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Photocatalysts - Science topic

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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.
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Dear all, the answer will depend whether the question is concerned by conventinal radical polymerization or by recent living/controlled polymerization ones. Among many factors that are detrimental: presence of oxygen (inhibition/retardation) and transfer reactions. My Regards
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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.
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"As for the difference between S-scheme and Z-scheme photocatalyst, the S-scheme photocatalyst is usually composed of two n-type semiconductors, while the Z-scheme is usually composed of n-type and p-type semiconductors. In addition, the construction of the Z-scheme photocatalyst is inspired by the natural photosynthesis process and the S-scheme photocatalyst is named for its staggered band structure."
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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.
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Yes, there are other photocatalyst concepts besides the Z-scheme that have been proposed for overall water splitting.
One such concept is the Type-II heterojunction, in which a semiconductor material with a wider bandgap is paired with a semiconductor material with a narrower bandgap. The two materials form a heterojunction, which allows for a more efficient separation of the electron-hole pairs generated by the absorption of photons. This concept has been proposed for use in overall water splitting by using semiconductors such as TiO2 and CdS as well as other combinations.
Another concept is the S-scheme, which involves the use of a single semiconductor material with a bandgap that is intermediate between the bandgaps of the materials used in the Z-scheme. This concept aims to improve the overall water splitting efficiency by reducing the recombination of the electron-hole pairs generated by the absorption of photons.
A good reference for these concepts is "Recent advances in photocatalytic water splitting" by D. Wang and Y. Wang, published in Journal of Materials Chemistry A (2013). This review article provides a detailed overview of the recent developments in photocatalytic water splitting and discusses the different photocatalyst concepts, including the Z-scheme, Type-II heterojunction, and S-scheme.
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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.
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Synthesis of chemicals / API / Drugs by continuous flow process using Flow Engineering / Flow Chemistry / Flow reactors / Technology. All the best ...
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I observed an increment in the absorbance of chloramphenicol using a UV spectrophotometer.
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Gentle Akinnuoye Likely formation of degradation products of chloramphenicol. You can expect some phenolic or quinonic products which will absorbe stronger in the UV-range.
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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?
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For bandgap Calculation, you can follow this article...
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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?
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To explore Scavenging effect, Follow this article
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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
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@ thanks a lot sir for your help
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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.
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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?
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Try oxidizing agents: ozone, hydrogen peroxide (perhydrol), sodium or potassium hypochlorite. It is also possible with acids or when changing the pH with coagulants.
Filtration, through a sorbent.
a lot depends on what your photocalizer consists of. Maybe just ultraviolet.
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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.
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With such a limited infomation it is impossible even guess. More details.
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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?
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hydrothermal synthesis. you could try GO and something else. Or just prepare some MOFs/COFs.
No it isn't possible. Ostwald ripening effect will make your particles bigger with increasing temperature.
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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.
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I'm not sure the size of your reactor. for the laboratory scale, the xenon lamp and mercury lamp are suitable because of their high light intensity. But in academic research, LED light sources may be a trend. I have compared conventional high-power light sources and LED in photocatalysis in my previous research, hope it works for you.
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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!
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I am seeing this phenomena in a non-quartz vial.
Thank you for the reference!
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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
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Surely yes, but it depends much on the complexity of the system.
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Is there any previous research show that co-doping for TiO2/ZnO nanocomposite photocatalyst is better than single doped?
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Dear Syahmi Basir, other option is the use of 'bimetallic NPs catalysts' (search with this keyword), they are by far more performing than nanocomposites. My Regards
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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
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That actually comes from some assumptions from electronic transitions in semiconductors, both direct and indirect bandgapped.
Starting with a direct bandgap in a 3D semiconductor, if you calculate the joint density of states for the absorption of a photon with energy bigger than the bandgap, you will find a result that is proportional to (hω-Eg)^1/2. α in this case is proportional to the transition rate divided by hω, which is proportional to the joint density of states. This is the simple one. You can find this explained very well in Mark Fox book Optical properties of solids.
For indirect bandgapped materials it is a little harder, but the electron-phonon interaction must come into play. I'm not going to go into detail though, and you can find it in Cardona's book Fundamentals of Semiconductors.
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How significant is the FTIR study of mixed metal oxide photocatalysts like WO3-TiO2 nanocomposites?
