, time-dependent graphs were drawn with absorbance and
concentration values obtained to compare methylene blue concentrations.
Time (min.)
0.00004 Methylene Blue -
Absorption
0.00004 Methylene Blue -
Concentration (M)
0.00008 Methylene
Blue -
Absorption
0.00008 Methylene Blue -
Concentration (M)
0 1,627 3,99E-05 2,384 5,85E-05
15 1,336 3,28E-05 1,601 3,93E-05
30 0,602 1,47E-05 1,48 3,63E-05
45 0,45 1,10E-05 1,185 2,90E-05
60 0,449 1,10E-05 1,023 2,51E-05
75 0,312 7,62E-06 1,005 2,46E-05
90 0,328 8,01E-06 0,722 1,77E-05
105 0,246 6,00E-06 0,717 1,76E-05
120 0,098 2,36E-06 0,652 1,60E-05
185 - - 0,12 2,90E-06
200 - - 0,099 2,39E-06
Absorption and concentration values of the comparison of methylene blue
concentrations
Absorption Chart Concentration Chart
• Zero-Order Reaction Assumption
Since the obtained equation gives the slope
velocity constant, the velocity constant is
derived from the following equation and is
found to be 0.2 × 10−6 𝑀 𝑚𝑖𝑛−1.
𝑦 = −2 × 10−7 𝑥 + 4 × 10−5
• First-Order Reaction Assumption
Since the obtained equation gives the
slope velocity constant, the velocity
constant is found as 0.0152 𝑑𝑘−1 from
the equation below.
𝑦 = 0.0152𝑥 − 0.0796
C) Effect of the amount of catalyst (TiO2)
In order to observe the effect of the catalyst in the treatments we made, 1 and 0.5 g of TiO2
were added to the synthetic waste water containing 0.04 mM of methylene blue and two
solutions were formed. These solutions were then subjected to purification by placing them
under the ultraviolet light. Time-dependent graphs were then plotted with the absorption and
concentration values obtained to compare the amount of TiO2.
Time (min.)
1 gram of TiO2 -
Absorption 1 gram of TiO2 - Concentration (M) 0.5 grams of TiO2 - Absorb 0.5 g TiO2 - Concentration (M)
0 1,627 3,99E-05 1,67 4,10E-05
15 1,336 3,28E-05 1,456 3,57E-05
30 0,602 1,47E-05 1,312 3,22E-05
45 0,45 1,10E-05 0,7 1,71E-05
60 0,449 1,10E-05 0,614 1,50E-05
75 0,312 7,62E-06 0,595 1,46E-05
90 0,328 8,01E-06 0,432 1,06E-05
105 0,246 6,00E-06 0,430 1,05E-05
120 0,098 2,36E-06 0,292 7,13E-06
135 0,172 4,18E-06
150 0,094 2,27E-06
Absorption and concentration values of TiO2 content comparison
Absorption Chart Concentration Chart
• Zero-Order Reaction Assumption
Since the obtained equation gives the slope
velocity constant, the velocity constant is
subtracted from the following equation to
find 0.3 × 10−6 𝑀 𝑑𝑘−1.
𝑦 = −3 × 10−7 𝑥 + 4 × 10−5
CONCLUSION AND DISCUSSION
• Two different synthetic wastewater containing 0.04 mM of methylene
blue and 1 g of TiO2 were exposed to ultraviolet light and daylight led
lamp to observe the photocatalytic reaction effect of the light selection.
Compared to these two separate test groups, the synthetic waste water
exposed to ultraviolet light was turned on within 120 minutes, but almost
no opening was observed in the synthetic waste water below the daylight
LED lamp. Thus, ultraviolet light is needed to activate TiO2.
• As the concentration of methylene blue increases, water pollution increases. Photocatalytic
bleaching of synthetic wastewaters containing methylene blue at two different concentrations,
one of which is twice as high as the other, has been observed. As a result, 0.08 mM methylene
blue waste water was opened at 120 minutes while 0.08 mM methylene blue waste water was
opened at 200 minutes. Based on these data, it has been proven that the concentration of the
dyeing substances which give the waste water coloring effect on the photocatalytic process.
• Finally, the effect of the amount of catalyst on the photocatalytic
color development was observed. The methylene blue solution left
to be opened using 1 gram of TiO2 was treated in 120 minutes
while the test group using 0.5 grams took 150 minutes. Accordingly,
the effect of photocatalytic opening of the amount of catalyst was
observed. In addition, since the TiO2 is not soluble in water, it is
expected to precipitate the catalyst while reading the absorption
value, and more waiting time is observed when more catalyst is
used.
• In order to obtain the velocity equation, the reaction was assumed to be zeroth and first order,
and graphs were plotted accordingly. Since R2 on the graph shows the reliability of the
obtained trend line, the speed equation was chosen by choosing the one closest to 1. Given
this situation, the methylene blue photocatalytic reaction was considered as the reaction of the
first order, and the rate constant for the three experimental groups was calculated as follows.
Experimental Speed Constants
methods Experiment Group 1 Experiment Group 2 Experiment Group 3
Zero Order Reaction(M
min-1)
0.3 × 10−6
R2=0.777
0.2
× 10−6 R2=0.879
0.3
× 10−6 R2=0.864
First Order Reaction(min-1)
0.02
R2=0.913
0.015
R2=0.945
0.018
R2=0.949
RECOMMENDATIONS
As a result of our work, we have observed that photocatalysis works for the
treatment of wastewaters containing methylene blue. We can say that this method
can successfully treat other thiazin dyestuffs because it is included in the thiazin
class among the methylene blue dyestuffs and the method we use in our project
purifies the methylene blue.
REFERENCES
• Güler, Ç., Çobanoğlu, Z., (Ankara, 1994) ‘’Su Kirliliği’’
• West, Larry (March 26, 2006). "World Water Day: A Billion People Worldwide Lack Safe Drinking Water".
• Jain, S., Jayaram, R.V., “Removal of Basic Dyes from Aqueous Solution by Low-Cost Adsorbent: Wood Apple Shell (Feronia
Acidissima)”, Desalination , 250 (3), 921-927, 2010.
• http://www.halkevleri.org.tr/basin-aciklamalari/iski-istanbul-halkini-zehirliyor-su-havzalarini-kirletiyor-suyun-ticarilestirilme
• https://biruni.tuik.gov.tr/bolgeselistatistik/degiskenlerUzerindenSorgula.do
• Franca, A.S., Oliveira, L. S., Ferreira, M. E., “Kinetics and Equilibrium Studies of Methylene Blue Adsorption by Spent Coffee
Grounds, Desalination , 249, 267-272, 2009.
• https://pubchem.ncbi.nlm.nih.gov/compound/methylene_blue
• Treatment of pollutants in wastewater: Adsorption of methylene blue onto olive-based activated carbon, Mónica Berrios, María
Ángeles Martín, , Antonio Martín, university of Cordoba (Spain), Department of Inorganic Chemistry and Chemical Engineering,
2011.
• Özkütük, N., (2007). ‘’Ultraviyole Lambaların Kullanımı’’
• https://tr.wikipedia.org/wiki/Spektrometre
• http://www.ledportali.com/isikta-renk-sicakligi-cci/
• http://www.ledportali.com/aydinlatma-icin-isik-renk-sicakligi-secimi/
• https://en.wikipedia.org/wiki/Titanium_dioxide
• Şam, E. D., Ürgen, M., Tepehan, F. Z.,‘’TiO2 Fotokatalistleri’’, İTÜDergisi, 5-6, 81-92, 2007.
• http://www.arokem.com/geri-kazanim-uniteleri/
• https://kimyasimya.blogspot.com.tr/2012/10/fotokataliz.html
• http://www.tekstildershanesi.com.tr/bilgi-deposu/tekstilde-boya-ve-boyarmaddeler-1.html

