Science method

Analytical Chemistry Techniques - Science method

Analytical Chemistry Techniques are methodologies used for the isolation, identification, detection, and quantitation of chemical substances.
Questions related to Analytical Chemistry Techniques
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I have a material that produces hydrogen gas under certain conditions.  I need to quantify this and was wondering if it was possibly with GC-FID.  I know TCD is preferred but that is not an option at this time. 
Update: Thank you for your responses.  Would other instruments such as DSC or TGA be able to analyze for H2?
Or is there a method to convert H2 to a derivative for GC-FID analysis?
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TGA can measure the amount of materials lost during heating. However, it can not determine what are the materials. To confirm the content of the released gas, TGA-MS should be used.
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After performing boehm titration using HCl,NaOH, Na2CO3, and NaHCO3.  I want to know the formula to calculate functional groups.
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Dear Esteemed Colleague,
Greetings. I trust this message finds you well and thriving in your scientific pursuits, particularly in the area of surface chemistry and characterization. Your inquiry about the mathematical formula for calculating functional groups on surfaces such as carbon materials via Boehm titration is both important and insightful. The Boehm titration technique is a cornerstone in the quantitative analysis of acidic and basic surface functional groups, providing invaluable data for material scientists and chemists alike. Below, I provide a detailed exposition on the formulation and methodology for calculating the concentration of these functional groups using Boehm titration.
Overview of Boehm Titration
Boehm titration is a technique designed to quantify the acidic and basic functional groups present on the surface of carbonaceous materials. This method involves treating the sample with a series of bases and acids to neutralize acidic and basic sites, respectively. The quantity of acid or base that reacts with the sample surface groups is then measured, providing an estimate of the functional group content.
Mathematical Formulation
To calculate the concentration of surface functional groups, the following formula is commonly employed:
�=(�blank−�sample)×��C=m(Vblank​−Vsample​)×N
where:
  • C is the concentration of functional groups (mol/g),
  • �blankVblank​ is the volume (in L) of titrant used in the blank titration,
  • �sampleVsample​ is the volume (in L) of titrant used in the sample titration,
  • N is the normality of the titrant, and
  • m is the mass (in g) of the carbon sample.
Step-by-Step Calculation
  1. Perform Titration:Carry out the titration for both your sample and a blank. The blank titration helps account for any titrant that does not react with the sample but is consumed due to other factors (e.g., dilution).
  2. Measure Volumes:Accurately measure the volumes of titrant used in the blank and sample titrations.
  3. Determine Normality:Ensure the normality of the titrant is accurately known. This may involve standardizing your titrant against a primary standard.
  4. Calculate Concentration:Use the formula provided to calculate the concentration of functional groups on the surface of your material.
Considerations and Best Practices
  • Accuracy of Measurements: Precision in measuring the volumes of titrant and the mass of the sample is critical for reliable results.
  • Selection of Titrants: Choose appropriate acids and bases for titration, typically hydrochloric acid for basic sites and sodium hydroxide, sodium carbonate, and sodium bicarbonate for various acidic sites.
  • Replicates and Averages: To ensure reliability, perform multiple titrations for both the sample and blank, averaging the results for increased accuracy.
  • Correction for Blank: Always subtract the volume used in the blank titration from that used in the sample titration to correct for non-specific consumption of the titrant.
By adhering to these guidelines and employing the formula with diligence, you can accurately quantify the functional groups present on the surface of carbon materials via Boehm titration. This quantification is essential for understanding the chemical behavior and potential applications of these materials.
Should you require further clarification or wish to explore more about the application of Boehm titration in material science, please do not hesitate to reach out. Your dedication to advancing our understanding of material surfaces is commendable, and I am here to support your research endeavors.
Warm regards.
Check out this protocol list; it might provide additional insights for resolving the issue.
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I have to analyse a compound by ESI-MS. if it is not soluble in Methanol, ACN and water. Then what can i do? my compound is chloroform soluble.
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Tripti Mishra,
ESI-Ms is a very sensitive technique and the least unimaginable soluble amount will be detected.
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Dear researchers,
I would like to ask you whether the retention of analytes of interest on the C18 column can be slightly affected by buffer concentration.
I have analyzed a mixture containing sulpiride (weak base) and diclofenac (weak acid) at 250 ng/mL on the C18 column with mobile phase A: ammonium formate and mobile phase B: methanol.
I have observed that when the concentration level of ammonium formate increased from 2mM, 5mM, to 10mM, the retention time of sulpiride slightly decreased from 6.72 min, 6.52 min to 6.46 min respectively, whereas that of diclofenac slightly increased from 10.04 min, 10.17 min to 10.28 min respectively.
As far as I am concerned, for a basic compound such as sulpiride, an increase in buffer concentration (ammonium formate) can result in a decrease in silanol activity so a positively charged compound such as sulpiride can have a slight loss of retention due to the ion exchange interaction between the compound and silanol group during a loading step. Consequently, the retention time of sulpiride was slightly decreased with an increase in buffer concentration.
However, for an acidic compound such as diclofenac, it is quite difficult to explain this phenomenon. In my opinion, it seems that when the concentration level of ammonium formate increases, the pH of the mobile phase slightly increases so the charged state degree of diclofenac slightly increases either. As a result, the energy configuration of diclofenac diffusing inside the pore of the C18 column is lower at a higher concentration level of ammonium formate (10mM) so it will have more interaction surface area with the C18 column, leading to more retention. However, this explanation seems not to be convincible because the higher charged state degree of diclofenac is, the more soluble is and the less retention is.
However, for the retention behavior of sulpiride and diclofenac, the above explanations are just my own opinion. Of course, I am not sure whether they are right or wrong.
If someone here can help me clear the retention behavior of sulpiride and diclofenac, I am really happy to listen to your valuable suggestions.
Thank you so much in advance,
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Back to your original question (and I am done with this thread)... You observed a small (tiny) difference in Rt from small changes you made to the mobile phase composition. No worries, this is normal because no two columns are the same and each may interact to a different degree (or none at all) when you make small changes to the mobile phase composition. Try 20 different C18 columns and you may find some show no change at all, some do. Pick and choose the one that you want for the application (this is what we do in analytical laboratories). The reason for the observed change (change, not "drift") is due to multiple interactions of the solute on the surface of the support. Hard to say if it is electronic or ionization in nature, but it is so small, practically, it does not matter. All chromatographers are familiar with this (no need to 'explain it'). Run enough samples and you will see it. In fact, the one thing that they might question is why you would use a mobile phase of just ammonium formate without an acid (e.g.formic). Why not use a buffer? For LC-MS applications, most would benefit from such a solution to promote ionization and maybe change the separation factor too (depends on samples).
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According to the pourbaix diagram of Fe(2+), it should be dissolve in pH<6, but it is solid even in pH=1. I realy dont know what is the reason.
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The ferrous chloride salt (possibly hydrated) can be generally expected to be partially oxidized, at least to trace level. When (freshly) dissolved in aq. dil. HCl, you may consider to reduce contaminant ferric ions to the ferrous state by adding electrolytic iron powder (a few wt% of the weighted salt). Then the sol. should be heated (not boiled) to facilitate ferric to ferrous reduction and the dissolution of any possibly excess of ferrous chloride; cooled to room temperature; being then either vacuum filtered while using nitrogen as blanketing gas, or pressure filtered by using nitrogen as pressurizing gas. Hydrogen can possibly be released during the purification process, owing to the concomitant reaction of metallic iron with HCl: Fe + 2HCl → FeCl2 + H2. Water should be either distilled or both deionized and N2-purged or boiled. The purified ferrous chloride / HCl aq. solution may then be redox-titrated, if required.
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My sample include small liquid crystal, monomer and photoinitiator. the mixture is a little viscous at room temperature. The sample was tested by rheometer. The resulr was G' was higher than G'' at the beginning, which is contrary to theory. When the Uv light was turned on, G' dropped signnificantly and was lower than G'' and then rose again over G'', which means I got two intersection points in this test. Theoretically it shoud be that G'' is greater than G' and lower G' after passing the gelation point. I'm very confused and fail to figure it out. thank you if you can help me fix this.
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because free radical changes,have occurred when activating,or exposted to uv radiation
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Dear colleagues.
Now I have the problem that the kitasato has joined to the other part of the system and, I can not separate them. I think it happened because the unions were wet while filtering.
Do you know how can I separate them?
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If your funnel was stuck to the flask neck it was most probably due to water finding its way in between the funnel and the flask neck either before or during the filtration. You should stop vacuuming the pump as soon as you see it otherwise it'll get even more stuck. If it is slightly stuck, try putting a towel wet with hot water over the connection for some time. If this doesn't loosen it, you can try flowing hot water over the connection to evaporate the moisture inside. As another solution, you can try sonicating (if that's physically possible) the glassware.
Mind that you need to be really careful handling the glassware as they are usually really fragile. So try less extreme stuff first.
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Hi everyone,
I am trying to do a calcium sulfate solution with anhydrous powder but I can't dissolve it in water! Do you have any solution please?
