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Photocatalysts - Science topic
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Questions related to Photocatalysts
In my case dimethylformamide was used as the solvent and an equimolar solution of methyl methacrylate and ethyl methacrylate was used. Moreover, the photocatalyst that was used was Tris(2,2'-bipyridil) dichloruthenium (II) hexahydrate.
Can someone assist with the primary differences between the Z-scheme and S-scheme photocatalyst, based on their charge transfer mechanisms/routes. Many research and review papers are unclear in explaining the two systems.
Sir/Madam,
As per Overall Water Splitting (OWS) discussion:
Mostly, Z-scheme concept is utilized in the photocatalyst sheet applications. Is there any other photocatalyst concept (such like Type-II heterojunction or S-scheme) is valid for the over all water splitting process?
Please share the good reference for related concept.
I am studying Master of Science in Chemical Engineering and I need some advice on new topics in chemical engineering. I want to choose my master thesis and I want to choose new topics in my research interests( wastewater treatment, sustainability, photocatalyst, renewable energy, energy conversion).
I am eager to know your thoughts on the selection of the master thesis.
I observed an increment in the absorbance of chloramphenicol using a UV spectrophotometer.
One reviewer asked me (One cannot understand the bandgap of a composite like g-C3N4/Fe3O4/Bi2WO6/Bi2S3. Does the derived bandgap of the g-C3N4/Fe3O4/Bi2WO6/Bi2S3 composite represent the bandgap of g-C3N4, Fe3O4, Bi2WO6, Bi2S3 or others? Please clarify it??)
Please, anyone can answer?
I'm going to do a test with radical inhibitors on my photocatalyst, but I'm not sure about the comparison. Should I compare the test results with the pure dye or with the dye + photocatalyst? Also, should the test be done in the dark and under light or only under light?
Dear colleagues,
i have performed the decoloration of MB using a photocatalyst but the COD experiment for all the samples read under range what is the wrong in my Experiment?
Best Regards
Huda
Photocatalyst uses ultra-violet radiation to active a catalyst and occurs a chemical reaction. Experimentally, the use of UV source is very dangerous for health. A lot of precautions are considered for using UV source. Hence, i would like to use a heat activated catalyst to generate *OH.
Thanks to all.
My designed photocatalyst changes the color of the simulated wastewater solution from bright yellow to dark brown/black. Neither centrifugation nor filtration can eliminate the photocatalyst from the solution after the 180-minute photocatalytic degradation period ends. The new solution color or remaining photocatalysts then provide an inaccurate absorbance peak in the UV spectrophotometer. What should I do to resolve the issue?
0.1mg/l is used to degrade 10mg/l solution(RhB) under white light irradiation at room temperature, ph 3 and contineous magnetic stirring during irradiation in doubled layered glass reactor with coooling system throughout the experiment.
How to prepare a photocatalyst with both good crystallinity and large surface area? Is it possible to improve the crystallinity of a photocatalyst by calcination without decreasing the BET surface area of a photocatalyst or even increase the BET surface area?
Can anybody share a comprehensive study on the comparison of light sources (lamp name with power value, manufacturing company, and associated wavelength range) with that of photocatalytic performance. However, sharing the comparison with sunlight is highly encouraged.
Sharing of general opinions by field researchers are warmly welcomed, positively.
Hi all! There is something that always calls my attention when I am working with Eosin Y, an organic dye and a photocatalyst. The color of its solutions depends on the concentration and the solvent. But also, and homogeneous solution in water/tBuOH, for example, is orange within the body but pink on the edge of the solution!
If you have any comments, want to share your experience I would appreciate it.
Thanks in advance!
Leo!
Hi,
Does the photocatalysts have their own life-time? Does the electrons in the photocatalyst will be used up during the photocatalysis reaction?
Thank you
Is there any previous research show that co-doping for TiO2/ZnO nanocomposite photocatalyst is better than single doped?
Various literature have hinted that "n" in Tauc equation, (αhυ) 1/n = k (hυ- Eg), is determined based on the nature of the electronic transition.
Why the Tauc exponent (n) for allowed direct and indirect transitions are equal to 1/2 and 2, respectively? Where do these values come from?
Thank you
How significant is the FTIR study of mixed metal oxide photocatalysts like WO3-TiO2 nanocomposites?