More Related Content

What's hot

M.TECH final viva voice
M.TECH final viva voiceM.TECH final viva voice
M.TECH final viva voiceGOKUL D
 
Oxidation of Acetaminophen by Fluidized-bed Fenton Process: Optimization usin...
Oxidation of Acetaminophen by Fluidized-bed Fenton Process: Optimization usin...Oxidation of Acetaminophen by Fluidized-bed Fenton Process: Optimization usin...
Oxidation of Acetaminophen by Fluidized-bed Fenton Process: Optimization usin...Oswar Mungkasa
 
IRJET- Colours Removal using Iron Oxide Nano Paarticles
IRJET-  	  Colours Removal using Iron Oxide Nano PaarticlesIRJET-  	  Colours Removal using Iron Oxide Nano Paarticles
IRJET- Colours Removal using Iron Oxide Nano PaarticlesIRJET Journal
 
Removal of chromium (vi) by activated carbon derived from mangifera indica
Removal of chromium (vi) by activated carbon derived from mangifera indicaRemoval of chromium (vi) by activated carbon derived from mangifera indica
Removal of chromium (vi) by activated carbon derived from mangifera indicaeSAT Publishing House
 
77201935
7720193577201935
77201935IJRAT
 
Electro-oxidation And Its Feasibility In Wastewater Treatment
Electro-oxidation And Its Feasibility In Wastewater TreatmentElectro-oxidation And Its Feasibility In Wastewater Treatment
Electro-oxidation And Its Feasibility In Wastewater TreatmentSakib Shahriar
 
Effect of Dye Type on MMT-Supported Pr-Doped TiO2 Composite Photocatalyst
Effect of Dye Type on MMT-Supported Pr-Doped TiO2 Composite PhotocatalystEffect of Dye Type on MMT-Supported Pr-Doped TiO2 Composite Photocatalyst
Effect of Dye Type on MMT-Supported Pr-Doped TiO2 Composite PhotocatalystBasak Otsukarci
 
Adsorptive Removal of Methylene Blue Using Groundnut Shell Activated Carbon C...
Adsorptive Removal of Methylene Blue Using Groundnut Shell Activated Carbon C...Adsorptive Removal of Methylene Blue Using Groundnut Shell Activated Carbon C...
Adsorptive Removal of Methylene Blue Using Groundnut Shell Activated Carbon C...IOSRJAC
 
Adsorption of Methylene Blue From Aqueous Solution with Vermicompost Produced...
Adsorption of Methylene Blue From Aqueous Solution with Vermicompost Produced...Adsorption of Methylene Blue From Aqueous Solution with Vermicompost Produced...
Adsorption of Methylene Blue From Aqueous Solution with Vermicompost Produced...IJMERJOURNAL
 
Treatment of textile wastewater using electrofenton process
Treatment of textile wastewater using electrofenton processTreatment of textile wastewater using electrofenton process
Treatment of textile wastewater using electrofenton processIAEME Publication
 
Degradation of mono azo dye in aqueous solution using
Degradation of mono azo dye in aqueous solution usingDegradation of mono azo dye in aqueous solution using
Degradation of mono azo dye in aqueous solution usingeSAT Publishing House
 
Photocatalysed degradation of a fungicide, thiram in aqueous suspension of ti...
Photocatalysed degradation of a fungicide, thiram in aqueous suspension of ti...Photocatalysed degradation of a fungicide, thiram in aqueous suspension of ti...
Photocatalysed degradation of a fungicide, thiram in aqueous suspension of ti...Siriporn Hassarangsee
 
J.fuel.2015.11.047
J.fuel.2015.11.047J.fuel.2015.11.047
J.fuel.2015.11.047Hameed66
 
Degradation of mono azo dye in aqueous solution using cast iron filings
Degradation of mono azo dye in aqueous solution using cast iron filingsDegradation of mono azo dye in aqueous solution using cast iron filings
Degradation of mono azo dye in aqueous solution using cast iron filingseSAT Journals
 
Lignin isolation from coconut coir, characterization and depolymerization usi...
Lignin isolation from coconut coir, characterization and depolymerization usi...Lignin isolation from coconut coir, characterization and depolymerization usi...
Lignin isolation from coconut coir, characterization and depolymerization usi...Richa Chaudhary
 

What's hot (18)

M.TECH final viva voice
M.TECH final viva voiceM.TECH final viva voice
M.TECH final viva voice
 
Oxidation of Acetaminophen by Fluidized-bed Fenton Process: Optimization usin...
Oxidation of Acetaminophen by Fluidized-bed Fenton Process: Optimization usin...Oxidation of Acetaminophen by Fluidized-bed Fenton Process: Optimization usin...
Oxidation of Acetaminophen by Fluidized-bed Fenton Process: Optimization usin...
 