Thank you
Julie
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It can dissolve easily with ammonium bicarbonate, or ammonia and carbon dioxide, in such way calcium sulfate converted to calcium carbonate and ammonium sulfate, the calcium carbonate then precipitated and ammonium sulfate can be used as fertilizer. the only problem which needs to overcome is coating of calcium carbonate over calcium sulfate particles, hence, the good mixing is necessary to prevent such coating,
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Hi, I'm working on my bachelor's final year thesis which is based on being able to detect the presence of saliva in crime scenes. My first step was to confirm that with the settings I have I am able to detect the presence of tryptophan. This was a 0.5g in 100ml solution of 5mM KCL and 2ml of this was placed in a cuvette and scanned for, which was successful - it result in an emission peak around 350nm.
I further tested swabbed dried saliva with a PBS swab off a lab-grade glass slide and placed it in a cuvette with 2ml of 5mM KCl and ran the tests. The results were way off the intensity scale.
So I tested for the range of dilutions to see in what range the readings wouldn't go off the scales, and dilutions of 1 in 100, 250, 500 and 1000 seemed to have worked. But unfortunately, the intensities of all of these were varying there was so linear relation like one would expect since its decreasing dilutions. I decided that I'll perform my tests from scratch and zeroed the instrument with KCl since that's what my samples are diluted in, and then ran the control again to see if any peak appears (since if you zero the instrument with a certain chemical, if you scan for it, nothing should appear), and a peak showed.
I then contacted Agilent hoping they'd be of some help. They said I was overloading/maxing out the detector, which I am unable to understand since I have diluted this to a small amount. And from previous papers that have performed similar experiments, they haven't needed to even dilute their samples.
I then tried varying the settings such as the PMT voltages, emission and excitation slits and performed tests with tryptophan to see if the peak at 350 would be detected. And failed as all the resulting peaks turned out to be "below threshold".
I am unable to determine how to go about it, and I'm nearing the deadline for working in the lab and I'm nearing the end of all options.
Obviously, since this is the first thesis I'll ever be writing I'm afraid I won't have results and just have various different trial and error methods.
All suggestions and any help I get will be really helpful.
I will be editing this post to add images of the settings I have my instrument on just for extra information. And for reference, I'm using the Cary Eclipse Agilent Fluorimeter with the Scan application.
Thank you in advance. :)
Shaina
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@Shaina Mercy Fernandes
I think there must be some problem with your solvent (water/aqueous buffer in this case). Check the fluorescence of blank solvent. To avoid such interference, always use triple distilled water.
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Thanks Matthias Knarr
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I am involved in a project to develop online software which simulates scientific instruments (such as absorption spectrometers) and chemistry experiments for science students (post 16 years) which is featured in the latest edition of Chemistry International (see following link):
Students can work their way through these online exercises producing data from the simulator, analyse that data and compile a laboratory report on their findings from anywhere that has an internet connection. We already have registered users from various institutions around the world incorporating these simulations into their degree programs.
1. I would be interested in the views of colleagues about the educational value of using our software, in general.
However, more specifically, I would also be interested to know how colleagues feel about the following:
2. Will this help to widen access to a science education, particularly for students from disadvantaged backgrounds?
3. As a company, we are eager to get involved with schemes/organisations that promote widening access to a science education. Can colleagues suggest how we might best go about this by identifying relevant organisations that may be interested in working with us/using our software?
We are a UK based company but would happily collaborate internationally with interested partners.
Delighted to receive any other comments/views.
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Very promising
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Since the target region in the PCR is smaller than the template DNA strand to be copied.
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The polymerase does not know that. The thing is that, in the first step, the polymerase will copy everything (into a complementary strand) from the primers. In the second step, this complementary strands now will have attached the another primer, so it delimits the region to be copied. Let's put an example focusing only on one strand: the direct primer will allow the polymerase to start the amplification from an end. After this step, you will have already delimited one part of your amplicon. In the second step, as the strand is the complementary one now, the primer bound will be the reverse, so delimitating the another end of your amplicon.
I don't know if I was able to explain myself as it is difficult to explain by words, but I hope it helped you
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I am trying to analyse a certain material in a certain food product via HPLC. However, I crossed problems and tried to correct them but problem goes on.
 After i see baseline in HPLC, i put standards and then my sample vial.
My sample showed a peak more area than standard peaks area. As first correction, i sent more concentration standard to HPLC column, Then i recognised that my sample peak got increase. As i increase standard concentration, peak of sample getting increase
As second application, i tried diluting sample concentration. Firstly i sent standards then i applied samples which are different concentration. But it didnt work well. For each diluted sample i read two times but machine didnt read peak of sample accurately. While first parallel showed a peak, second parallel didnt show any peak. 
I cleaned HPLC column with mobile phase but it didnt change results. After cleaning of column i get a baseline but while reading samples, it doesnt show peak each time.
What is your recommendation for this problem?  
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I have no specific experience, but it sounds like you have a source of urinary acid , like an ester. At that pH this ester is breaking apart at the ester bridge giving you more urinary acid than expected. Try increasing the pH of the mobile phase to 3, then 4, then 5 and check your peak.
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Protocol for monosaccharide analysis of polysaccharides by LC-MS/method development/solvent used.
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I use HPLC method to check the monosaccharide content.
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PdCl2 was taken with 0.2M HCl, will it form PdCl42-?
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If you have want PdCl2 at 0.2 M, you will need at least HCl at 0.4 M, this is because for each mol of PdCl2, you need 2 moles of HCl.
PdCl2 + 2HCL —> H2PdCl4.
If you use less than 2 mols of HCl per mol of PdCl2, then you’ll not have the entire reaction of the PdCl2.
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I have produced oleum by adding sulfur trioxide, SO3, to sulfuric acid. It mostly contains disulfuric acid (also called pyrosulfuric acid) but i think this method is not suitable for laboratory purpose so is there any feasible procedure for the synthesis of oleum for laboratory purpose?
Suggestions will be highly appreciable.
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Dear Daniyal Ahmed just in case that this question is still of interest to you: The article cited below contains a detailed description of how to make oleum in the laboratory:
Preparation of Sulfur Trioxide and Oleum
Personally I would suggest to buy oleum from commercial sources as it is an industrial product manufactured on a large scale.
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Oxidized alginate has aldehyde groups. Gelatin has amine groups. I hope that oxidized alginate/gelatin mixtures can form hydrogels by Schiff base reaction and I can control the gel properties by varying the aldehyde amount of oxidized alginate. However, I couldn't make hydrogels. When I mix 3 wt% oxidized alginate and 5 wt% gelatin solution (pH 7.2) together, immediately the precipitation formed.
Could you share with me your explanations?
Following my thinking, there is a strong interaction between negative charge of alginate (-COOH) and positive charge (-NH3) of gelatin that leads to easily form precipitation or aggregation. Following your experiences, how can we make the hydrogels using Schiff base reaction for 2 these polymers? Is there another reason for explaining this phenomenon?
I am looking forward your answers,
Thank you very much,
Thai Thanh (Ms.)
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Hello dear
I have the same problem like the one you explianed. Did you realize the problem? I can not produce gel with oxidized alginate and gelatin. Was the problem the type of the gelatin? Or the pH of the solutions should be specific?
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total phosphorus?
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Calcium Phosphate should not be effected by the persulfate. There would be no reaction of the persulfate with either the calcium or the phosphate. Calcium phosphote is insoluble; however, the solubility is pH dependent. If the solution is acidic below a pH of about 4 , the equilibrium will shitf towards the monobasic form of the phosphate which will result in the solubility of the calcium phosphate.
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When specification limit not known, how we calculate and how we decided the test concentration in RS?
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How we calculate total impurities based on LOQ and RF values
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Hello and thanks in advance!
I'm trying to separate an amino acid standard, but have been only seeing 2 peaks, one internal standard (ABA) and one broad peak around 17 minutes. 
I've been using the same conditions as Liu, J. Chromatog. A, 1994, 670, 59-66, basically, using 6- AQC to derivitise,
wavelength at 248 nm,
Waters Eluent A as eluent A and acetonitrile and water as eluent B,
run time of 46 minutes,
flow rate of 1 ml/min,
C18 AccQ.Tag column.
I'm stumped as to why this is happening. Thanks for any help!
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find info in above mentioned link
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I'm doing OPA derivatization in HPLC-C18 column and should be getting 17 peaks. However, I am getting 20 peaks. Can someone help please?
Mobile A : 40 mM Sodium monophosphate
Mobile B : Acetonitrile:MeOH:H2O = 9:9:2
Online derivatization has been done.
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Has any one have the experience of using FTIR for anaylzing the water vapours concentrationby volume(%) in the gas sample? I have some query to ask related to its validations of results with gravimetric methods.Thanks.Looking forward for your reply.
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Following
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Hello,
I am trying to develop a gas chromatography method for analyzing glycol from glycol dehydration plants. I am using an Agilent DB-Wax_UI column and FID detector. I am getting +/-10% error for my analytes (ethylene glycol and triethylene glycol). Can anyone provide any insight about how to decrease my error?
Thank you very much!!