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Hi Aarif Shah , in gas phase catalysis FTIR can be quite useful to probe the chemistry of the surface. (In water phase, may be not much will be seen because of water interference, you can perhaps do it, who knows)
If you have a pure metal oxide powder. The FTIR spectra (ATR is preferred) of the powder will already give a few important information about the surface. First, the water molecules that may have from the atmosphere. H2O can adsorb both as molecules, but also in the dissociated form: H and OH. H2O will also be present in the condensed form due to capillary condensation. Now, the dissociated H2O is interesting! Because it denotes a catalytic process. In TiO2, the active sites dissociates the water and then the H and OH are sitting on the active sites. On FTIR a small shoulder at 3596 cm-1 denotes dissociated water for TiO2. Same is observed for ZnO. Around 1600 cm-1 adsorption of molecular water is denoted by a peak. Further absorption bands from the metal oxide itself are difficult to interpret. But things can still be improved because data science is developing as well.
Now if you are investigating the photocatalysis with WO3 and TiO2, then you can study degradation of a surface organic molecule with FTIR. The C-H stretches of long chain organic molecules show strong absorption in the 2800 cm-1 to 3000 cm-1 region. This absorption peak you can monitor during the degradation. During degradation, CO2 peaks will also evolve. In this work, we exploited the FTIR analysis for studying TiO2, WO3, ZnO and CuO. You may find this interesting:
What is also interesting is DRIFT (Diffuse reflectance FTIR). So this is FTIR where you probe the diffusely reflected signal from the sample after IR incidence. For catalysis it is particularly interesting because it gives only the surface chemistry due to reflection based probing. DRIFT cells are accessories that can bought along with normal FTIR set-ups. An in-situ DRIFT cells where vacuum can be created or gas phase reaction can be carried out is an inexpensive but powerful set-up!
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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?
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thank you very much
i experienced your comment a bout coating of FTO with thin layer of catalyst and also increasing annealing temperature until 470 degree C. and successfully was controlled cracking of coated film.
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Which photocatalysts will be preferred for better efficiency? Metal-doped or Non-metal doped?
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For that please follow these articles
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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?
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The type-II heterojunction is the conventional mechanism which describes that, upon irradiation electrons of both the semiconductors (in the photocatalyst) get excited to the CB leaving holes in the VB. Then the lifetimes of these photogenerated electrons and holes are extended because of the shifting of electrons in the CB of the semiconductor with a more negative CB band edge to the CB of the semiconductor with less negative CB band edge and similarly holes will shift towards less positive VB. So, this prevents the recombination of electrons and holes.
In the Z-scheme mechanism, there are donor and acceptor terms involved.
Basically, in this mechanism, photogenerated electrons in the CB of the semiconductor with less CB band edge recombine with the holes in the VB of the semiconductor with less positive VB band edge. Thus, unwanted electrons and holes recombine and this enhances the lifetime of strong photogenerated electrons (in the CB of semiconductor with more negative VB band edge) and holes (in the VB of semiconductor with more positive VB band edge) which will subsequently take part in the photocatalysis.
This is the basic difference.
Yu et al. have explained these mechanisms in detail in their paper. (10.1016/j.chempr.2020.06.010)
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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
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@ Esther, the attached file may be useful to you.
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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
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For preparing g-C3N4, you can calcinate any specific amount of ammonia or urea in a Muffle furnace at 500-550 C° for 2-3 hours.
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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.
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Dear Zakarya Zebiri
In order to explore heterojunction formation in multi-component photocatalysts, XPS analysis is a versatile instrument. Because in this technique, binding energy of elements is very sensitive to changes of electronic environment of elements. Hence, you can simply compare the binding energy of C, N, Co, and O elements in the composite relative to the pure components. For more information, please refer to the following valuable paper, pages 6-8:
-Liuyang Zhang, Jianjun Zhang, Huogen Yu, Jiaguo Yu, Emerging S-Scheme Photocatalyst, Adv. Mater. 2022, 2107668.
Regards
Aziz Habibi-Yangjeh
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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?
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The most likely reason is due to the small amount of the solution (50 ml) and the high amount of eriochrome black (20,25,30,35, and 40 ppm). Try adding a small amount of eriochrome black (1 to 10 ppm).