I have a electro fenton system that cathode electrode is graphite and anode is FTO coated with a photocatalyst . when i want to increase current density to upper limit, suddenly deposited layer was being separated uniformly from FTO anode via oxygen releasing from anode surface .
anode surface pre treatment(degreasing with ethanol and functionalization with HNO3) was done before layer deposition and annealing after deposition . would you please help my how can i prevent from separation of deposited layer on anode surface?
Which photocatalysts will be preferred for better efficiency? Metal-doped or Non-metal doped?
I have been reading a lot of papers on either side of the spectrum but have been finding it difficult how to understand which is which.
Can someone post a review or book or any piece of the written document as to how we can differentiate the two of them concerning photocatalytic reactions?
Titanium oxide technical grda contains aluminium oxide and silica oxide. It is also resistant to dissolving in most solvents. I would like to increase the percentage of titanium oxide for use as a photocatalyst
In the preparation of g-C3N4/BiFeO3 photocatalyst, a number of papers mention words like 'certain/appropriate' amount for chemical agents. Can anyone tell what this amount actually is?
Reference papers:
1. Wang, X., Mao, W., Zhang, J., Han, Y., Quan, C., & Zhang, Q. et al. (2015). Facile fabrication of highly efficient g-C3N4/BiFeO3 nanocomposites with enhanced visible light photocatalytic activities. Journal Of Colloid And Interface Science, 448, 17-23. doi: 10.1016/j.jcis.2015.01.090
2. An, J., Zhang, G., Zheng, R., & Wang, P. (2016). Removing lignin model pollutants with BiFeO 3 –g-C 3 N 4 compound as an efficient visible-light-heterogeneous Fenton-like catalyst. Journal Of Environmental Sciences, 48, 218-229. doi: 10.1016/j.jes.2016.01.024
Hello everyone
I'm working on photocatalysts based on g-C3N4 and Co3O4 and the junction formed seems to be type II. Is there any method to make sure that the junction formed is a scheme junction?
Best regards.
I had prepared 50ml of 20,25,30,35 and 40 ppm of eriochrome black T and add 25mg of copper sulphide as photocatalyst with stirring under dark for an hour then under light for 2hours the resulted data were 99.7,99,57, 43.25 and 37.22%. Iwanna ask why this sharp decrease occurred?
Hello everyone.
I am preparing photocatalysts based on g-C3N4 and Co3O4, but the junction formed is type II, is there any method to make sure that the junction formed is s scheme junction.
I came across papers where researchers have used multiple polymers including both synthetic and natural for synthesizing electrospun nanofibers. But if we use these nanofibers in photocatalytic applications like degradation the polymer gets evaporated during calcination because we have to use the photocatalyst in powder form. So what remains the purpose of using multiple polymers?
The concentration of aqueous solution of ibuprofen can be measured by using UV-VIS?
I am working on the photodegradation of pharmaceuticals using iron oxide as a photocatalyst, but instead of having a decrease, there is an increase in absorption.
Please suggest a method to determine this practically. Please avoid mentioning the publications having the final results. The guidelines or procedure for measurement is required. Any related discussion or fruitful comments are warmly welcomed.
Iam using photocatalyst for photodegrade phenolphethalien in alkaline medium but the fading of phenolphethalien color with time cause aproblem in monitoring %R making me not know this percent due to fading or degradation I had tried for more times but the PH decrease and the color fading with time
when i add soda after the reaction the solution turned to pink
please any one can help me in this problem?
When I carried out the active species capture experiments to study the photocatalytic mechanism, I found that the amount of capture agents was different in different work, for example, in a paper, EDTA 1 mmol/L, tert-butyl alcohol (BuOH) 5 mmol/L and p-benzoquinone (BZQ) 1 mmol/L, but in another paper, their amounts are all 1mmol/l. This really confuses me, I don't know how to select the amount of capture agents in my experiments, especially for BuOH.
What do you think of this problem? Is there a general test standard or reference?
Thank you very much for your suggestions and answers.
The photo-stability and reusability properties are very crucial factors for photocatalysts for their large-scale application (Zeng et al., 2017; Huo et al., 2018).
Reference should appear like this in text
Zeng, C., Hu, Y., Huang, H., 2017. BiOBr0.75I0.25/BiOIO3 as a novel heterojunctional photocatalyst with superior visible-light-driven photocatalytic activity in removing diverse industrial pollutants. ACS Sustain. Chem. Eng. 5, 3897e3905.