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I think in simple terms we have a training issue here. Tao, basic GC method development requires a solid understanding of the fundamental chromatography principles and hardware/software used (instrument). Learning these fundamentals takes time (years) and is critical to using and developing proper GC methods that provide accurate data.
You report a 10% variation of some type which has you concerned (and you should be concerned, but do not say what this variation is or how you measured it. Then you comment as follows:
"For the same sample, if I inject it multiple times, I usually get below 1%RSD. It is the quantification that I think I'm having the most problem with." - - So where does the 10% variation come from ? Is it in peak area totals or peak height measurements? For one compound, a few, all of them? What happens if you inject the same std, 6-times, at 3 different concentrations (low, middle ad high ranges)? What is the %RSD?
You also commented that;
"Although my calibration curve says correlation is greater than 0.99 so it came pretty confusing to me." - - You can have variation in peak signal areas/heights because these are averaged before being used in a calibration curve. They are not related to linearity at all. Those types of fundamentals, regarding the basic GC technique, must first be learned to appreciate how all of these parameters contribute to the reported results / data.
Web forums are a very poor training tools when the basic fundamentals are not well understood. While many of the concepts and ideas can be learned from books and articles (which I strongly recommend), hands-on time with a more experienced chromatographer will speed up the learning process for you 100x. My recommendation is that you obtain help locally first. Take some classes (esp. GC manufacturer operation classes), read some of the classic books on the topic, get more hands-on time to run your own experiments to 'see' cause vs effect with the system using standards. Troubleshooting to find a specific actual cause requires being there in-person (assume nothing) to provide high quality assistance, something that we can not do as well remotely.
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How to determine cellulose, Hemi-cellulose, Lignin Content of natural fiber?...What type of chemical treatment should done to determine these contents....Please provide the details which you find very useful.
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There are chemical methods by which the chemical composition of the natural fibers can be determined. For example TAAPI procedure in which the individual components (alpha cellulose, hemicellulose and lignin) are separated and determined quantitatively. There are several research papers on the properties of natural fibers (such as Hildegardia populifolia uniaxial natural fabric, Tamarind Fruit fibers, Borassus fruit fibers, Ridge guard 3 dimensional fabrics etc) available in the literature which describe these procedures.
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I have searched for a recommended way to cite a method from the APHA collection of standard methods
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It's a late response, but I figured it now after struggling with the same challenge. How citing this book is dependent on the edition, assuming 2012 for now. It is generally accepted to cite this book as "APHA, 2012" in the text, although there are two more contributors/authors: AWWA, WEF. The editors are:
Rice, Eugene W.
Baird, a B.
Eaton, Andrew D.
Clesceri, Lenore S.
For the bibliography, it depends on which style you are using. These are other details you should input on Mendeley:
City: Washington, DC.
Edition: 22
Publisher: American Public Health Association
ISBN: 9780875530130
Hope you find it helpful :)
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Can anyone help me with the protocol on how to digest fish feed and faecal samples for determination of chromium using Atomic absorption spectroscopy (AAS).  Thanks
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cAn anyone tell me procedure of nitric acid digestion in plants . i want full recepie step by step
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How can I attach an amine group (-NH2) to a carboxyl group (-COOH)? What are the experimental conditions, such as temperature, atmosphere, pH etc? I want to attach mPEG-NH2 to α-Lipoic acid in water solutions.
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Dissolve the acid in def add doc then add ammonium formate or acetate. Remove solvent work up. You get the corresponding abide. Good luck!
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hello,
I did a soil incubation experiment. I put NaOH 1M traps in my jars. I make assays of NaOH with HCl and I would like to have my quantity of C-C02 g-1 dry soil starting from my equivalent volume of HCl. I find very low respiration and i would like to be sure of the calculation method. Thanks for your help
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I do support Dr M.F.Wahab for fantastc discussions.
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Principle depends on the addition of acid or base at the beginning of the water extract of tobacco
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Isolation
- Principle
Nicotine is a classical alkaloid the separation of which teaches the
main principles of an alkaloid isolation. Consisting of a combination
of two tertiary amines of which the pyrrolidine is the stronger basic
one, nicotine is protonated in the plant and forms carboxylate salts such as formate, acetate or maleate. Therefore, the fi rst and typical step is to bring the alkaloid into a distinctively strong alkaline environment, such as NaOH solution to cleave the organic salts and release free nicotine into the aqueous solution. Nicotine is readily soluble in water due to its ability to act as an acceptor for hydrogen bonds to water.
Another useful property is its volatility with water vapour. This allows
steam distillation to be used for a very selective separation of nicotine
from many other water-soluble tobacco constituents. In the distillate,
the alkaloid is protonated by addition of hydrochloric acid and the
nicotinium ions formed are precipitated by addition of sodium picrate
solution. The yellow nicotinium picrate formed is pure. To obtain the
free alkaloid base, a second alkaline cleavage as with the starting tobacco is necessary with the nicotinium picrate. The free base is extracted from the basic solution with diethyl ether and fi nally purifi ed by a distillation in vacuo.
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Dear colleagues;
What are the novel and accurate methods for testing the following:
  1. Total cholesterol conc.
  2. Triglycerides conc.
  3. HDL-C conc.
  4. LDL-C & VLDL-C
  5. Lipid peroxidation marker (MDA)
Best regards;
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Hello, see the info below you can find some news there.
Good luck!
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I am looking for an analytical method for iron release from the hemin/hematine molecule and further porphyrin set determination by HPLC. Hypochlorous acid could be used but the porphyrin set would be destroyed too.
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A large number of methods exist for porphyrin demetalation which vary in their execution. One of the latest methods uses ultrasound; see: Chengguo Sun, Bingcheng Hu, Weiyou Zhou, Shichao Xu and Zuliang Liu, Investigations on the demetalation of metalloporphyrins under ultrasound irradiation, Ultrasonics Sonochemistry, 10.1016/j.ultsonch.2010.08.010, 18, 2, (501-505), (2011).
Briefly, you need to reduce the iron (III) to iron (II) in the presence of a suitable acid. (ranging from HCl, formic acid to acetic acid). The change in ionic radius in the reduced form of iron makes it easier to expel from the porphyrin ring. Ensure that use either a suitable standard and TLC and 1H-NMR if you have access. The 1H-spectrum for the standard is found rather upfield at around -4.00 pm and should integrate to 2 ppm. Check downfield down to at least 100 ppm to ensure that the iron has been completely expelled. Various methods for demetallation are listed in the above reference. The first useful method was published by the Hans Fischer group and his groundbreaking work: https://www.wikiwand.com/en/Hans_Fischer
Standard PPIX/heminCl can be reliably purchased from Frontier Scientific. Although this post is too late to assist you, it may prove useful to others.
FMDI
Centre for Natural Product Discover, Liverpool.
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I want to solve KOH in an organic solvent .Afterwars, I want to react it with the chloromethylated polysulfone in order to substitute the chloride group by the hydroxide group. So please I want a solvent that can solve them both ( a common solvent ) and what are the reaction conditions
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Dear All,
I have a query regarding solubility of KOH in DMF. When we are trying to dissolve KOH in DMF, color of the solution turns black. What kind of reaction is taking place here?
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Dear experts,
I am struggling to calculate the accurate weights of starting precursors to represent the formula Mg0.95Ni0.04Cr0.01O. The precursors are:
1. Mg(NO3)2.6H2O (M.W = 256.4 g/mol), M.W of Mg is 24.305 g/mol which represents about 9.47 %.
2. Ni(NO3)2.6H2O (M.W = 290.8 g/mol), M.W of Ni is 58.69 g/mol which represents about 20.18%.
3.Cr(NO3)3.9H2O (M.W = 400.14 g/mol), M.W of Cr is 51.996 g/mol which represents about 13 %.
I used 0.5 M (0.025 mol) by disolving the precursors in 50 ml water. To represent the chemical formula above, I variate the precursors amount as follow:
1- Mg(NO3)2.6H2O , 0.5 M x 0.95 = 0.475 M, (0.02375 mol). 6.0895 grams, to represent the amount of Mg, 6.0895 x 9.47% = 0.57722 grams,
2- Ni(NO3)2.6H2O, 0.5M x 0.04 = 0.02 M, (0.001 mol). 0.2908 grams, to represent the amount of Ni, 0.2908 x 20.18% = 0.05868 grams.
3- Cr(NO3)3.9H2O, 0.5 M x 0.01 = 0.005 M, (0.00025 mol). 0.100035 grams, to represent the amount of Cr, 0.100035 x 13% = 0.01299 grams.
by summation and dividing the results, I got , 89 % Mg, 9 % Ni, 2 % Cr.
Therefore, when I consider the wt%. , the calculated values do not represent the formula (Mg0.95Ni0.04Cr0.01O) becuase I use the weights of metal nitrate precursor not the bare elements Mg, Ni and Cr. Further, both Ni and Cr are heavier than Mg.
I believe that the quantitaive EDX results will give me very different values.
I used sol-gel method to produce the gel and heat treated at 400 C.
I hope I will get help.