IRJET- Colours Removal using Iron Oxide Nano Paarticles
IRJET-  	  Colours Removal using Iron Oxide Nano PaarticlesIRJET-  	  Colours Removal using Iron Oxide Nano Paarticles
IRJET- Colours Removal using Iron Oxide Nano Paarticles
 
1.pdf
1.pdf1.pdf
1.pdf
 
Removal of chromium (vi) by activated carbon derived from mangifera indica
Removal of chromium (vi) by activated carbon derived from mangifera indicaRemoval of chromium (vi) by activated carbon derived from mangifera indica
Removal of chromium (vi) by activated carbon derived from mangifera indica
 
77201935
7720193577201935
77201935
 
Electro-oxidation And Its Feasibility In Wastewater Treatment
Electro-oxidation And Its Feasibility In Wastewater TreatmentElectro-oxidation And Its Feasibility In Wastewater Treatment
Electro-oxidation And Its Feasibility In Wastewater Treatment
 
Effect of Dye Type on MMT-Supported Pr-Doped TiO2 Composite Photocatalyst
Effect of Dye Type on MMT-Supported Pr-Doped TiO2 Composite PhotocatalystEffect of Dye Type on MMT-Supported Pr-Doped TiO2 Composite Photocatalyst
Effect of Dye Type on MMT-Supported Pr-Doped TiO2 Composite Photocatalyst
 
Adsorptive Removal of Methylene Blue Using Groundnut Shell Activated Carbon C...
Adsorptive Removal of Methylene Blue Using Groundnut Shell Activated Carbon C...Adsorptive Removal of Methylene Blue Using Groundnut Shell Activated Carbon C...
Adsorptive Removal of Methylene Blue Using Groundnut Shell Activated Carbon C...
 
Adsorption of Methylene Blue From Aqueous Solution with Vermicompost Produced...
Adsorption of Methylene Blue From Aqueous Solution with Vermicompost Produced...Adsorption of Methylene Blue From Aqueous Solution with Vermicompost Produced...
Adsorption of Methylene Blue From Aqueous Solution with Vermicompost Produced...
 
Treatment of textile wastewater using electrofenton process
Treatment of textile wastewater using electrofenton processTreatment of textile wastewater using electrofenton process
Treatment of textile wastewater using electrofenton process
 
Degradation of mono azo dye in aqueous solution using
Degradation of mono azo dye in aqueous solution usingDegradation of mono azo dye in aqueous solution using
Degradation of mono azo dye in aqueous solution using
 
Photocatalysed degradation of a fungicide, thiram in aqueous suspension of ti...
Photocatalysed degradation of a fungicide, thiram in aqueous suspension of ti...Photocatalysed degradation of a fungicide, thiram in aqueous suspension of ti...
Photocatalysed degradation of a fungicide, thiram in aqueous suspension of ti...
 
77494865
7749486577494865
77494865
 
Ijetcas14 550
Ijetcas14 550Ijetcas14 550
Ijetcas14 550
 
J.fuel.2015.11.047
J.fuel.2015.11.047J.fuel.2015.11.047
J.fuel.2015.11.047
 
Degradation of mono azo dye in aqueous solution using cast iron filings
Degradation of mono azo dye in aqueous solution using cast iron filingsDegradation of mono azo dye in aqueous solution using cast iron filings
Degradation of mono azo dye in aqueous solution using cast iron filings
 
Lignin isolation from coconut coir, characterization and depolymerization usi...
Lignin isolation from coconut coir, characterization and depolymerization usi...Lignin isolation from coconut coir, characterization and depolymerization usi...
Lignin isolation from coconut coir, characterization and depolymerization usi...
 

Similar to #scichallenge2017 Photocatalytic Degradation of Synthetic Wastewaters Containing Stain

M.Perez R.Jacobs poster 2015
M.Perez R.Jacobs poster 2015M.Perez R.Jacobs poster 2015
M.Perez R.Jacobs poster 2015Roxanne Jacobs
 
Final Photocatalysis Lab Report (1) (1)
Final Photocatalysis Lab Report (1) (1)Final Photocatalysis Lab Report (1) (1)
Final Photocatalysis Lab Report (1) (1)Henry Hsieh
 
Solvent free synthesis of malonyl chlorides a green chemistry approach
Solvent free synthesis of malonyl chlorides   a green chemistry approachSolvent free synthesis of malonyl chlorides   a green chemistry approach
Solvent free synthesis of malonyl chlorides a green chemistry approacheSAT Journals
 
DISINFECTION OF WATER CONTAINING E. COLI BY PHOTOCATALYTIC ROUTE USING TIO2/...
 DISINFECTION OF WATER CONTAINING E. COLI BY PHOTOCATALYTIC ROUTE USING TIO2/... DISINFECTION OF WATER CONTAINING E. COLI BY PHOTOCATALYTIC ROUTE USING TIO2/...
DISINFECTION OF WATER CONTAINING E. COLI BY PHOTOCATALYTIC ROUTE USING TIO2/...Michael George
 
CONVERSION OF DIMETHYL-NITROBENZENE TO DIMETHY L ANILINE, EFFECT OF SOME PROC...
CONVERSION OF DIMETHYL-NITROBENZENE TO DIMETHY L ANILINE, EFFECT OF SOME PROC...CONVERSION OF DIMETHYL-NITROBENZENE TO DIMETHY L ANILINE, EFFECT OF SOME PROC...
CONVERSION OF DIMETHYL-NITROBENZENE TO DIMETHY L ANILINE, EFFECT OF SOME PROC...Berklin
 
Static mixer as process intensification in photo catalysis
Static mixer as process intensification in photo catalysisStatic mixer as process intensification in photo catalysis
Static mixer as process intensification in photo catalysisPraveenJangid32
 
Stoichiometric-calculations part 2.ppt
Stoichiometric-calculations part 2.pptStoichiometric-calculations part 2.ppt
Stoichiometric-calculations part 2.pptAhmadHashlamon
 
Improving the Synthesis of Lidocaine_2014_Odneal_Aills_Jeffery
Improving the Synthesis of Lidocaine_2014_Odneal_Aills_JefferyImproving the Synthesis of Lidocaine_2014_Odneal_Aills_Jeffery
Improving the Synthesis of Lidocaine_2014_Odneal_Aills_JefferyStephanie Melton
 
