Science method

Analytical Chemistry - Science method

Analytical chemistry is the study of the separation, identification, and quantification of the chemical components of natural and artificial materials. Qualitative analysis gives an indication of the identity of the chemical species in the sample and quantitative analysis determines the amount of one or more of these components.
Questions related to Analytical Chemistry
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Dears,
I'm using the UV/vis method to determine water-soluble chrome in cement as follows:
I take particulate mass from dichromate to make a stock solution then take various volumes of aliquots into a 50 ml volumetric flask to set up a calibration curve.
for measuring the sample, I take a 25 g sample and 25 ml of water then filter and take 5 ml of filtrate into a 50 ml volumetric flask and dilute to mark with water after adding a color indicator.
my inquiry why don't I consider 50 ml dilution of aliquoted sample in the calculation equation ? and if I deviate from the method and make a dilution of the aliquoted sample 100 ml instead of 50 ml what does the formal calculation equation become?
#analytical Chemistry
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- Why don't I consider 50 ml dilution of aliquoted sample in the calculation equation ?
Because you are diluting both, sample and standard, to the same final volume of 50 mL.
If you decide to dilute your sample to 100 mL instead of 50 mL, this means that the concentration value that you will get from the calibration curve must be multiplied by a factor of 2 (because the sample is now twice more diluted than the standards).
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Can a published journal article be submitted to conferences?
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It is quite common to present talks or posters on the basis of previously published papers. However, care must be taken when contributing to the proceedings of the conference so as not to infringe the copyright of the journal's publisher.
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For those working in the field of Mass Spectrometry, Chromatography and allied topics, and based in NY state, we are launching a new local discussion group !
Feel free to sign up as member to be part of it.
We will organize in-person events (main area: Buffalo, Syracuse, Ithaca, Corning, Rochester) and virtual meetings - which anybody can attend !
Soon to be listed officially among other local discussion groups on the American Society for Mass Spectrometry (ASMS) website.
Thierry
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ahah hello All !
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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 am measuring primary aromatic amines by UV-VIS and using the NEDA solution as my coupling reagent. The method says that the reagent needs to be made fresh every day. However, the solution is sold commercially from 0.1-1.0% with a shelf life of 6-12 months. Why does it have to be made fresh? What is its stability? Is it a temperature or UV dependent reaction? Can storing in a brown(amber) bottle and/or refrigerating allow for longer use?
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In such cases, it is preferable to prepare it daily and avoid its instability as a result of it being affected by various conditions such as light, temperature, etc. It is best to prepare the amount as needed daily
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Dear colleagues,
We have recently optimized a TDS-GC-MS method for VOCs (SVOCs) analysis. (Gerstel + Agilent).
A high-temperature column with mid-polarity is chosen for a better resolution (similar to DB-624ms but with a higher operating temperature of 300/320 °C).
Although the desired separation is achieved with a programmed-temperature method (final temperature: 290 °C), some analytes with low boiling points, such as dichloromethane, benzene, and heptane, show unacceptable intensity variation. (The RSD of three replicas can be as high as 30%). On the other hand, compounds with higher boiling points (such as naphthalene and pentadecane) are more stable. (RSD < 5%)
We further lower the final temperature of the method (from 280 °C to 260 °C), and the repeatability of benzene and heptane is much better (RSD < 5%), while the dichloromethane is still fluctuating (RSD ~ 15%).
Any explanation for this phenomenon?
p.s. the column pressure can be very high under high-temperature
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Hey there Junlong Huang,
It's great to hear about your progress with the TDS-GC-MS method for VOCs analysis! Now, regarding your question about the final oven temperature and its influence on the repeatability of low boiling point analytes, let's dive into it.
The fluctuations in intensity you're observing, particularly with dichloromethane, benzene, and heptane, can indeed be puzzling. The change in final oven temperature seems to have a significant impact on the stability of these compounds, with lower temperatures showing better repeatability for benzene and heptane but not so much for dichloromethane.
One potential explanation for this could be the volatility and thermal stability of the compounds. Lower boiling point analytes like dichloromethane are more sensitive to temperature changes, and even a slight variation in final oven temperature can lead to fluctuations in their intensity. On the other hand, compounds with higher boiling points like naphthalene and pentadecane are less affected by these temperature changes, hence the more stable RSD.
Additionally, considering the column pressure under high-temperature conditions is crucial. High pressures can exacerbate the volatility of low boiling point analytes, leading to increased intensity variation.
In summary, the interplay between compound volatility, thermal stability, and column pressure under high-temperature conditions likely contributes to the observed phenomenon. Fine-tuning the method parameters, such as oven temperature and column pressure, can potentially mitigate these fluctuations and improve repeatability.
Hope this sheds some light on the issue! Let me know if you Junlong Huang need further clarification or assistance.
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In 2009, while investigating whether injections of methylcobalamin would help my chronic health condition, I chanced upon an intriguing happenstance. The contents of four vials (from a batch of twelve vials) were remarkably effective. All up, over a two-year period I injected methylcobalamin from a total of 41 vials (from four different batches). Injections from 37 of the vials made no impact whatsoever on my condition. Injections from the four effective vials were not consecutive so this wasn't a situation where an initial good response waned.