Thanks in advance
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Mohammed M. Obeid Thank you and good luck to you too for your future work
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I am looking for extra small vials for HPLC. Standard vials with inserts have usually a volume of 150 or 200 microliter and a minimum volume of 10 microliters. For an application I would like to have single vials with a volume below 10 microliters. perfect would be a volume of 5 microliters and a residual volume of <2 microliter. I know there are microtiter plates with total volumes of about 12 microliters a minimum volume of 3 microliters. However for my experiments I would like to use vials instead of a huge plate (I have only 5 - 10 Samples).
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I sort of have a similar issue, though mine is with a reagent -- it's sensitive to light, and oxygen, so I want to minimize the reagent volume in each aliquot. When in use, I only use 0.5uL for each sample (usually no more than 20 samples), so there is a lot of reagent waste. I looked for a similarly small-volume insert or vial to minimize the interaction with oxygen upon being pierced. I found an insert from a supplier that *said* it held 50uL, but they were only counting the little bulb at the bottom, not the entire volume of the insert. So instead, I currently use a 100uL insert, filled only about 1/3 full, and the extra volume in the entire vial is filled with nitrogen. Your question made me think of the dimensions of 10uL volume. This is the result.
There is a problem with the math of the basic measurements -- I did a quick calculation using reference to 10ga, 20ga, and 30ga needles (I'm not sure the width of your autosampler needle) using Wikipedia as a source for width of these gauges. If the vial were to hold a maximum of 10uL, a 10ga needle could drop into the vial only 1.10mm deep (20ga: 15.4mm; 30ga: 131mm). Then the total volume of pickup at a maximum (unless drawing the sample while descending into the vial) would be 6.25uL (20ga: 4.41uL; 30ga: 2.61uL). At such a low volume, you would have to take into account the volume of the metal of the needle. Though it's a trade off: the finer the gauge of the needle, the softer it will become, and less able to pierce a vial septa.
The only other idea (if you want to be a bit creative) is to get short vials and lose them at the bottom of the autosampler well(s), but being short would hold a smaller volume. AND since it's at the bottom already, it would allow for the full extension of the needle.
Consider keeping the trays, covering/washing/marking the used wells, and use other spots on the tray for the new sample set.
Hope that helps give some perspective.
(sorry for the lengthy post and the 4-year delay)
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I have experienced (-) negative values for a particular element in AAS or ICE-AES analysis.
1. What does this really mean and how could it happen? Can we explain it using the calibration curve?
2. I further have observed that there is the same (-) value for a particular element in different samples and changing (-) value for a particular element in different samples. How can it be explained.
eg.
For Mn: Std are 0.3, 0.5 and 1 ppm in 0.1M HNO3
The samples in 0.1 HNO3 and calculated concentration is -0.035 for all (50) samples
For Ca: Std are 0.5, 1 and 1.5 ppm in 1M HNO3
The samples in 1M HNO3 and calculated concentrations are -0.157, -0.181, -0.199 (changing but (-)so on for all (30) samples.
Thanks in advance
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Your calibration is statistical; you are fitting a curve to a series of calibration points. It has error associated with the curve. When you get down to a low enough concentration, and you have calibrated correctly, then you can, statistically, get negative numbers. This is normal; in fact, any decent auditor would applaud you for doing your job correctly. As long as you are not getting large negative numbers then the data is telling you that the element(s) you are measuring are not present at your detection limit. This is also why you determine, and use, a lower limit of detection (LOD) and a lower limit of quantification (LOQ). These indicate the point at which your calibration is no longer valid; you shouldn't report values below your LOD.
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My Problem:- I am working on ammonia sensor. I want to calibrate this sensor in a 1.2 L Airtight Chamber by Liquor Ammonia of 30% concentration and Specific Gravity 0.89.
So, What amount (in volume) of liquor ammonia is needed to achieve 1 ppm concentration of ammonia in chamber to calibrate the sensor.
My Answer:-
Ammoin is very volatile hence I used a fan fitted in the chamber for better mixing of gas in chamber and also for total ammonia evaporation from the sample.
To make a calibration mixture for liquid ammonia, a known volume of liquid is vaporized in a known volume of dilutant air. The ideal gas law states that one gram mole of molecules will occupy 24,500 cc of volume at 25 degree centigrade and at 760 mm of mercury or sea level atmospheric pressure.
One part per million (by volume) is equal to a volume of a given gas mixed in a million volume of air.
1 ppm = (1 gas volume)/(〖10〗^6 air volumes)
A micro litre volume of gas in one litre of air would therefore be equal to 1 ppm:
1ppm= (1µL gas)/(1L air)
According to specification of liquor ammonia 30%
100mL liquor ammonia contains 30gm ammonia
Or, 1mL liquor ammonia contains 0.3gm ammonia
After dissolving 1mL liquor ammonia in 2499ml pure de-ionized water we obtained that:
2500mL liquor ammonia contains 0.3gm = 300mg ammonia
Or, 1mL liquor ammonia contains 1.2mg ammonia
Or, 1µl liquor ammonia contains 0.12µg ammonia
According to Standard Temperature and Pressure (STP) law
17 gm ammonia will occupy 24.5 Litre volumes
Or, 17µg ammonia will occupy 24.5 µL volumes
Or, 0.694µg ammonia will occupy 1 µL volume
Or, 0.833µg ammonia will occupy 1.2 µL volumes
We know that,
1ppm= (1µL gas)/(1L air)
And, We have an Airtight chamber of 1.2L volume
Hence
1ppm= (1.2µL gas)/(1.2L air)
Form above calculation we can derive an equation for ppm calculation for 1.2 liter gas.
liquor ammonia (µl)= (0.833 ×ppm ×dilution)/300
Therfore, If we take 7µL diluted (2500 times) liquor ammonia and placed in 1.2 L Airtight chamber
Then, We obtained 1ppm ammonia concentration in that chamber.
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Follow
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I have done 60 minutes column adsorption experiment for the removal of triclosan. The triclosan solution of known concentration was passed through the column and values of concentration of triclosan was estimated at every 10 minutes of the experiment. Now for the kinetic modeling studies, I need the experimental qe value first. Please, can anyone help?
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Ce and Qe are obtained by batch experiments not column studies. The formulas mentioned by Mr. Omar Khelifi are used in batch adsorption experiments. In fixed-bed studies, you dont have an equilibrim concentration, because the concentration varies by time and during the whole length of the bed. You may not reach to the equlibrium state because of having flowrate.
good luck
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Which mechanism(s) or linker are needed to change a methyl group (-CH3) to a carboxyl or amine groups (-COOH/_NH2)?
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On the plant surface (and in solution), paraquat is rapidly broken down photochemically.
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I'm working on starch, for instance. It has got linear and branched units. In order to estimate the number of OH groups, and the possibilities of making H bonds, I need to know the number of repeating units of the polymer. is there any way to do that?
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First you have to deal with a fundamental difficulty. Starch is a mixture of two biopolymers, linear amylose (MW ca 10E6) and branched amylopectin (MW ca 10E8). So starch has a bimodal molar mass distribution which is very broad. Because for most starches, amylopectin is the dominant fraction (typically 70-80 %) and because the preferred experimental method is size exclusion chromatography with light scattering detection, which is more sensitive to the high molar mass species, the molar mass of amylopectin is a rather good approximation for that of whole starch, except for the amylose-rich starches.
In doing molar mass determinations one has to ensure that the starch has been molecularly dissolved in a way that no molecular degradation has occurred. This is not a simple task. Fortunately, suitable methods have been developed and literature values for most common starches are available. The authors of the paper provided by Md. Abdur Rahman are real experts in the field but their paper does not provide numerical values. Data for various starches were presented in a paper by Yoo and Jane (Carbohydr. Polym. 49 (2002) 307-314) which you find in the attachment.
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Hello Everybody
I am using HPLC with ELSD to determine the unknown concentration of my samples after adsorption test.
My samples contain a blend of two surfactants so i tried to prepare two calibration curves for the two surfactants.
One of the calibration curves is linear where the other one doesn't seem to be linear so is it possible to use any other type of mathematical functions. Or is there any other way to solve this problem. "the Excel file is attached"
Just to add an extra comment: i prepared the preparation of the samples twice to make sure because that's what i was advised to do and i repeated the calibration curve twice and i checked the repetition of the same samples and there were no significant difference.
Your help is highly appreciated.
Regards,
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I think optimize your mobile phase and use suitable column (This observation is from the area u got, where proportionaly change in area respect to concentration).
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If I got 37% concentration of HCl how can I have 5% concentration of it?
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C1 x V1= C2 x V2
C1 is the initial concentration(37%) C2 is the diluted concentration(5%)
for example if you want to prepare 100ml of 5% solution you do the following:
37 x V1= 5 x 100 => V1=13.51ml
So you must take 13.5 ml out of your initial solution (37%) and add them to a 100 ml volumetric flask then add distilled water until the bottom of the meniscus is level with the horizontal line on the neck of the flask.
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We have so many spectroscopic method for the structure elucidation of organic molecule. I have a doubt, which of the spectroscopic method alone can do the structure elucidation? is it IR, NMR, Mass or UV? Because, most of the undergraduate students always ask this questions? I always suggest all the method have its own advantages and disadvantages. It is better to use all the spectroscopic method for getting complete idea of the structure of molecule. Still, which is better technique without of the help of other technique? The question is seems to be so simple, but the answer is little confusing and complicated.