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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.
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thank you for your answer.
Dear sir, I have the bandgap and the potentials of the bands (CB and VB) for both semiconductors and I know throw the use of scavengers that the junction formed is type II. But I want to form a Z scheme junction to protect the high redox ability of the two semiconductors. What I'm asking is, are we able to control what junction that will be formed or that's something we couldn't know before the synthesis?
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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?
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Matheus Mendes thaks for your valuable suggestion
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The concentration of aqueous solution of ibuprofen can be measured by using UV-VIS?
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Yes you can.
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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.
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Also check please the following good link:
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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.
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It can be calculated from UV data of photocatalyst as well as DRS data of photocatalyst. While using UV data Tauce's equation is used. While in other case kubelka munk equation is ised
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Microsoft excel sheet required.
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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?
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Phenolphthalein is a common acid-base indicator used to determine the endpoint in acid-base titrations. It is also the active ingredient in some laxatives. If excess base is present at the end of an acid-base titration, the pink phenolphthalein color fades if the solution is allowed to stand for a while.
The structure of the colorless form of phenolphthalein is C20H14O4. At a pH of 8 or lower, the structure will be abbreviated as H2P and in the pH range of 8-10 both acidic protons are rapidly removed from the colorless H2P by NaOH, (OH - ) to give the pink P2- ion according to the equation:
H2P+2OH-=P2-+2H2O(pink)
At a pH above 10 the pink color slowly fades as P2- reacts further with NaOH, (OH - ), to give the colorless POH3- ion:
P2-+OH-=POH3-(colorless)
For decolorization, pH is a major factor. I can say the above from my side.
Regards
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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.
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By the introduction of different scavenging agents into the photocatalytic system.
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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.
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Please refer to printbibliography output for "[author year] entrydata" (using biblatex-ext and its introcite option) if you are using a more recent TeX installation.
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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.
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Do you need to create the bibliography or just cite the references in the body of the paper?
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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?
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Manga Raju Imandi thanks for your valuable answer
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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??
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Dear Bakhtyar K. Aziz, I think your repoted value of Eg is much higher than the most common ones. The synthesis techniques and protocols highly influence the Eg values. Please check the following RG free access documents. My Regards
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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?
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You did not write the most important thing whether the supposed suspension is photocatalysis or not. To prove heterogeneity
1. Separate by long standing
2. Separate by centrifugation
3.Add an immiscible solvent and see the distribution of substances in each of them
4. Add larger nanoparticles and view by DLS.
5. Add coagulant chloride or aluminum sulfate and check if there is precipitation
6. Change the pH and see the change in precipitation
You must know the possible nanoparticles of the photocatalyst then you can discuss the problem more specifically.
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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
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Only on the basis of UV experiment one can not get the clear idea about why band gap increased. First, I would like to suggest to repeat the experiment again including synthesis. If possible then measure the standard sample using same UV measurement system to check whether instrument is working fine or not. If instrument is fine, then try to do other characterization such as temperature dependent (low temperature region) electrical resistivity from which you can also calculate the band gap. Another important point is to check the chemical composition as off stoichiometric sample can affect the electronic structure near chemical potential, which can lead to the shrink or broadening of the band gap depending upon the excess or deficiency of oxygen. Che king from different techniques and analysis with different model you can find the exact reason which is responsible for such unusual results. At the end I hope xrd will be single phase, just confirm it with crystal structure analysis method. Good luck.
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I am preparing photocatalysts based on g-C3N4 and molybdates, but I have doubts about the heterojunction that will be formed between them.
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In addition to scavengers the use of PL spectroscopy could be very useful. Comparison of the intensity (under adequate excitation wavelenght) with respect to the parent components would provide evidence of the type of interface you are analyzed.
Using g-C3N4 we measured the type of several interfaces.
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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?
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Dear Andrea,
this is a very good and important technical question. As a synthetic inorganic chemist I'm absolutely not a specialist in this field. However, I just came across the following potentially useful review article which could help you in your analysis:
A comparative perspective of electrochemical and photochemical approaches for catalytic H2O2 production
Unfortunately this review article has not been posted as public full text on RG. However, the first author has an RG profile (https://www.researchgate.net/profile/Yanyan-Sun-8). Thus you should be able to request the full text directly from this author via RG.