Removal of Methylene Blue from Aqueous Solution by Adsorption using Low Cost ...
Removal of Methylene Blue from Aqueous Solution by Adsorption using Low Cost ...Removal of Methylene Blue from Aqueous Solution by Adsorption using Low Cost ...
Removal of Methylene Blue from Aqueous Solution by Adsorption using Low Cost ...ijsrd.com
 
Yogesh Kumar Walia* and Dinesh Kumar Gupta**
Yogesh Kumar Walia* and Dinesh Kumar Gupta**Yogesh Kumar Walia* and Dinesh Kumar Gupta**
Yogesh Kumar Walia* and Dinesh Kumar Gupta**Dheeraj Vasu
 
IRJET- Comparative Study on the Removal of Zinc from Synthetic Wastewater by ...
IRJET- Comparative Study on the Removal of Zinc from Synthetic Wastewater by ...IRJET- Comparative Study on the Removal of Zinc from Synthetic Wastewater by ...
IRJET- Comparative Study on the Removal of Zinc from Synthetic Wastewater by ...IRJET Journal
 
final final accepted-High temperature stability and photocatalytic activity of
final final accepted-High temperature stability and photocatalytic activity offinal final accepted-High temperature stability and photocatalytic activity of
final final accepted-High temperature stability and photocatalytic activity ofnasrollah najibi ilkhchy
 
Equilibrium and kinetic studies on the adsorption of methylene blue from aqueous
Equilibrium and kinetic studies on the adsorption of methylene blue from aqueousEquilibrium and kinetic studies on the adsorption of methylene blue from aqueous
Equilibrium and kinetic studies on the adsorption of methylene blue from aqueoustshankar20134
 
Rate of reaction for limestone citric acid reaction.
Rate of reaction for limestone  citric acid reaction.Rate of reaction for limestone  citric acid reaction.
Rate of reaction for limestone citric acid reaction.dhmcmillan
 
ASYMMETRIC ORGANOCATALYSIS
ASYMMETRIC ORGANOCATALYSISASYMMETRIC ORGANOCATALYSIS
ASYMMETRIC ORGANOCATALYSISBasudeb Mondal
 
Photocatalytic Performance of TiO2 as a Catalyst
Photocatalytic Performance of TiO2 as a CatalystPhotocatalytic Performance of TiO2 as a Catalyst
Photocatalytic Performance of TiO2 as a Catalystmaamirazam
 

Similar to #scichallenge2017 Photocatalytic Degradation of Synthetic Wastewaters Containing Stain (20)

M.Perez R.Jacobs poster 2015
M.Perez R.Jacobs poster 2015M.Perez R.Jacobs poster 2015
M.Perez R.Jacobs poster 2015
 
Final Photocatalysis Lab Report (1) (1)
Final Photocatalysis Lab Report (1) (1)Final Photocatalysis Lab Report (1) (1)
Final Photocatalysis Lab Report (1) (1)
 
Solvent free synthesis of malonyl chlorides a green chemistry approach
Solvent free synthesis of malonyl chlorides   a green chemistry approachSolvent free synthesis of malonyl chlorides   a green chemistry approach
Solvent free synthesis of malonyl chlorides a green chemistry approach
 
final presentation
final presentationfinal presentation
final presentation
 
Titrimetric Methods
Titrimetric Methods Titrimetric Methods
Titrimetric Methods
 
DISINFECTION OF WATER CONTAINING E. COLI BY PHOTOCATALYTIC ROUTE USING TIO2/...
 DISINFECTION OF WATER CONTAINING E. COLI BY PHOTOCATALYTIC ROUTE USING TIO2/... DISINFECTION OF WATER CONTAINING E. COLI BY PHOTOCATALYTIC ROUTE USING TIO2/...
DISINFECTION OF WATER CONTAINING E. COLI BY PHOTOCATALYTIC ROUTE USING TIO2/...
 
CONVERSION OF DIMETHYL-NITROBENZENE TO DIMETHY L ANILINE, EFFECT OF SOME PROC...
CONVERSION OF DIMETHYL-NITROBENZENE TO DIMETHY L ANILINE, EFFECT OF SOME PROC...CONVERSION OF DIMETHYL-NITROBENZENE TO DIMETHY L ANILINE, EFFECT OF SOME PROC...
CONVERSION OF DIMETHYL-NITROBENZENE TO DIMETHY L ANILINE, EFFECT OF SOME PROC...
 
Photochemistry
PhotochemistryPhotochemistry
Photochemistry
 
Static mixer as process intensification in photo catalysis
Static mixer as process intensification in photo catalysisStatic mixer as process intensification in photo catalysis
Static mixer as process intensification in photo catalysis
 
Stoichiometric-calculations part 2.ppt
Stoichiometric-calculations part 2.pptStoichiometric-calculations part 2.ppt
Stoichiometric-calculations part 2.ppt
 
Improving the Synthesis of Lidocaine_2014_Odneal_Aills_Jeffery
Improving the Synthesis of Lidocaine_2014_Odneal_Aills_JefferyImproving the Synthesis of Lidocaine_2014_Odneal_Aills_Jeffery
Improving the Synthesis of Lidocaine_2014_Odneal_Aills_Jeffery
 
Removal of Methylene Blue from Aqueous Solution by Adsorption using Low Cost ...
Removal of Methylene Blue from Aqueous Solution by Adsorption using Low Cost ...Removal of Methylene Blue from Aqueous Solution by Adsorption using Low Cost ...
Removal of Methylene Blue from Aqueous Solution by Adsorption using Low Cost ...
 
Yogesh Kumar Walia* and Dinesh Kumar Gupta**
Yogesh Kumar Walia* and Dinesh Kumar Gupta**Yogesh Kumar Walia* and Dinesh Kumar Gupta**
Yogesh Kumar Walia* and Dinesh Kumar Gupta**
 
IRJET- Comparative Study on the Removal of Zinc from Synthetic Wastewater by ...
IRJET- Comparative Study on the Removal of Zinc from Synthetic Wastewater by ...IRJET- Comparative Study on the Removal of Zinc from Synthetic Wastewater by ...
IRJET- Comparative Study on the Removal of Zinc from Synthetic Wastewater by ...
 