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Structure elucidation involves identification of various parts of structure like its functional groups, double/triple bonds, cyclic groups, molecular weight, etc.
We need to let students know that all the individual techniques have their own specific application.
But, with advancements in Mass and IR techniques they have become more helpful in structure elucidation. Moreover, NMR would be one of the top preference for any organic molecule as it gives almost a clear picture of the structure along with any impurities in the compound.
SO, I WOULD SUGGEST NMR.
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Any instrument or method that can measure lifetime of film samples?
Thanks
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Thanks @Mohammed Mohammed . Really appreciate it!
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Kindly explain the major differences between the concept of catalyst inhibitors and catalyst poisons with suitable examples.
Thanks a lot.
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Miroslaw,
I think of fouling as a blockages that cause maldistribution. A burn will sometimes remove a blockage (e.g. if it is coke blocking a pore) but sometimes it will not and dumping and reloading catalyst is often necessary, especially if he blockage is caused by scale/metals instead of hydocarbons.
Coking/carbon disposition is the most common way for commercial Hydrotreating, Catalytic Cracking and Hydrocracking catalyst to lose actiity. Historically these catalyst were :regenerated" with a burn but recently the trend has been to dump catalyst and send it to an offsite regeneration facitity for screnning and coke burning. Arsenic and lead are posons that will permanently deactivate most catalyst and cause them to be unregenerable via burn.
I think of an inhibitor as a material that competes with reactant for catalyst sites inhibition is reversable. If the inhibitor is removed from the feed the rate of the desired reaction will increase. An inhibitor may also increase the rate of coking. If the calayst site is coked up it will usually require a burn(with air or O2) to remove the coke. that has closed up catalysyt pores and/or blocked active sites
.
Poisoning and coking are forms of catalyst deactivation that usually require a stoppage either for regeneration or catalyst replacement.You seem to disagree with the comment it can sometimesbe removed during a regeneration (usually a burn with air or O2). I agree it is not really a "poison" if you can remove it with air/ burn.
All catalyst can be "regenerated" if you take extreme enough measures.
For my purposes - in the refining indusrty- catalyst is not regenerable if activity can not be recovered with a simple burn or other relatively minor procedures like a wash with a solvent.
However even then the active metals can be reclamed and used to make new catalyst.
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I am analyzing complex samples by Acquity UPC2 coupled to HRMS and I am having trouble with the carry-over effect of polar compounds - sugars. I´ve tried changing the initial wash solvent (MeOH/IPA 1:1) to more polar one (MeOH/H20 up to 1:1) and increased its volume without any success. Anything else I can do?
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Does anyone know of a Acquity UPC2 users forum?
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After used in thermal analysis(30-1000℃), the internal surface of platinum crucible become black perhaps due to its reaction with the sulphur or halogen elements of the samples. I boiled the crucible in 1M HCl for several hours, rinse it with ultrapure water, and immerse it in HF acid for several days, but cannot make the crucible clean and light as before. Could anyone give me any suggestions, thanks in advance.
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I just re-read the question and the answers. If the surface is darkened, this may be due to the formation of Pt-oxide, especially at temperatures below 1000°C. However, these oxides are rather volatile. The only thing to do is to put the crucible in a furnace and heat up to 1400°C in air. The oxides are volatile and will disappear and the crucible looks as new.
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I am wondering if it is possible to use pillar array columns for separations other than in the reversed-phase mode? I have found a paper explaining the difficulty of coating the pillar surface with C18 being the small interpillar spaces, and because of the adsorbed water that may cause polymerization (and thus clogging). However, I don't quite understand how this would translate in modifying the pillar surface to suit normal phase, or other modes. As far as my knowledge goes, the silicon forms silicon dioxide spontaneously, and the surface should, therefore, be modified just as easily as silica-based packed columns.
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Thank you for answering.
What exactly do you mean with HILIC? For that mode, you need a polar stationary phase, and the pillar array format is only available in RP mode. Pharmafluidics only sells C18 end capped coated pillars. This is exactly why I started to wonder about the other separation modes. I understand that when the interpillar distance is too small, it would clog. However, if C18 modifications are possible (which is a very long chain, longer than others), then this made me think that other coatings should be possible as well... but somewhere here in the thinking process I must be making a mistake because I have not found any paper discussing this, or other modes with pillar array columns.
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Hi,
I'm performing TBA assay to measure the degree of lipid oxidation of raw pork, using the steam distillation method with Kjeldahl distiller.
I collected 50 ml of distillate, and it didn't react with my TBA solution so didn't develop the reddish-pink color which can be absorbed at 530 nm.
The distillate should contain some amount of malondialdehyde, but I think my distillate contains only pure water without malondialdehyde.
If the heating temperature is high, distillate is collected very quickly, but it seems to contain only water. So I tried to decrease the heating temperature, then the distillate was just not collected at all.
Please help me, find anything wrong in my procedure...Here's my procedure.
10 g of pork + 97.5ml DW + 2.5ml 4N HCl  ==> Blending, homogenizing
Put it into Kjeldahl flask+distiller
The collected distillate is reacted with 0.02 M TBA reagent dissolved in 90% acetic acid in 100'C for 40 min
The absorbance is measured at 530 nm
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I want to do water and ethanol extraction by an inhibition assay, in which I need to dissolve the extract in 0.5% DMSO. 
Can any one help me with the steps? Thanks.
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1- First, a Beaker or a crucible should be brought, weighed (Assume that the weight is 100 g)
2- Transfer the extract to the Beaker
3- The solvent used in the extraction process shall be disposed of by evaporation of until the dry matter is obtained as far as possible
4- The beaker is weighed after full evaporation of the solvent (Assume that the weight is 110 gm)
5- The weight of the extract (the weight of the beaker with the extract - the weight of the empty beaker) = 110-100 = 10 g
6- The extract is dissolved in the appropriate solvent Ethyl alcohol is often used and an emulsifier may be added (the amount of the solvent is calculated to obtain the desired concentration(
To prepare different concentrations:
1- The extract is dissolved in the minimum amount of suitable solvent and then a quantitative transfer is done to a volumetric flask with a final size of 100 ml (the appropriate size for the quantity of the extract).
The concentration of the extract is calculated as follows
10gm/100ml = 10×103mg/100ml= 100 mg/ml
Different concentrations could be prepared from that stock solution
To prepare 5 mg / ml with a final volume of 100 ml
V1×C1 (before dilution) = V2×C2 (after dilution)( the concentration which we would to prepare )
? ×100 = 5×100
V1= 5×100/100= 5 ml
Take 5 ml of stock solution (Conc 100mg/ ml) and supplement with appropriate solvent to 100 ml in volumetric flask.
To prepare 0.5 mg / ml with a final volume of 100 ml
? ×100 = 5×100
V1= 0.5×100/100= 0.5 ml
Take 0.5 ml of stock solution (Conc 100mg/ ml) and supplement with appropriate solvent to 100 ml in volumetric flask.
In that case we use a DMSO 0.5% instead of the solvent
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Hello Everyone, 
the other day I tried to run a ellman's regent experiment using L-cysteine as my control.  the overall objective was to plot the values obtained from the standards(L-cysteine) to generate a standard curve.Then Determine the experimental sample concentrations ( my actual protein that has 2 cysteines) from this curve. 
Material:
• Reaction Buffer: 0.1M sodium phosphate, pH 8.0, containing 1mM EDTA
• 4.8mM L-cysteine Stock solution 
• 10mM Ellman’s Reagent Solution ( in 1 mL of reaction buffer)
Protocol:
 I Prepare a set of cysteine standards; these standards will be prepared by dilution the 4.8mM L-cysteine stock solution into final concentrations of   1.5mM, 1.25mM, 1.0mM, 0.75mM, 0.50mM, 0.25mM and 0mM of L-cysteine  in the cuvettes. (Total volume of 800uL).
2. Prepare a set of test tubes, each containing 50µL of Ellman’s Reagent Solution and 500uL of Reaction Buffer.
3. Add 250µL of each standard or unknown to the separate test tubes prepared in step 2.
4. Mix and incubate at room temperature for 15 minutes.
5. Measure absorbance at 412nm.
Except, when I tried to my blank 0mM of L-cysteine( 50uL of ellman's regent, 750uL of reaction buffer). the spectrometer did not read anything at 412nm. it gave me xxxx values meaning something could not been read.  The blank has 750uL of reaction buffer and 50ul of ellman's regent, (total vollume 800ul) there is no cysteine sample inside the blank. I think something went wrong with the ellman's regent concentration was too strong or weak for the spectrometer to read at 412nm. Or maybe the reaction buffer doesn't work well for ellman's regent. If anyone has any idea to make this ellman's regent protocol work or have another protocol that works. please let me know.
Thank you
Jesus A. Aldana 
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How did you prepare the reaction buffer?