Good luck with your work!
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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?
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Dear Serhat Sezer , have you tried to perform centrifugation on your solution with the catalyst? You can separate the powder catalyst from the solution, and also perform FTIR before and after the photocatalytic process.
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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.
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Tq for the
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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.
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Continuing the topic of possible dependencies of efficiency measures on, for example, photocatalyst concentration or light intensity, one should expect mainly empirical equations/functions.
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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.
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Got it.
Brajesh Kumar Thanks a lot! Thanks again for your time.
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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)
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Ridha Djellabi, Since you've linked your work, here's a quick comment. The most important thing is, of course, the possibility of complete removal of pollutants and the interpretation of the observed phenomena. The mathematical description of the kinetic data is of secondary importance. However, if you choose to do so, do not mislead the reader. There is no evidence in this paper that the processes under investigation are of the first-order. The mere compliance of the empirical exponential function with separate kinetic curves is not enough, and the results presented in Figs. 2 and 4 and in Table 1 even contradict it.
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In the literatures I have read, the parent TiO2 is synthesized via hydrothermal, solvothermal, or other methods.
Thank you in advance!
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Hello Lea Bongat
There a lot of reasons that's why it is necessary to treat commercial TiO2:
1. In many of the cases, titanium dioxide have impurities that are necessary to remove because could affect catalytic activity.
2. Do not have a high surface area. Commercial TiO2 only have at least 34 m2/g, which could decrease considerably the reaction rate of your material in a specific reaction.
3. Commercial TiO2 have a very specific "shape" or "architecture" that could do not favor your reaction.
With kind regards,
Julián :)
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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.
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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.
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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?
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No - for other materials the value is different. For example - for sulfides it is around 0,033 eV.
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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.
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"cellulose fibre" does not exist. By definition all organic materials contain C.
Read what you write and then respond to the titled question.
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How does the cut off filter fit on the photocatalyst reactor?
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It depends on the photocatalyst, if you need more information, you can send me a message.
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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?
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Azeez Abdullah Barzinjy Thomas Jüstel Luiz Fernando de Sousa Lima Thank you for your input. I most certainly agree with the idea that "Irrespective of the method of synthesis" (sol-gel method or photodeposition), the idea of Ag forming substitutional vacancies in TiO2 crystal is not rooted in theoretical observation. However, I do believe that Ti-O-Ag bonds are formed which somehow reduce the charge density and affect the lattice constants, thereby affecting the crystal strain however I am still working on proving this theory. The following paper has also reported the presence of Ti-O-Ag bonds. Perhaps oxygen vaccancies and its quantification is a good place to start.
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I need to simple method to study a zero point charge of photocatalysts...
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Video link for determination of Point of zero charge (PZC)
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Can a photocatalyst (excited by ultraviolet or visible light) be used as a radiation catalyst (excited by X-ray)?
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No. It cant be. The role of photocatalyst is to initiate redox reaction only. The phenomena of excitation under UV or visible light can promote one electron to accept/donate from the catalyst, hence the process started. The utility of light (UV or vis) is no more.
For radiation catalyst, the role is completely different. X-ray is a source of much higher energy and hence, harder ionizing capability rather than visible light or UV. So, for much forceful phenomena is obtained by this type of catalysts
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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?
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You're welcome.
In case of antipyretics - when it contains benzoic acid unit or something similar, probability of dimers formation is very high. Drugs can also form charge-transfer complexes with semiconductor (via hydroxyl or carboxyl groups) which can also affect the changes in concentration. It depends of course on the photocatalyst type, and most often it is included in adsorption-desorption equilibrium of the contaminant.
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Please explainn this.
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Nice discussion
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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
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Hi Joshua,
The best answer is that it depends. Primarily on the size and relative position of rGO w.r.t. your traditional p and and n-type photocatalysts. People have reported all different kind of systems including z-schemes and transistors using all kinds of charge mediators ranging from Au nanoparticles to graphene.
I haven't had a chance to go through recent literature on the topic, but I am guessing there might be some literature on that. Coming back to the question: even thin layer of rGO might be enough to disrupt the formation of a p-n junction as the semiconductors are not in contact. As to whether it is bad or not depends entirely on you application.