E0432733
E0432733E0432733
E0432733
 
final final accepted-High temperature stability and photocatalytic activity of
final final accepted-High temperature stability and photocatalytic activity offinal final accepted-High temperature stability and photocatalytic activity of
final final accepted-High temperature stability and photocatalytic activity of
 
Equilibrium and kinetic studies on the adsorption of methylene blue from aqueous
Equilibrium and kinetic studies on the adsorption of methylene blue from aqueousEquilibrium and kinetic studies on the adsorption of methylene blue from aqueous
Equilibrium and kinetic studies on the adsorption of methylene blue from aqueous
 
Rate of reaction for limestone citric acid reaction.
Rate of reaction for limestone  citric acid reaction.Rate of reaction for limestone  citric acid reaction.
Rate of reaction for limestone citric acid reaction.
 
ASYMMETRIC ORGANOCATALYSIS
ASYMMETRIC ORGANOCATALYSISASYMMETRIC ORGANOCATALYSIS
ASYMMETRIC ORGANOCATALYSIS
 
Photocatalytic Performance of TiO2 as a Catalyst
Photocatalytic Performance of TiO2 as a CatalystPhotocatalytic Performance of TiO2 as a Catalyst
Photocatalytic Performance of TiO2 as a Catalyst
 

Recently uploaded

human computer interaction of movie booking system project
human computer interaction of movie booking system projecthuman computer interaction of movie booking system project
human computer interaction of movie booking system project201roopikha
 
CCXG global forum, April 2024, Sirini Jeudy-Hugo
CCXG global forum, April 2024,  Sirini Jeudy-HugoCCXG global forum, April 2024,  Sirini Jeudy-Hugo
CCXG global forum, April 2024, Sirini Jeudy-HugoOECD Environment
 
CCXG global forum, April 2024, Chiara Falduto
CCXG global forum, April 2024, Chiara FaldutoCCXG global forum, April 2024, Chiara Falduto
CCXG global forum, April 2024, Chiara FaldutoOECD Environment
 
CCXG global forum, April 2024, Amar Bhattacharya
CCXG global forum, April 2024,  Amar BhattacharyaCCXG global forum, April 2024,  Amar Bhattacharya
CCXG global forum, April 2024, Amar BhattacharyaOECD Environment
 
CCXG global forum, April 2024, Mentimeter results
CCXG global forum, April 2024, Mentimeter resultsCCXG global forum, April 2024, Mentimeter results
CCXG global forum, April 2024, Mentimeter resultsOECD Environment
 
CCXG global forum, April 2024, Surabi Menon
CCXG global forum, April 2024, Surabi MenonCCXG global forum, April 2024, Surabi Menon
CCXG global forum, April 2024, Surabi MenonOECD Environment
 
CCXG global forum, April 2024, Raphaël Jachnik
CCXG global forum, April 2024, Raphaël JachnikCCXG global forum, April 2024, Raphaël Jachnik
CCXG global forum, April 2024, Raphaël JachnikOECD Environment
 
https://www.facebook.com/people/Proper-Keto-Capsules-UK/61557989683758/
https://www.facebook.com/people/Proper-Keto-Capsules-UK/61557989683758/https://www.facebook.com/people/Proper-Keto-Capsules-UK/61557989683758/
https://www.facebook.com/people/Proper-Keto-Capsules-UK/61557989683758/dikjog
 
Uae-NO1 Black Magic Specialist Expert In Bahawalpur, Sargodha, Sialkot, Sheik...
Uae-NO1 Black Magic Specialist Expert In Bahawalpur, Sargodha, Sialkot, Sheik...Uae-NO1 Black Magic Specialist Expert In Bahawalpur, Sargodha, Sialkot, Sheik...
Uae-NO1 Black Magic Specialist Expert In Bahawalpur, Sargodha, Sialkot, Sheik...Amil baba
 
CCXG global forum, April 2024, Annett Möhner
CCXG global forum, April 2024,  Annett MöhnerCCXG global forum, April 2024,  Annett Möhner
CCXG global forum, April 2024, Annett MöhnerOECD Environment
 
CCXG global forum, April 2024, Jolien Noels
CCXG global forum, April 2024,  Jolien NoelsCCXG global forum, April 2024,  Jolien Noels
CCXG global forum, April 2024, Jolien NoelsOECD Environment
 
_International World Heritage Day by Slidesgo.pptx
_International World Heritage Day by Slidesgo.pptx_International World Heritage Day by Slidesgo.pptx
_International World Heritage Day by Slidesgo.pptxsnehalshah72
 
CCXG global forum, April 2024, Beatrice Cyiza
CCXG global forum, April 2024,  Beatrice CyizaCCXG global forum, April 2024,  Beatrice Cyiza
CCXG global forum, April 2024, Beatrice CyizaOECD Environment
 
CCXG global forum, April 2024, Thomas Spencer
CCXG global forum, April 2024,  Thomas SpencerCCXG global forum, April 2024,  Thomas Spencer
CCXG global forum, April 2024, Thomas SpencerOECD Environment
 
CCXG global forum, April 2024, Alban Kitous
CCXG global forum, April 2024,  Alban KitousCCXG global forum, April 2024,  Alban Kitous
CCXG global forum, April 2024, Alban KitousOECD Environment
 
CCXG global forum, April 2024, Siddharth Singh
CCXG global forum, April 2024, Siddharth SinghCCXG global forum, April 2024, Siddharth Singh
CCXG global forum, April 2024, Siddharth SinghOECD Environment
 
CCXG global forum, April 2024, Geert Fremout
CCXG global forum, April 2024,  Geert FremoutCCXG global forum, April 2024,  Geert Fremout
CCXG global forum, April 2024, Geert FremoutOECD Environment
 
CCXG global forum, April 2024, David Mutisya
CCXG global forum, April 2024,  David MutisyaCCXG global forum, April 2024,  David Mutisya
CCXG global forum, April 2024, David MutisyaOECD Environment
 
CCXG global forum, April 2025, Key takeaways
CCXG global forum, April 2025, Key takeawaysCCXG global forum, April 2025, Key takeaways
CCXG global forum, April 2025, Key takeawaysOECD Environment
 
Title-Role of forestry in restoration of degraded lands.pptx
Title-Role of forestry in restoration of degraded lands.pptxTitle-Role of forestry in restoration of degraded lands.pptx
Title-Role of forestry in restoration of degraded lands.pptxSagar Chaudhary
 