The photo-stability and reusability properties are very crucial factors for photocatalysts for their large-scale application (Zeng et al., 2017; Huo et al., 2018). Reference should appear like this in text Zeng, C., Hu, Y., Huang, H., 2017. BiOBr0.75I0.25/BiOIO3 as a novel heterojunctional photocatalyst with superior visible-light-driven photocatalytic activity in removing diverse industrial pollutants. ACS Sustain. Chem. Eng. 5, 3897e3905.
After each cycle of usage of a photocatalyst for exampe in dye degradation how to recover the photocatalyst and use it further in other cycle?
MgO has a high energy band gap (7.1 eV) and is supposed to not be capable of acting as a photocatalyst. So how does this happen??
We are not sure whether our photocatalyst is a perfectly soluble complex or an aggregation of very small nanoparticles, or even something in between like a cluster.
There is neither visible particle suspension no perceivable Tyndall effect. DLS tells us that for sure we don't have nanoparticles bigger than 10 nm.
I've read some papers reporting a control experiment consisting in measuring the rate of the reaction in the presence of mercury in solution. If no inhibition is observed, the absence of nanoparticles can be deduced. Honestly, I don't know how the principle of this control experiment should work.
The ultimate options would be to hope to see something from TEM or to try to get single crystals by evaporation to obtain the crystallogrphic structure. Do you have any other idea?
Thin-film TiO2 photocatalysts prepared by dipping, spinning, and spray coating by sol-gel method but the UV–vis absorption plots for the samples that yielded bandgaps of tio2 is 3.75 (very high) which is not required for the photocatalysis process. It should be 3.20 and below
Chemicals who used in the experiment : titanuim butoxide, ethanol, isopropanol and acetic acid
calcination temperature 450 C for 1 hour
what is Affected parameters to reduce pure tio2 band gap for 3,20 ev
I am preparing photocatalysts based on g-C3N4 and molybdates, but I have doubts about the heterojunction that will be formed between them.
We are testing our photocatalyst for both water oxidation reaction (WOR) to O2 and oxygen reduction reaction (ORR) to H2O2. Can you in principle close the cycle from H2O to H2O2 (and then back to H2O by H2O2 decomposition) through O2?
We got some H2O2 in one day when we introduced our photocatalyst in oxygen-deprived water (by freeze-dry). Can we conclude that the hydrogen peroxide comes from oxygen evolved from O2? Or is it more likely from direct 2 electron water oxidation?
In the lab, there is titanium dioxide (TiO2, Sigma, purity 99.9%). Can I put it directly into the solution when using it in photocatalysis experiments? If I put it directly into the solution, the water becomes blurry and it becomes impossible for me to use the catalyst again. Because it's in powder form. In this case, the degradation efficiency gives very high results. Or do I need to convert it into a more visible particulate photocatalyst in solution so that I can use the photocatalyst again?
For example, when TiO2/GO tested under irradiation of UV light produces methanol, but when it is experimented under irradiation of visible light produces methane.
When performing photocatalysis experiment e.g. TiO2 photodegradation of methylene blue, there are no clear measure that contributes the efficiency of the photocatalytic. I am wondering if there are any references that can be provided that illustrates the different efficiency equations that people use to report the efficiency of their photocatalyst or lists the contributing factors in the efficiency? Most of the literature reading I have read don't elaborate nor provide methods they used to quantify the efficiency.
We know that band bending decides either electrons or holes can migrate to the surface, but how do we know which direction does the band bends (or it doesn’t)?
Then, why would the band bending change when the fermi level changes?
It would also be great if you only give some key words for me to search.
Thanks for reading.
i do research about simultaneous photoreduction of Cr(VI) and Fe(III) by TiO2/UV. And I have problem with kinetic model for this reaction. Normally the reaction happens as:
Cr(VI) + H+ +e- --> Cr(III)
Fe(III) + H+ + e- --> Fe(II)
Can I write the overal reaction as:
Cr(VI) + Fe(III) + H+ +ne- --> Cr(III) + Fe(II)
In the literatures I have read, the parent TiO2 is synthesized via hydrothermal, solvothermal, or other methods.
Thank you in advance!
Usually, certain amount of photocatalyst powder is placed in the dye/drug (organic contaminates) solution under UV/Vis light irradiation. I found some confusion about effect of reactive volume, sample volume, and solid/liquid ratio during photodegradation process. Thank you.
One of the difference between metal oxide photocatalyst and non-metal photocatalyst is the effect of pH on the valence band. How does it affect and why?
Recently, many publication related to photocatalyst material supported on activated carbon (AC), for example: water pollutant adsorption-degradation and CO2 reduction applications.