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FTIR spectra were generated for 0.1 M H2SO4 and 0.1 M H2SO4 which had a soaked polymeric membrane. At first, I thought the spectrum of the latter was a mirror image of the former, but that's not the case. Looking at the spectra at 860, 1010 and 1160 cm-1, supports this observation.
The absorption bands from 1310-1910 cm-1 and 3500-4000 cm-1 were caused by H2O molecules present in the branched polymer (30% PEI in H2O). The issue here is, the doublet at 2360 cm-1, which supposedly represents absorption by CO2 seems to be oriented at different directions for the two samples. What could be the possible phenomenon behind this effect?
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Simple: The CO2 content of the air is different. If the CO2 content decreases after the background measurement, the corresponding peaks are negative in the absorbance spectrum otherwise if the content increases you get the usual positive peaks.
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I have a solution of both Peroxydisulfate (S2O82-) and Hydrogen Peroxide, and most methods used to detect Peroxydisulfate (S2O82-) interfere with H2O2 because of the similar O-O bond. How can we quantify one without the interference of the other?
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Dear Ali,
there were several papers in which detection of peroxydisulfate and peroxymonosulfate was achieved by ion chromatography and HPLC, probably by this you could distinguish between h. peroxide and PS.
Please see:
Moreover, one chapter in this review is devoted to the determination methods of PS:
Regards,
Stan
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I need to determine the molecular weight of a polymeric sample in NMP through GPC. Can it be done through THF column or is there any specific column for NMP.
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N-Methyl-2-pyrrolidone is a regulated substance. Attached is the OSHA method which uses a DB-Wax column in a GC-FID.
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There are 4 factors affecting the adsorption process. I have a data of 30 experiments. I want to optimise the process using ANN GA. I have tried doing it but I am not getting accurate results can someone share their source code or can help me with the same ? I have came up with this code so far. I am unable to perform validation checks when I run my training code. Can someone please look into it and help me with the code.
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I suspect you have not built in the sampling codes at the initiation stage.
Soumitra K. Mallick
for Soumitra K. Mallick, Nick Hamburger, Sandipan Mallick
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We are considering the purchase of a new dissolved carbon and nitrogen analyzer. We would like to know what are the most reliable and economic options. If you know the ballpark cost of an analyzer or have any general input, that would be very helpful. Thank you.
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vario TOC select - TOC/TNb analysis without limitations
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I'm looking for a relatively simple analytical method (colorimetric analysis etc.) for measuring methanol in aqueous solutions in the concentration of about 100 µM ?
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I have tested this method for methanol production from PEC reduction of CO2. provided the quantity of of the methanol is high enough to an extent it is measurable by this method, then its good to follow. But from my experience, methanol produced from CO2 reduction was not detectable by this method..but GC does.
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Please, is this true that Hydrongen and Oxygen can be interact to generate water using induction coil interaction???
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Dear Professor Isam,
I know that Hydrogen with Oxygen interaction to generate water requires a strong power "energy". I just thought this power can be generated from induction coil energy. I thought this idea may be applicable to implement
Thank you very much
Best wishes,
Osman
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I want to ask about courses, certifications or something like that is useful along with PhD in chemistry for personal development and knowledge building as well as those which are helpful in future for career along with PhD ?
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CQA (certified quality auditor)
CQE (certified quality engineer)
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I'd like to know the best databases available, so I can know the best appropriate method of separation, analysis, quantification with regard to chemical identities?
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Dear Sir. Concerning your issue about the best resources/databases/websites for analytical chemistry. Analytical techniques providing more information, in particular molecular spectrometry, are preferred for identification. Other techniques are just briefly considered, with for the exception of chromatography, whose combination with spectrometric techniques sharply increases possibilities and trueness of identification. As a whole, mass spectrometry is superior to other spectral techniques in such features as sensitivity, selectivity, generation possibility of molecular mass/ formula, and combinability with chromatography. Different types of mass spectrometric instruments are outlined, with many performances tabulated. Experimental conditions for identification of volatile, non-volatile, and high-molecule compounds are discussed. Next, classification of chemical methodologies is given where screening and confirmatory methods are noted. Related procedures, sample treatment, and quantitative determination are also considered as ones affecting qualitative analysis. I think the following below links and the attached file may help you in your analysis:
Thanks
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Hi,
I would like to check the bio-compatibility of a polymeric material. what are the biochemical/toxicological test or any other method that I can perform in order to prove the bio-compatibility.
Any suggestions on cell line culture or any other method will be highly appreciated.
Thanks in advance for your kind help and suggestion.
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Dear Sir. Concerning your issue about how to check the biocompatibility of a polymeric material. An in vivo method is described for screening polymeric materials for biocompatibility. The test is based on grading acute and subacute tissue reactions at 7 and 28 days, respectively, following implantation in rats. The method is reproducible and reliable. It is designed to provide uniform test criteria for biocompatibility assessment in the early phases of the development of surgical implant materials. I think the following below links may help you in your analysis:
Thanks
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Is it possible to track the complexation behavior of a polymer with an aqueous dispersion of iron oxide (Fe3O4) nanoparticles through potentiometric complexation? And if yes, is it also possible to investigate this complexation behavior in the aqueous solution of Fe2+ and/or Fe3+ representing the surface cationic species of Fe3O4 nanoparticles?
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Dear Mr. Hodaei,
Your question is interesting in the way you try to understand the behaviour of your material in solution, which can be of potential value in applications such as adsorption. However, your writing mentions Fe2+ and Fe3+ as charge of iron, while the oxidation states II+ and III+ were mentioned, respectively. The apparently small difference has strong consequences to the overall speciation. No iron in such constellation is assumed free and ionic, but bond to oxygen. At the outer surface of FexOy nanoparticles, oxide or hydroxide groups will determine governing charge and interaction towards species. Avoid "complexation" as choice of interaction unitl you actually characterized that interaction mechanism . It is not likely FexOy have the potential to chelate certain compounds in solution.
Regarding the available analytical instrumentation, consider solid phase characterization, for instance using TEM-EDX, EELS, Mössbauer spectroscopy or XRD. The reference applies some of these techniques for the characterization of Fe3O4 nanopartikels in a porous host.
Best regards, Karel Folens
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I want to make a 1M solution of PbI2 in DMF. I mixed 460 mg PbI2 in 1 ml DMF and kept it for overnight stirring at 70 oC  and  found that only about 40 % of PbI2 was dissolved in DMF. How can I solve this solubility problem?
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1 M (460 mg) of PbI2 is fully soluble in 1 ml DMF at 700C  for over night stirring. PbI2 in DMF is transparent yellowish solution at 70C but at room temperature it,s converted into gel like appearance but after heating it again converted into transparent solution. I have prepared this solution many times for the 2 step perovskite coating. In your case I think there is problem with PbI2 purity. I am using PbI2 of sigma (98% Purity). 
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"A properly designed guard column does not deteriorate the separation. As a matter of fact, a well designed and well packed guard column using the same material as in the analytical column is a small column extension that ADDS to the column plate count. It thus IMPROVES the separation. In some cases, a good sample preparation can eliminate the need for a guard column. However, in some cases it is virtually impossible to do so. This is the case when one is working with samples of biological origin: plasma, urine, meat, etc. Under these circumstances, a column contamination is practically unavoidable" 
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I do not see how the paper you reference is related?
Mel: A guard column is a generic term to describe any "column" which is placed in front of the actual method (analysis) column to protect it. We characterize columns, not 'guard columns' so I am unaware of any articles designed to compare or describe them. Normally, a guard column only contains a filter or a tiny amount of stationary phase and the goal is to make them invisible (you may introduce more error by adding them). They add delay volume and can result in band spreading (undesirable). Regarding efficiency, you asked "how low it can be"? That question can not be answered as guard columns are not used for (and should not be used for) separation, so 'efficiency' is not used. This is a small filter we are talking about. 
To generalize, Guard Column dimensions should be very small as we do not want them to negatively contribute or impact the chromatography method being used at all. They principally serve as an expensive filter or solvent saturation device (esp in NP) only. Normally, they contain the same packing material as the working column (so as to NOT change or interfere with the actual method). They are NOT replacements for an actual HPLC column at all. We do not normally use them in method development. "Efficiency" is not relevant and measuring it also is not relevant. Those metrics are reserved for actual columns used in the analysis, not a pre-filter such as a guard column. Guard columns are normally described by their packing material details (support type, functionality and particle size).
Why are you interested in these accessories? We do not use them for analysis.
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Just wondering about their expense to make. Does liquid propulsion cause excess interference in IR?. A multifunctional HPLC that checks for impurities would be more valuable. Does the liquid sample need to be stationary to be ananlytes by IR?.
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Most HPLC's come equipped with a UV detector (PDA/DAD).  An IR detector is known but not typically used since everything absorbs (thus molecular spectroscopy) including mobile phase solvents like Methanol, Water....
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We are estimating polysorbate 80 by HPLC, initially we were getting expected result, but the sample sample when we analysed after 2 months, we are getting higher values. Can anyone say why this is happening?
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Dear Anindita.