Recently uploaded (20)

human computer interaction of movie booking system project
human computer interaction of movie booking system projecthuman computer interaction of movie booking system project
human computer interaction of movie booking system project
 
CCXG global forum, April 2024, Sirini Jeudy-Hugo
CCXG global forum, April 2024,  Sirini Jeudy-HugoCCXG global forum, April 2024,  Sirini Jeudy-Hugo
CCXG global forum, April 2024, Sirini Jeudy-Hugo
 
CCXG global forum, April 2024, Chiara Falduto
CCXG global forum, April 2024, Chiara FaldutoCCXG global forum, April 2024, Chiara Falduto
CCXG global forum, April 2024, Chiara Falduto
 
CCXG global forum, April 2024, Amar Bhattacharya
CCXG global forum, April 2024,  Amar BhattacharyaCCXG global forum, April 2024,  Amar Bhattacharya
CCXG global forum, April 2024, Amar Bhattacharya
 
CCXG global forum, April 2024, Mentimeter results
CCXG global forum, April 2024, Mentimeter resultsCCXG global forum, April 2024, Mentimeter results
CCXG global forum, April 2024, Mentimeter results
 
CCXG global forum, April 2024, Surabi Menon
CCXG global forum, April 2024, Surabi MenonCCXG global forum, April 2024, Surabi Menon
CCXG global forum, April 2024, Surabi Menon
 
CCXG global forum, April 2024, Raphaël Jachnik
CCXG global forum, April 2024, Raphaël JachnikCCXG global forum, April 2024, Raphaël Jachnik
CCXG global forum, April 2024, Raphaël Jachnik
 
https://www.facebook.com/people/Proper-Keto-Capsules-UK/61557989683758/
https://www.facebook.com/people/Proper-Keto-Capsules-UK/61557989683758/https://www.facebook.com/people/Proper-Keto-Capsules-UK/61557989683758/
https://www.facebook.com/people/Proper-Keto-Capsules-UK/61557989683758/
 
Uae-NO1 Black Magic Specialist Expert In Bahawalpur, Sargodha, Sialkot, Sheik...
Uae-NO1 Black Magic Specialist Expert In Bahawalpur, Sargodha, Sialkot, Sheik...Uae-NO1 Black Magic Specialist Expert In Bahawalpur, Sargodha, Sialkot, Sheik...
Uae-NO1 Black Magic Specialist Expert In Bahawalpur, Sargodha, Sialkot, Sheik...
 
CCXG global forum, April 2024, Annett Möhner
CCXG global forum, April 2024,  Annett MöhnerCCXG global forum, April 2024,  Annett Möhner
CCXG global forum, April 2024, Annett Möhner
 
CCXG global forum, April 2024, Jolien Noels
CCXG global forum, April 2024,  Jolien NoelsCCXG global forum, April 2024,  Jolien Noels
CCXG global forum, April 2024, Jolien Noels
 
_International World Heritage Day by Slidesgo.pptx
_International World Heritage Day by Slidesgo.pptx_International World Heritage Day by Slidesgo.pptx
_International World Heritage Day by Slidesgo.pptx
 
CCXG global forum, April 2024, Beatrice Cyiza
CCXG global forum, April 2024,  Beatrice CyizaCCXG global forum, April 2024,  Beatrice Cyiza
CCXG global forum, April 2024, Beatrice Cyiza
 
CCXG global forum, April 2024, Thomas Spencer
CCXG global forum, April 2024,  Thomas SpencerCCXG global forum, April 2024,  Thomas Spencer
CCXG global forum, April 2024, Thomas Spencer
 
CCXG global forum, April 2024, Alban Kitous
CCXG global forum, April 2024,  Alban KitousCCXG global forum, April 2024,  Alban Kitous
CCXG global forum, April 2024, Alban Kitous
 
CCXG global forum, April 2024, Siddharth Singh
CCXG global forum, April 2024, Siddharth SinghCCXG global forum, April 2024, Siddharth Singh
CCXG global forum, April 2024, Siddharth Singh
 
CCXG global forum, April 2024, Geert Fremout
CCXG global forum, April 2024,  Geert FremoutCCXG global forum, April 2024,  Geert Fremout
CCXG global forum, April 2024, Geert Fremout
 
CCXG global forum, April 2024, David Mutisya
CCXG global forum, April 2024,  David MutisyaCCXG global forum, April 2024,  David Mutisya
CCXG global forum, April 2024, David Mutisya
 
CCXG global forum, April 2025, Key takeaways
CCXG global forum, April 2025, Key takeawaysCCXG global forum, April 2025, Key takeaways
CCXG global forum, April 2025, Key takeaways
 
Title-Role of forestry in restoration of degraded lands.pptx
Title-Role of forestry in restoration of degraded lands.pptxTitle-Role of forestry in restoration of degraded lands.pptx
Title-Role of forestry in restoration of degraded lands.pptx
 

#scichallenge2017 Photocatalytic Degradation of Synthetic Wastewaters Containing Stain