I would suggest you to read a review article that we published recently, which has a lot of examples of what such bi-phasic photocatalysts (with w/o a charge transfer interface) have been used for.
I hope it helps.
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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.
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If you are interestes in the molecules in solution just use described procedure.
But this works only for organic dyes. If you have inorganic particles making the color you would have to do XRF and may be XRD with the sediment after centrifugation or at last SEM or TEM.
I wonder from where you get single TiO2 nano particles as well as color dyes from real life pollutants. Anyway I would strongly recomment TEM to clarify the real situation of your pollutant.
For Molecules adsorbed on TiO2 use microwafeextraction with some commonly used alcohol as solvent.
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what can be other reasons such as surface charge, absorption etc. Please provide detailed explanation and reading material.
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Photocatalytic processes are considered redox processes initiated by charge carriers (electrons and holes) separated after excitation of the photocatalyst. As it is known - the valence band and conduction band of photocatalyst lies around certain potential values. When the redox potential of the reaction is higher than conduction band edge potential - then the reaction is impossible due to the fact that electron wants to decrease its energy. The same happens when reaction redox potential lies under the potential of the edge of valence band. Pollutants can be also degraded by radicals which arise in described processes or in the case in which the organic molecule (most often dye - it is called a sensitizer) is excited and then the electron can be transferred from the LUMO orbital of this molecule to the conduction band of the semiconductor and then radicals can arise in reaction with the electron from conduction band. Of course the LUMO orbital of sensitizer must have greater energy than conduction band of the photocatalyst. This process in known in literature as photosensitization. In some cases the pollutant can be a sensitizer itself.
These phenomena, as well as possibility of adsorption of pollutants on photocatalyst surface or possibility of absorption of the light from certain range, or the rate of charge carrier recombination etc. can affect photocatalytic activity of the material.
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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!
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Au and Ag nanoparticles can be formed to absorb visible spectrum efficiently that's why its commonly used photocatalysts.
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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.
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Dear Joshua Nigel Fernandes thanks for your interesting question. Please see the following article entitled "Simple Pyrolysis of Urea into Graphitic Carbon Nitride with Recyclable Adsorption and Photocatalytic Activity". The paper is available as public full text on RG. In the experimental procedure it is stated: "After drying at 80 °C for 24 hours, the urea was put in a covered crucible and heated in an oven. The yellow colored g-C3N4 was obtained by heating at 550 °C for 3 hours." Thus the authors don't specify the heating rate at all. Perhaps the drying of the urea prior to the pyrolysis plays some role.
Please also find attached the Supplementary Information for this article. It does not contain any further details about the heating rate either. Apparently the heating rate is not crucial in this process.
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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
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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?
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If you are using TiO2 foam in a photoelectrochemical system as photoanode, the thickness of the electrode is very important. The thickness of the electrode (thin film) should be less than the electron diffusion length. Larger the thickness may lead to efficient recombination of photogenerated charge carriers.
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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.
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Hi, Febiyanto,
May be, you can first do a bibliography on your synthetic materials to assess their stability with respect to pH, which I agree with you is an important parameter during the organic pollutants degradation such as dyes.
Good luck
Safia
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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.
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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.
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you know that the peak size is derived from the peak width such as the full width at half maximum (FWHM)
The maximum peak height come here into play because from the peaks with the largest heights this height(s) (and thus the half of the height(s)) can be determined with the highest confidence due to minimum noise, which statistically affects the individual height. Noise goes with sqrt(N) with N being the counts of the peak height. The relative noise Nr (as the noise relative to the peak height) is a measure of the measurement uncertainty of the peak height:
Nr =sqrt(N)/N= 1/sqrt(N)
So for the heighest N of the peaks we have the lowest uncertainty in peak height determination, which directly affects the (lowest) uncertainty of FWHM calculation.
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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?
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Yes..I too agree with Prof Feroz, Graphene act as adsorbent.
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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?
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In the right side p-n junction structure the field region in the transition region will direct the electrons to the n-side where they will be accumulate on the surface of the n-side. At the same time the photognerated holes will be directed to the p-side where they will accumulate on the surface of the p-type material. So, the p-side will be source of holes which is oxidizing. The electrons accumulating on the n-side will be reducing.