Kindly share literature method as i am also struggling for Estimation in Cream 
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There is a simulation project that I am working on. We have to find the pH of a solution which contains the above components. Is there a formula for calculating the pH of the mixture, the mole fraction of H2O is 0.9996, mole fraction of HCOOH is 0.0002 and mole fraction of NaOH is 0.0002.
P.S:  the solution is a waste water 
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After following the suggestions of my RG colleagues, a sign that you are on the right track is that the pH you will find out will be above 7 because:
HCOOH & NaOH are completely soluble in water & they will undergo a neutralization reaction: HCOOH + NaOH → HCOONa + H2O .
The product is an aqueous solution of sodium methanoate "which is a basic salt".The use of a pH meter for this solution will confirm that the pH is > 7.
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Actually, I have to come to grips with using a GCMS ( Perkin Elmer Clarus 500/560s) and have difficulties to find informations about the Special Needs of highly volatile substances like Ether, Chloroform etc.
Do you have general tips to handle highly volatile substances in GCMS (like experience with preparation or Setting of the GC) or know where to find them?
Or aren't there any general using conducts and I have to get the Information for every single substance (thats what I did first but its not the solution)
Thanks!
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Optimizing the gc-part (separation) without the trap is a good advice. You can introduce the trap later if you are not satisfied with the sensitivity. With the trap you'll gain a factor 20 to 100 ,depending on the analyte and settings, and it si not that hard to master. The main problem, in my opinion, is finding a suitable internal standard. For the selection of the trap there is plenty of information online about the properties of available absorbents although your manufacturer may offer a limited choice (PE has only two traps). Filling your own traps is an interesting option.
In your case , if you'll need the trap, I would go for a low equilibration temperature and a trap that is not retaining water and avoid excessive dry purging.
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I am developing a new method for phenolic compounds (especifically: chlorogenic acid, caffeic acid and vainillinic as well). RP-Column C18 (Venusil XBP C18 250 mm x 4.6 mm x 5 um). My mobile phase system includes:
ACN (A) and acetic acid 0.5% in ultra-pure water (B). I have set the wavelenght to 320 nm. My flow rate is 1.000 ml / min and my column temperature is 25 °C. It's a Knauer machine equipped with a quaternary pump and a LPG system and a degasser system, too.
I have flushed my column with isopropanol for around 1 hour till I see no peaks or drift in the baseline. Then, I made baseline with 10 % ACN and 90% of acetic acid solution (0.5%). When I sample with a blank (the same mobile phase) I get it with noise and peaks in my "baseline".
Any help would be appreciated.
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Typically you get that kind of noise out of a UV detector when you either have a saturated reference channel or you have bubble formation. Not familiar with your system, so I have no idea as to how you are mixing the ACN and H2O (low pressure, high pressure, etc), and therefore I have no idea if you could have bubble formation. 
I question the need for a 100 minute separation for something that is relatively simple. Your gradient certainly can be significantly faster. I also question the choice of ACN. You know for certain that the phenols are highly soluble in alcohol; why not use methanol rather than ACN for the separation? 
Have you checked the pka of the compounds? Are you certain that acetic acid is your best choice? I would have probably leaned more towards formic acid or TFA for this analysis.
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I have a liquid mixture consisting of a two compounds of unknown concentration. I have calculated the calibration curves for each compound separately. Now, I have prepared a two sample solutions of 1000 micro litre. One sample consists of 10 micro litre of the liquid mixture and another sample consists of 20 micro litre of the liquid mixture. I have injected both the samples one after another into the Gas Chromatography. These two samples are giving different concentrations of the individual compounds present in the liquid mixture. Here, my question is if I am analyzing the concentration of the individual compounds in a same liquid mixture, the concentrations are different for 10 micro litre and 20 micro litre samples of the same liquid mixture. Why? In order to get the same concentration of the liquid mixture compounds by taking whatever amount of the sample from the given liquid mixture, what should I do?
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Dear V mani Rathnam
(1) You need to read a simple text on the fundamentals of quantitation in gas chromatography.
(2)Your faculty advisor should have given you this fundamental guidance before allowing you to use the instrument.
(3)None of these instruments is an 'answer machine'. The best technique for quantitation depends on the conditions, sample and hardware.
**** I personally do not trust any commercial software to do the job right, so I export all raw signal data into Excel worksheets and do my own analysis of the data. I strongly recommend that students and professionals alike do this until there is proof that the instrument and software are truthful.
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Please can any one help me?
I fabricated four aluminum matrix composite with SiC and MgO, and I need the best method to find the exact chemical composition after casting.
What is the best method to analyze the chemical composition of metal matrix composites?
I used EDS, but the Si did not appear.
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XRD will provide information about the phase composition. You can use XRF in order to get the detailed chemical composition. Also, the use of SEM attached with EDS will provide information on elemental composition.
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 I want to separate a heavy oil sample with boiling temperature ranges, 350 - 750 C, ex) 350-450, 450-550, 550-650, 650-750 
However, In deep vacuum distillation column (1 torr), the fraction of temperature above 540 C can not be distilled. Because, In above 540 C, thermal cracking can occur. 
I want to know how I separate heavy oil according to boiling point, not using deep vacuum distillation column. 
I think that chromatography like HPLC or GPC can be the alternative. 
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Thank you for this question because it aroused my curiosity in the search for the subject and knew the beautiful information about the subject
  Please, press on the following website link for more information
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As an alternative to liquid/liquid extraction the use of SPE disks for the extraction of POPs from the wet and particulate deposition seems to be applicable as can be taken from some literature sources. However I do not find some references dealing with the validation work of this critical step of the analytical protocol. 
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Thank you for your answer and sorry for the late response. We just started with the project and we try to chractarize real samples as thoroughly as possible. However, you were already pointing to the key fact: The elution of particle sorbed POPs and their recoveries. We will perform some validation work with real samples concerning the elution..... 
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Sample preparation
Analytical column
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Dear Ahmed,
Thank you very much for the article. Your help is much appreciated.
Kind Regards,
Sony
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To find composition of binary system of CPME and Acetic acid
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 CPME (supposedly Cyclopentyl methyl ether) is not a Bronsted acid, so the simplest method is titration of acetic acid in the mixture by a base. The mixture may be diluted in water or in MeOH/H2O or EtOH/H2O if CPME is not soluble enough. A pH-meter or an acid-base indicator may be used for determining the equivalence.
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Effect of moisture in the purity of organic compound.
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1) Weight difference using analytical weights after storage them on the dry compounds (i.e. P2O5, etc)
2) Absorbed water can work as medium for organic compounds hydrolysis
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I am doing experiments with HPLC. I prepared 3 vials from same sample and put them to rack of the hplc. Before that i took the sample from cool batch and i am suspecting that the temperature difference can effect on the peaks? I completed all the preparation in 15 minutes. The peaks are in the image. How can they be different like this? Same behaviour but with different height.
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It looks like your peaks have comparable responses, but the baseline is all over the place.  Is this a UV detector?  If so, what wavelength are you using and what is the mobile phase solvent system?  It looks like one of the chromatograms has a stable baseline whereas the others show some drift.  My initial thought would be that this is either lack of equilibration, or a loss of equilibrium during the analysis.  This looks like more of an instrument/method issue rather than a sample effect.
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The purpose is to detect mole fraction of CPME in the binary mixture of CPME and acetic acid.
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Since Cyclopentyl methyl ether (CPME) is an ethereal solvent, will DB-FFAP (agilent) work for it ?
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While searching for this i had come to know that "The determination limit for carbon, nitrogen and sulfur with sample amounts of 2 to 3 mg was proven to be at about 0,05 w-% (500 ppm) with an uncertainty below 0,02 w-%". so the U(X)= +-0.02 %. Is it correct or the uncertainity is different for C, H, N and S.
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Agreements with  Peter Apps
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I have a technical grade material is approx. 4  year old. I would like to know how much its been degraded overtime. Basically, I would like to confirm the % purity of the active ingredient content left in it by using Gas Liquid Chromatography. 
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Paul Milham the material is technical grade insecticide. 
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Dear colleagues,
I need to idetify peaks in the ESI MS spectra (the txt file is attached) . In this spectra I need to find the folic acid that was attached to the NH2 groups grafted onto Ag nanoparticles. The folic acid was removed from NPs by chemical treatment with trifluoroacetic acid in H2O and then the solution was introduced into the ESI MS.
Thanks a lot in advance.
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The spectrum was acquired using FT ICR MS Bruker Apex Ultra in ES ionization mode using ionization potential 4 kV. The flux of solution was 2 microL/min. Spectrum was averaged from 200 scans.
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Whiçh will elite first in chloride, chlorite, chlorate, and perchlorate ions in ion exchange. If we go through molecular size the pattern of elution will be same as  i mentioned above in the question itself. But when we are doing experiment, it was observed that chlorite is eluting first before chloride even though the molecular weight of chlorite is more than chloride. Kindly clarify?
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See attached link,  it's the US EPA method and shows chromatograms of elution patterns of the anions on different columns (last page).  Also column manufacturers are a great source of information..for instance if you have a column from Dionex - see atttached IC column manual.
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How can the interference of excipients in the dissolution results be minimized when the quantitative procedure is by UV-vis spectrophotometry?