  • 1. Photocatalytic Degradation of Synthetic Wastewaters Containing Stain Berat KARATAŞ Seher Elif MEKİK
  • 2. THE GOAL OF THE PROJECT In our project, it was aimed to purify wastewaters containing methylene blue component and harmful to environment from methylene blue. For this purpose, synthetic methylene blue waste water was formed and chemically treated by photocatalysis.
  • 3. METHOD • Photocatalysis Photocatalytic means, in words, self-cleaning with light. Photocatalysis is also a generic term for all of the methods used in photocatalytic reactions. These methods involve the conversion of the catalysts activated by ultraviolet light and the harmful substances in the waste water to harmless substances in the environment in which they are contained.
  • 4. • Preparation of Standard Solutions • In order to examine the opening of the methylene blue in the spectrophotometer, a graph of the absorption and concentration of the methylene blue is needed. For this plot, 7 different standard solutions were prepared with molarities of 0.005 mM, 0.0075 mM, 0.01 mM, 0.015 mM, 0.02 mM, 0.03 mM, 0.04 mM.
  • 5. Absorption of these solutions in 660 nm spectrophotometer it was measured. As a result of this measurement, and a chart of constants was obtained. According to the Beer Lambert Act, the concentration linear equation is as follows it was found. y = 40735x + 0,0017 R² = 0,9972 Concentrations using absorption data were obtained by the following example calculation. y=1.2 (measured absorption) 𝑦 = (1.2 − 0.0017) 40735 = 2.94 × 10−5 𝑀
  • 6. • Preparation of Experimental Groups After removal of the concentration and absorption graph, different experimental groups were prepared and time-dependent absorption measurements were made. In these experimental groups, pH value is 5 and temperature is 30-33 oC. There are three variable effects in the preparation of experimental groups; The choice of light used for catalyst activation, the amount of catalyst and the pollution of the water were investigated. Four different experimental groups were constructed to measure the effect of these variables on the photocatalytic reaction.
  • 7. A) 0.04 mM Methylene Blue + 1 g / L TiO2 Experimental Group One solution was prepared with 0.04 mM methylene blue and 1 g of TiO2. This solution was left under the ultraviolet lamp and the photocatalytic reaction was observed. B) 0.04 mM Methylene Blue + 1 g / L TiO2 Experimental Group One solution was prepared with 0.04 mM methylene blue and 1 g of TiO2. This solution was left under the daylight LED lamp and the photocatalytic reaction was observed. C) 0.08 mM Methylene Blue + 1 g / L TiO2 Experimental Group One solution was prepared with 0.08 mM methylene blue and 1 g of TiO2. This solution was left under the ultraviolet lamp and the photocatalytic reaction was observed. D) 0.04 mM Methylene Blue + 0.5 g / L TiO2 Experimental Group One solution was prepared with 0.04 mM methylene blue and 0.5 g TiO2. This solution was left under the ultraviolet lamp and the photocatalytic reaction was observed.
  • 8. RESULTS • Finding Speed Equation In order to have a velocity equation, the reaction reaction grade was separately taken as zero and one was plotted. Zero and first order reaction reactions were also tried for the three experimental groups performed under ultraviolet light. Zero and first order reaction equations are given below. Zero Order Reaction First Order Reaction
  • 9. • Parameters to be Compared Four different experimental groups were constructed to measure the effect of the three variables on the reaction. The first and second experimental groups were prepared to measure the effect of ultraviolet light on TiO2 activation. In the first and third experimental groups, the effect of the amount of methylene blue, that is, the pollution of the water, on the cleaning time was compared. In the first and fourth experimental groups, the effect of catalyst amounts on cleaning times was compared. A) The Impact of the Light Culet In order to compare the synthetic wastewater prepared with 0.04 mM of methylene blue and 1 g of TiO2 according to the effect of the light used in the experiment, one was observed under the ultraviolet light lamp and the other was observed under the daylight LED lamp. Later, time- dependent graphs were drawn with absorbance and concentration values obtained to compare ultraviolet light with daylight LED lamp.
  • 10. Time (min.) Ultraviolet Light - Absorption Ultraviolet Light - Concentration (M) Daylight - Absorption Daylight - Concentration (M) 0 1,627 3,99E-05 1,89 4,64E-05 15 1,336 3,28E-05 1,54 3,78E-05 30 0,602 1,47E-05 1,58 3,87E-05 45 0,45 1,10E-05 1,529 3,75E-05 60 0,449 1,10E-05 1,567 3,84E-05 75 0,312 7,62E-06 1,503 3,69E-05 90 0,328 8,01E-06 1,46 3,58E-05 105 0,246 6,00E-06 1,45 3,56E-05 120 0,098 2,36E-06 1,452 3,56E-05 135 - - 1,347 3,30E-05 150 - - 1,357 3,33E-05 165 - - 1,342 3,29E-05 180 - - 1,369 3,36E-05 195 - - 1,245 3,05E-05 210 - - 1,335 3,27E-05 225 - - 1,274 3,12E-05 240 - - 1,231 3,02E-05 Absorption and concentration values of daylight versus ultraviolet light.
  • 11. Absorption Chart Concentration Chart 0 0.2 0.4 0.6 0.8 1 1.2 1.4 1.6 1.8 2 0 50 100 150 200 250 300 Absorption Time (min.) UV Lamp
  • 12. • Zero-Order Reaction Assumption Since the obtained equation gives the slope velocity constant, the velocity constant is subtracted from the following equation to find 0.3 × 10−6 𝑀 𝑚𝑖𝑛−1 . 𝑦 = −3 × 10−7 𝑥 + 3 × 10−5
  • 13. • First-Order Reaction Assumption Since the obtained equation gives the slope velocity constant, the velocity constant is found to be 0.02 𝑚𝑖𝑛−1 from the equation below. 𝑦 = 0.02𝑥 + 0.1071
  • 14. B) Effect of Methylene Blue Concentration Synthetic wastewater containing 0.04 mM and 0.08 mM methylene blue was added to 1 g of TiO2 to effect methylene blue concentration treatment. Then the wastewater was treated with ultraviolet light. Later, time-dependent graphs were drawn with absorbance and concentration values obtained to compare methylene blue concentrations.