My question for discussion:
1. [for water pollutant adsorption application] Is it the promising concept due to the large surface area of the AC can promote the adsorption of the pollutant molecule and further the pollutant will degrade by photocatalyst material?or the removal of pollutant is dominated by the adsorption process?Since the surface of activated carbon itself has dark color which will absorb light. Is the AC will promote photocatalytic activity?or reduce photocatalytic activity?
2. [for CO2 reduction application] Is it possible that photocatalyst will degrade the AC itself?and the process will produce gas ,such as CO, or another organic compound that causes error to determine the photocatalytic performance?
Thank you for your attention.
How does the cut off filter fit on the photocatalyst reactor?
One of the methods by which we prepare P25 photocatalyst is by depositing AgBr on surface of TiO2 (P25). Will depositing of Ag/AgBr on TiO2 surface and then annealing it at 500C cause some Ag+ ion to diffuse into TiO2 lattice and displace Ti forming substitutional vacancies?
I need to simple method to study a zero point charge of photocatalysts...
Can a photocatalyst (excited by ultraviolet or visible light) be used as a radiation catalyst (excited by X-ray)?
I am doing a photocatalytic performance evaluation by RhB dye degradation. I am facing a problem which is:
After achieving the absorption -desorption equilibrium, I checked the concentration and marked it as C0. I repeat the same process to check the performance of my sample after every 30minutes. And I can clearly observe the decrease in concentration, even though, the degradation of RhB is very slow. However, after some time, the concentration suddenly increased to a specific number. For example, 1, 2, 3, and 4th sample concentration is 1.88, 1.65, 1.35, and 1.10 respectively. but in the 5th sample, it will be like ~2.15. What is the reason of facing such a problem and how to counter this?
Hello,
I was interested in knowing whether using rGO as the charge mediator between a p-type semiconductor and an n-type semiconductor (in a ternary composite, for example g-CN/rGO/α-Fe2O3) would have any negative influences on charge transfer between the two semiconductors by negatively influencing the natural p-n junction which forms at the interface (in the example's case, between g-CN and α-Fe2O3).
I have noticed that rGO or graphene is commonly used as the charge transfer layer, due to its high conductivity, in many ternary composites, but I also happened to notice that both the semiconductors of these composites happen to be n-type semiconductors, for example g-CN/rGO/TiO2.
Hence, my above concern.
Thank you,
Joshua Nigel
I'm working on the degradation of various pollutants with bare and composite TiO2. Since the size of TiO2 is too small, the particles won't be settling down as we take the dye solution at intervals to record the absorbance of the dye. How can I get the peak of dye alone without the noise from TiO2 or other materials?
I tried using a microfilter, in that case, the dye molecules themselves get filtered out in some situations. I also tried centrifugation, but that too didn't completely settle the suspended TiO2 NPS.
what can be other reasons such as surface charge, absorption etc. Please provide detailed explanation and reading material.
In all the literature I've read, I always find Au and Ag as metals for surface plasmon resonance photocatalysis. Why are other metals never used?
One option I've considered is that other metals oxidise and cannot remain in metallic form to act as a photocatalyst, but then, why do we never see Pt SPR for example?
Thanks in advance!
I am interested in synthesizing (graphitic) carbon nitride (g-CN) from Urea.
Almost all literature states that the synthesis is performed at a heating rate of 2-3°C/min, 500-600°C for 3-4 hours.
I have attempted the synthesis (using 15g of urea) at 550°C for 3h, at a heating rate of 10°C/min (Currently it is not possible to alter the heating rate of the furnace). However, my final product was only melem/melam and not g-CN (i have attached its data).
I am aware that the heating rate can influence the crystallinity, morphology and other such properties; however, will it also determine what my final product will be?
As in, without a heating rate of 2-3°C/min, will I not be able to successfully produce g-CN at all?
This is my main query. I have already posted a question about the influence of the heating rate, but I did not express my query appropriately.
I do intend on repeating the synthesis at 600°C for 4H (15g of urea and 10°C/min ) as these results could simply be due to incomplete polymerization, but I earnestly need some clarity regarding the rate of heating.
Oxidative and reductive reaction could happen simutanously. Is there any method to control the reaction by adding some specifical chemicals? If we wanna to enhance the oxidative reaction rate, could we use particular electron scavenger to boost the consumption of electrons?Look forward to hearing your opinion.
Regards
Xinxing
TiO2 foam is generally highly porous in nature, but for my sample it is showing very less around 600 micromoles for 2.5 hours. Can you give some suggestions about this comment?