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Try standard addition (spiking) method.
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When I analyzed oligonucleotides by LC-ESI-TOFMS with HFIP-TEA system, the charge-state distribution was different in two batches of experiment but same method. How to explain this and how to obtain higher charge-state on LC-ESI-TOFMS using current mobile phase system.
Thanks
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Thank you all for the responses.
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 my blank (contorl) is incolor ????
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The only reaction that I recall were Salicylate is used is the Bertholet reaction for ammonium ion, not hydroxyl radical.
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I weighed 100 mg of sample and digested it in 8 ml of 6 M HCl. After digestion, I filtered through 0.2 um and dilute with 25 ml distilled water before pH adjustment to 2.2. The final volume after pH adjustment was approximately 45 ml. 
I pipette 0.01 ml and derivatize with 0.09 ml of my derivatization reagent solution and 0.001 ml was injected and analyzed with the UPLC.
The UPLC quantified the amino acids results in pmol/ul.
For example, Met concentration of 1.520 pmol/ul was obtained, how do I go about the calculation to obtain the amount of Met in my original sample???
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My recommendation is As with Sandra has mentioned
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Hello. I'm looking for some advice regarding gas chromatography analysis of cholesterol. Can anyone share a method that has worked in their hands? I have read papers and have almost all the parameters but would like to see what has worked well for others.
Thank you
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Well there you go! I was going to recommend trimethylsilylation to increase its volatility.
I am glad it is working for you now.
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Hi guys, I have a question.
I have extracted 0.5 g biomass using 5 mL of solvent. From this, 40 uL were used to calculate the total phenolics content (TPC).
40 uL extract + 1560 uL distilled water + 100 uL Folin reagent + 300 uL Na2CO3. Using absorbance of 725 nm, and based on gallic acid calibration curve, we have only got 25 mg/L GAE. How can I convert it to mg/g biomass?
Does the dilution using 1560 uL distilled water affect the calculations?
Thank you.
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No if the calibration curve was constructed considering 1600 uL of standard. 
To convert:   25 mg/L * 0.005 L / 0.5 g
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Please  suggest alternate solvent to prepare Grignard reagent.
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You need a slightly polar aprotic solvent for preparing Grignard reagents (that is why diethyl ether & THF are extensively used). I thought like you & tried, in the past, 1,4-dioxane but it did not work well. Dibutyl ether was a good solvent in preparing & protecting the Grignard reagent until it did its function. Wishes for success in your research.
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I am doing thermal analysis of sodium azide. In dsc and TA there is always residual mass left.. is there a way to get complete combustion?? Is there anyway to achieve complete combustion in dsc? It need not be related to sodium azide also.. Please do help..
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Hi Midhun C R
As a follow up to Alexander's answer, the attached paper will be useful
2NaN3 + 1/2O2 --> Na2O + 3N2   (thus a white Na2O residue will be obtained if heating in air or O2)
NaN3 --> Na + 3/2N2 (a grey, highly reactive residue will be obtained if heating in an inert atmosphere such as N2)
Best
Geoff
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Lets assume that i used the SIM to quantify a mixture having 2 compounds, A and B. Based only on peak's area, can I say that compound A has higher concentration than compound B? Or should I do the calibration first to draw such a conclusion.
 
I'm sure that with classic chromatographic detectors, such as FID for CG or UV in HPLC, we can’t say this since the peak area depends on compound’s quantity in the mixture and its sensitivity toward the detector. So I wonder if it is the same in case of GC/MS or HPLC/MS.
 
Thank for your timegg
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Short answer: You cannot make a determination that A has a higher concentration than B unless each compund is very similar in structure. If you think about the "original" mass spectrum of A, the peak you chose for your SIM quantification calculation peak might be the only significant peak - Like the parent 78 peak in benzene is roughly 1.5x the intensities of all of the other spectral peaks combined - Whereas for hexane the parent 57 peak is only about a quarter of the intensity of all of the other peaks combined. This is ignoring other variables like the relative efficiency of ionization. You must do a calibration unless the spectra are almost identical, as they would be for, say, different dichlorobenzene isomers. See: hexane and benzene spectra links.
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Dear all,
What is the relation between pKa value of adsorbent (activated carbon) and it's capability to react with base (alkaly solution) in Boehm titration? And how to find the pKa value of carboxylic acid, phenolic, and lactonic (in boehm titration)?
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The pka of DBU in acetonitrile is 24.34. The pKa values are affected by temperature and the solvent dielectric constant. Is there a formula to convert pka values from one solvent to another as well as temperature?
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There are propiertary software where you can simulate it,  but empirical methods have still no rival 
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I have problems to dissolve 4,4 mg of Laccase from Rhus Vernicifera,  I have used a buffer phosphate pH 7 (0,1 M), but it does not work. 
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Hi Juan! How did you solve this problem?
Thank you so much for the attention.
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I need to determinate European-wide authorised organic UV-Filters in sunscreen formulations like: p-aminobenzoic acids and its derivates, benzophenones, benzylidene camphor derivatives, salycilates, triazine and benzotriazole derivates, methoxycinnamates, dibenzoylmethanes.
I work with Agilent 1220 + eclypse XDB - C18 column 4.6x250 mm.
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You may want to review this!  I assume other HPLC manufacturers have similar methods like Waters and Agilent.
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I my method these three products are coming in "M" shape manner. So its difficult to analyze.
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Dear Shuvashish Behera,
If the column is new and your not getting proper separation, there is a fault in your method. if the column is already used and the column pressure more than 980 psi, then regenerate the column with 25mM sulfuric acid at 0.2mL/min for 30 to 48 hr. And equilibrate the column with eluent for 12 hr or more. den run the sample. If problem is still persist, run 5% methanol as mobile phase in reverse flow for 24hr or more den try.
All da best.
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I am running spectrophotometry of two known concentration of acetylsalicylic acid with an unknown aspirin concentration, how do I use this two values to calculate for aspirin concentration?
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Dear Christina Gabion,Hi,
    If You have two points of absorbance (A) of course, plus the (A) of the unkown, you can use the Bracketing method assuming the calibration of Beer's law is slightly curved.
 You can do that as follows: Asuming You have the Concentrations (C1 and C2 and Absorbances As1 and As2 of your Standards) and for the Unkown (Cx  and Ax).  Write this Equation first  [ As1/C1 = Ax/Cx = As2/C2 ]. Note that, itis Important that both standards points must be very close to the unknown's point of Absorbance. Then make another Equations as follows:  [ (As1- As2)/(C1-C2)] = [(Ax- As2)/(Cx- C2)] ...Here also for easy calculation make the solution concentrations such that As1 of larger value than As2  and Ax larger than As2.   You can see that  ( Cx ) is the only unknown in the equation. I am Sure You can Solve the Equation easily by Yourself.  Thank You and Good Luck.
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Hi everybody! I was wondering if any of you work with Acrylic acid N-hydroxysuccinimide ester a.k.a NHS. Commercialy, it's available as a white powder and I'm trying to make a solution with it using toluene, yet it doesn't dissolve, not even a bit. Any help is useful.
Thanks!!!!
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Not yet, I´m a student of this innovation carreer, and not began with the PFI
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in APha 2350e use of KI, starch, Na2S2O3, H2SO4, then say use of KI trap and send bubble to KI, then in 10 min or any time ( lower time is more speed of measurement). then mix a 10ml of H2SO4 with KI and now color is like brown. then say titrate with Na2S2O3 until "the yellow iodine color almost disappears". and then add 1-2 ml of starch to change color to blue. now I can't see yellow color is disappear. in some of paper say "until KI is colorless and I can't reach to white color".
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Hi are you referring that you can't observe the colour change from brown to yellow? Are you using trap other than water ? End point of titration should give you a transparent solution (Brown -> Yellow -> Add starch turns purplish blue -> Colourless) 
The aim of sodium thiosulfate titration before adding starch indicator is to remove interference faced of binding starch with iodine when presence of too much iodine in solution.
If you add too much KI solution, you need a lot of sodium thiosulfate solution for your titration. Did you check the concentration of sodium thiosulfate and KI solution you used ?
Even though sulfuric acid was used in APHA, I more prefer HCl as sulfuric acid is an oxidizing acid which may contribute to your final result. 
Perhaps you can upload your titration pictures, or video for a clearer image of the problem you faced.  
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In AOCS 29-C Method we are using for 3MCPD analysis but now we are planning for Glycidyl ester analysis in palm oil. Glycidyl ester Which standard derivative you are using for this AOCS 29-C method?
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As palm oil has major amounts of palmitic and oleic acids, glycidyl ester of palmitic acid or glycidyl ester of oleic acid can be used
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Thorin (IUPAC: Disodium 3-hydroxy-4-[(2-arsonophenyl)diazenyl]naphthalene-2,7-disulfonate)
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Thorin is a tridentate ligand; barium can coordinate two of them in an octahedral coordination. For discussion of tridentate azo compounds, see Comprehensive Coordination Chemistry, ed-in-c. Sir G. Wilkinson, Pergamon, 1987, vol. 6, Section 58.2.3 pp.46ff.