  • 15. Time (min.) 0.00004 Methylene Blue - Absorption 0.00004 Methylene Blue - Concentration (M) 0.00008 Methylene Blue - Absorption 0.00008 Methylene Blue - Concentration (M) 0 1,627 3,99E-05 2,384 5,85E-05 15 1,336 3,28E-05 1,601 3,93E-05 30 0,602 1,47E-05 1,48 3,63E-05 45 0,45 1,10E-05 1,185 2,90E-05 60 0,449 1,10E-05 1,023 2,51E-05 75 0,312 7,62E-06 1,005 2,46E-05 90 0,328 8,01E-06 0,722 1,77E-05 105 0,246 6,00E-06 0,717 1,76E-05 120 0,098 2,36E-06 0,652 1,60E-05 185 - - 0,12 2,90E-06 200 - - 0,099 2,39E-06 Absorption and concentration values of the comparison of methylene blue concentrations
  • 17. • Zero-Order Reaction Assumption Since the obtained equation gives the slope velocity constant, the velocity constant is derived from the following equation and is found to be 0.2 × 10−6 𝑀 𝑚𝑖𝑛−1. 𝑦 = −2 × 10−7 𝑥 + 4 × 10−5
  • 18. • First-Order Reaction Assumption Since the obtained equation gives the slope velocity constant, the velocity constant is found as 0.0152 𝑑𝑘−1 from the equation below. 𝑦 = 0.0152𝑥 − 0.0796
  • 19. C) Effect of the amount of catalyst (TiO2) In order to observe the effect of the catalyst in the treatments we made, 1 and 0.5 g of TiO2 were added to the synthetic waste water containing 0.04 mM of methylene blue and two solutions were formed. These solutions were then subjected to purification by placing them under the ultraviolet light. Time-dependent graphs were then plotted with the absorption and concentration values obtained to compare the amount of TiO2.
  • 20. Time (min.) 1 gram of TiO2 - Absorption 1 gram of TiO2 - Concentration (M) 0.5 grams of TiO2 - Absorb 0.5 g TiO2 - Concentration (M) 0 1,627 3,99E-05 1,67 4,10E-05 15 1,336 3,28E-05 1,456 3,57E-05 30 0,602 1,47E-05 1,312 3,22E-05 45 0,45 1,10E-05 0,7 1,71E-05 60 0,449 1,10E-05 0,614 1,50E-05 75 0,312 7,62E-06 0,595 1,46E-05 90 0,328 8,01E-06 0,432 1,06E-05 105 0,246 6,00E-06 0,430 1,05E-05 120 0,098 2,36E-06 0,292 7,13E-06 135 0,172 4,18E-06 150 0,094 2,27E-06 Absorption and concentration values of TiO2 content comparison
  • 22. • Zero-Order Reaction Assumption Since the obtained equation gives the slope velocity constant, the velocity constant is subtracted from the following equation to find 0.3 × 10−6 𝑀 𝑑𝑘−1. 𝑦 = −3 × 10−7 𝑥 + 4 × 10−5
  • 23.
  • 24. CONCLUSION AND DISCUSSION • Two different synthetic wastewater containing 0.04 mM of methylene blue and 1 g of TiO2 were exposed to ultraviolet light and daylight led lamp to observe the photocatalytic reaction effect of the light selection. Compared to these two separate test groups, the synthetic waste water exposed to ultraviolet light was turned on within 120 minutes, but almost no opening was observed in the synthetic waste water below the daylight LED lamp. Thus, ultraviolet light is needed to activate TiO2.
  • 25. • As the concentration of methylene blue increases, water pollution increases. Photocatalytic bleaching of synthetic wastewaters containing methylene blue at two different concentrations, one of which is twice as high as the other, has been observed. As a result, 0.08 mM methylene blue waste water was opened at 120 minutes while 0.08 mM methylene blue waste water was opened at 200 minutes. Based on these data, it has been proven that the concentration of the dyeing substances which give the waste water coloring effect on the photocatalytic process.
  • 26. • Finally, the effect of the amount of catalyst on the photocatalytic color development was observed. The methylene blue solution left to be opened using 1 gram of TiO2 was treated in 120 minutes while the test group using 0.5 grams took 150 minutes. Accordingly, the effect of photocatalytic opening of the amount of catalyst was observed. In addition, since the TiO2 is not soluble in water, it is expected to precipitate the catalyst while reading the absorption value, and more waiting time is observed when more catalyst is used.
  • 27. • In order to obtain the velocity equation, the reaction was assumed to be zeroth and first order, and graphs were plotted accordingly. Since R2 on the graph shows the reliability of the obtained trend line, the speed equation was chosen by choosing the one closest to 1. Given this situation, the methylene blue photocatalytic reaction was considered as the reaction of the first order, and the rate constant for the three experimental groups was calculated as follows. Experimental Speed Constants methods Experiment Group 1 Experiment Group 2 Experiment Group 3 Zero Order Reaction(M min-1) 0.3 × 10−6 R2=0.777 0.2 × 10−6 R2=0.879 0.3 × 10−6 R2=0.864 First Order Reaction(min-1) 0.02 R2=0.913 0.015 R2=0.945 0.018 R2=0.949
  • 28. RECOMMENDATIONS As a result of our work, we have observed that photocatalysis works for the treatment of wastewaters containing methylene blue. We can say that this method can successfully treat other thiazin dyestuffs because it is included in the thiazin class among the methylene blue dyestuffs and the method we use in our project purifies the methylene blue.
  • 29. REFERENCES • Güler, Ç., Çobanoğlu, Z., (Ankara, 1994) ‘’Su Kirliliği’’ • West, Larry (March 26, 2006). "World Water Day: A Billion People Worldwide Lack Safe Drinking Water". • Jain, S., Jayaram, R.V., “Removal of Basic Dyes from Aqueous Solution by Low-Cost Adsorbent: Wood Apple Shell (Feronia Acidissima)”, Desalination , 250 (3), 921-927, 2010. • http://www.halkevleri.org.tr/basin-aciklamalari/iski-istanbul-halkini-zehirliyor-su-havzalarini-kirletiyor-suyun-ticarilestirilme • https://biruni.tuik.gov.tr/bolgeselistatistik/degiskenlerUzerindenSorgula.do • Franca, A.S., Oliveira, L. S., Ferreira, M. E., “Kinetics and Equilibrium Studies of Methylene Blue Adsorption by Spent Coffee Grounds, Desalination , 249, 267-272, 2009. • https://pubchem.ncbi.nlm.nih.gov/compound/methylene_blue • Treatment of pollutants in wastewater: Adsorption of methylene blue onto olive-based activated carbon, Mónica Berrios, María Ángeles Martín, , Antonio Martín, university of Cordoba (Spain), Department of Inorganic Chemistry and Chemical Engineering, 2011. • Özkütük, N., (2007). ‘’Ultraviyole Lambaların Kullanımı’’ • https://tr.wikipedia.org/wiki/Spektrometre • http://www.ledportali.com/isikta-renk-sicakligi-cci/ • http://www.ledportali.com/aydinlatma-icin-isik-renk-sicakligi-secimi/ • https://en.wikipedia.org/wiki/Titanium_dioxide • Şam, E. D., Ürgen, M., Tepehan, F. Z.,‘’TiO2 Fotokatalistleri’’, İTÜDergisi, 5-6, 81-92, 2007. • http://www.arokem.com/geri-kazanim-uniteleri/ • https://kimyasimya.blogspot.com.tr/2012/10/fotokataliz.html • http://www.tekstildershanesi.com.tr/bilgi-deposu/tekstilde-boya-ve-boyarmaddeler-1.html