The structure in the the right side is composed of two intrinsic materials with the left side has an electron affinity greater than the right side. The two materials have almost an equal energy gap. Both materials are optically active where on absorbing photons they will both generate electron hole pairs.
The electrons will be accumulated on the left side while the holes will be accumulated in the right side.
So, the right side will be oxidizing while the left side will be reducing.
Both will have photovoltaic effect.
The second structure is simpler to produce than the first p-n junction structure.
Best wishes
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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.
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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?
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graphene being zero bandgap shows fast recombination of excitons, and has no photocatalytic activity. it is just adsorption of dye on the graphene surface. if you want to use graphene/carbon materials for photocatalysis, you can only use carbon or graphene quantum dots. no catalysis journal accepts the photocatalysis of graphene. if you have graphene, then graphene quantum dots synthesis is not that much difficult using the following method.
You can see these papers as a reference.
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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
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Not sure why there are issues here other than the formulae are not correct in the question or the attached paper. Chloroplatinic acid is usually formulated as H2PtCl6.xH2O (x = nominally 6) and chloroauric acid as HAuCl4.yH2O. The x's and y's are important because both salts are hygroscopic and weighing out exact quantities is a problem. It's usual to measure the real metal loading afterwards by AAS or ICP - one usually finds that the actual loading is less than that aimed for because of wash out and the underestimation of 'x' and 'y'. The catalyst preparation isn't conventional either - normally one would just saturate the pores of the support (and this requires a knowledge or measurement of the pore volume. The calculations are not correct either: to make a 1 (wt)% loading of metal on support requires 1 g of metal and 99 g (not 100 g) of support. So, I suspect that chemists or catalyst engineers were not the authors of the paper.
Let's take one example. A desired loading of 1% Pt on 1 g of TiO2 requires 0.01 g of Pt on 0.99 g of TiO2. In order to get 0.01g of Pt (atomic weight 195.084) requires [517.90/195.084]*0.01 g of the chloroplatinic salt precursor (the MW of H2PtCl6.6H2O is 517.90) or ~ 0.0265 g of the salt. It's freely soluble in water so you'd dissolve the approximate amount in water and use this solution with the 0.99 g of the TiO2. Now the key here is the pore volume of the TiO2 (and, of course, that x is not equal to 6 but practically greater). It wouldn't be normal in catalyst engineering to just dissolve 0.0265 g of the precursor in any amount of water. One would want to just saturate the pores. Imagine a TiO2 with a known pore volume of 1 mL/g then the ideal situation would be to dissolve 0.0265 g of the salt precursor in 0.99*1 mL = 0.99 mL of water and add this to the dried TiO2 support. This is not really practical and that's the reason why most people would make 25 or 100 g of final catalyst.
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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?
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Good discussion!
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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?
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Yes, of course. SEM image can also strictly identify the surface deterioration which meaning that catalyst surface and substrate may be inhibited by it.
You're welcome Muhammad Shuaib Khan.
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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?
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No comments on FTIR, only on SEM. You do not have a "transparent layer". Electrons of 15KeV have very small depts of penetration, much, much less than your scale bar of 1 micron. You do not see surfaces covered with some layer (may be you have one, but you do not see it at least), you have just something (artifact?) on the bottom of one of the particles. For proper observation in secondary electrons you had too high voltage and as a result - very strong edge effect which obscure details. You may want to repeat your observations at lower accelerating voltages (1-5 kV) and higher magnifications.
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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?
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If it is not the instrument error, then most probably the slight shifts of peak positions toward lower angles might be occurred due to the substitution of small radius ion by a larger one (Vegard’s law) which leads to an increase in the cell parameters that may cause a slight distortion in the lattice and a modification of the crystal structure.
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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 ?
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In my work
You can get the best oxide catalyst to phenol stability at high temperatures
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I have seen in many papers that co-doping enhances(not always) the photocatalytic activity of a photocatalyst. What is the reason behind this?
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I have replied such a question a few months back. I repeat.
Higher photocatalytic activity of Cu-N_codoped TiO2 may be due to decrease in band gap of TiO2 as metal doping (Cu) added some new energy levels below conduction band resulting in lowering of conduction band. On the other hand, doping by a non-metal like N helps in raising the valence band by adding new energy levels above the valence band. As a consequence, the band gap decreases and in turn wavelength