Dear colleagues
pH setting such as for testing the stability of photocatalyst (or other materials) is one of the important thing. Generally, this condition can be adjusted by pouring or dropping some acid or base compound droplets like HNO3 (nitrate acid), HCl (chloride acid), NaOH (sodium hydoxide) and so on. But, I think there're some main considerations to choose one of them. Maybe, there some of you can share tips to select a proper acid and base compounds in controling pH situation especially in inorganic synthesis material, pH stability, or dye photodegradation?
Thank you very much.
Dear colleagues,
I have used Scherrer equation and Williamson-Hall in determining the crystallite size and strain within peak broadening phenomenon. Sometimes, by using both of them, the data showed a various values. How I can interpreate this data? and whats the relationship between both of methods?
Thank you.
Dear colleagues,
When I read paper, the crystallite size can be calcukated by taking the XRD data with the highest intensity profile. Btw, in our research using Ag3PO4 photocatalyst, it observed at 2 thetha = 20-25° and Miller indice of [210]. However, I just wonder how the maximum peak intensity of X-ray could be a refference in the crystallite size determination? What's the basic information to support it?
Thank you.
Graphene is being used for the treatment of pollutants in aqueous medium especially for oil spills. Would like to know its performance as a photocatalyst/adsorbent?
In a p-n heterojunction under internal electric field, the photogenerated electrons and holes will transfer to the n-type semiconductor and the p-type one, respectively. It can be assigned to the fact that CB and VB of n-type semiconductor are normally lower than those of p-type semiconductor. It seems that the type-II heterostructure is similar to this p-n photocatalyst. So what is the main difference between these two heterostructures?
Dear colleagues,
To date, I have researched photocatalyst based materials, this was done under the UV or visible light irradiation. When I used a commercial lamp (they have red or blue-appeared color), I just wonder that how I can determine the mono or polychromatic type of those used light sources? What is the simple way to determine them?
Thank you.
As far as I known, The bandgap of Graphene Oxide (GO) is dependent on H coverage. But, GO is an organic material. Therefore, Should we use inorganic (Ev, Ec, Eg) or organic (HUMO-LUMO) energy band theory to describe the photocatalytic properties of GO?
To 50 ml of AgNO3, HAuCl4 or HPtCl6 in deionized water, 1 gm of TiO2 was added. How do they arrive at the calculations that these are 1% Ag/TiO2, Au/TiO2 and Pt/TiO2 photocatalysts?
(research paper attached)
https://doi.org/10.1016/j.jphotochem.2019.01.032
Dear colleagues,
Since band gap energy is related to material size, somehow, the quantum phenomenon could be found in the range of Bohr atomic radius for semicondutor based materials. Did you know about that? How I can collect the data of atomic Bohr radii for photocatalysts?
While observing overall water splitting of pure water, my heterostructure photocatalyst exhibited H2 evolution initially in 1st hour and then O2 evolution in 2nd and 3rd hour. After that it became inactive. I have used Pt and Ag as cocatalysts.
What can be the possible reason for;
(1). Why it is not able to produce H2 and O2 simultaneously?
(2). Why after 3rd hour, O2 evolution is also stopped?
Dear colleagues,
In the lab, I tried to synthesize photocatalyst using PEG-1000 as directing or controlling agent in crystal formation. Based on the results, SEM using secondary and backscattering methods showed that the photocatalyst surfaces were covered by the transparent layer as the attached figure. I assumed that they were the PEG-1000 residuals because there were no additional compounds besides PEG. But, when it is analyzed using FTR, the peak absorption of PEG-assisted photocatalyst synthesis is different from their reference (pure PEG-1000). How do we explain this? Is FTIR powerful to analyze the left PEG residuals on the material surfaces? Can you help me by attaching some related references?
Dear colleagues,
I have analyzed the crystallinity of photocatalyst material (without calcination treatment and calcined samples) using XRD in two place XRD analysis services in my campus. When I comparing the data, there a significant movement between them. Obviously, the peaks have significantly shifted to the lower thetha (°) for calcined samples than control (untreated sample). Based on this fact, is it an instrument error or structure destruction?
I want to know what is the best catalysts or photocatalyst that can be used in the degradation of lignin to its value-added monomers such as benzene, phenol, toluene and xylene that could have an added value as fine chemicals and in pharmaceutical industry ?
I have seen in many papers that co-doping enhances(not always) the photocatalytic activity of a photocatalyst. What is the reason behind this?