From the batch of twelve vials that contained four effective vials, the first two effective vials were discarded after use. I saved the remaining ten used vials.
In early 2012 I had the dregs from the ten vials analysed (HPLC at 361 nm). Unfortunately I could not distinguish the two effective vials from the other eight vials so the best I could achieve was to discover if there was anything different about two of the ten vials.
A methylcobalamin injection in light-protected glass ampoule from a different manufacturer was used as the standard (i.e. Methycobal® made by Eisai Co Japan).
Along with the dregs from ten used vials, content from an unused but expired vial (which had been stored correctly) and content from an unused but current vial (sent directly to the analytic lab from the manufacturer's premises) were analysed.
HPLC indicated the standard (i.e. Methycobal®) was pure. It contained two major peaks, the main being MeCbl (eluted at ~ 19 mins) with a smaller OHCbl peak (eluted at ~ 13 mins). Identity of these peaks was subsequently confirmed by MS.
HPLC of the remaining 12 samples (10 x dregs from used vials + 1 x expired vial + 1 x current vial) indicated all were similar to each other. All 12 samples contained four major peaks. Two of these major peaks corresponded to the two peaks in the standard (i.e. MeCbl + OHCbl). Relative ratios of these peaks was as expected – i.e. more MeCbl had degraded to OHCbl according to age of product.
All vials contained significantly more MeCbl than OHCbl (gauged visually from height/width of peaks and subsequently confirmed by calculation of area under peak).
The lab is a reputable commercial lab with up-to-date equipment.
The results look 'pristine'.
All major peaks are symmetrical, narrow, distinct, well separated, no tailing, twin peaks etc.
The lab ran blanks before and between samples.
The order of run was –
10 x dregs* > 1 x expired vial > 1 x standard (Methycobal®) > 1 x current vial
* The first 4 x dregs were rerun the following morning (approx 20 hrs later) because operator was not happy with initial results (I think there was rt drift)
Additional listed ingredients do not account for the unidentified peaks.
Additional listed ingredients –
• Methycobal® – D-mannitol 50 mg (per 500μg MeCbl in 1mL ampoule)
• The vials – Sodium Chloride 18 mg (per 10,000 μg MeCbl in 2mL vial)
Neither product contains preservative.
Concentration of the samples for analysis made from the dregs varied due to variable volume of dregs in each vial.
Looking at the HPLC chromatogram –
Visually it is obvious that two of the ten vials with dregs contain significantly more of one of the two unidentified major peaks (eluted at ~ 15 mins). Relative to the height of the MeCbl peak this peak is ¼ to ⅓ MeCbl height in 8 x dregs. In 2 x dregs it is around ½ the height (i.e. there is around twice as much of this substance in 2 x dregs than in the other 8 x dregs).
I used the height (mAU) of the MeCbl peak to plot a standardised graph of the height of the peaks in Excel. That is, I multiplied the mAU for the MeCbl peak of each sample by a factor^ so that MeCbl peaks from each sample were equal – i.e.they appear as a single dot on the Excel graph. (In the chromatogram the mAU of the MeCbl peak for the standard + expired and current vials was similar but the mAU for the dregs varied due to limited volume available for analysis.)
^ For each sample, mAU of each major peak was raised by the same factor (i.e. factor needed to equalise MeCbl).
When plotted in Excel the results look orderly. The unidentified peak at 15 mins is more or less the same height as the OHCbl peak for all samples except for 2 x dregs. The unidentified peak at ~ 12 mins is a little lower than the OHCbl peak in all samples. (These two peaks are missing from the standard.)
The OHCbl peak is lowest in the current vial and in the standard – I'll call this the baseline. OHCbl peak is approx 70% higher than baseline in expired vial and in 6 x dregs (in 4 x dregs OHCbl is ~ 55% higher than baseline).
The unidentified peak at 12 mins is lowest in the current vial (baseline). It is around 70% higher in the expired vial, and higher still in the 10 x dregs (varies from 130% to 250% higher than baseline, evenly distributed through this range).
The unidentified peak at 15 mins is lowest (baseline) in current and expired vials (around 20% higher in expired than in current vial). In 8 x dregs the height of this peak varies from 36% to 85% higher than baseline (evenly distributed through this range). In 2 x dregs the height of this peak is 200% to 220% higher than baseline.
The baseline for each peak:
~12 mins 175 mAU
~13 mins (OHCbl) 375 mAU
~15 mins 357 mAU
~19 mins (MeCbl) 2270 mAU
At the time of HPLC analysis the attitude from analytical lab and manufacturer of vials was that it was virtually impossible for there to be any difference between vials within a batch. The lab's report – on the HPLC chromatogram – advised all vials were similar and did not comment on the disparity between height of peak at 15 mins in 2 x dregs. The lab attributed the extra two major peaks in the vials to an unlisted ingredient (when questioned the manufacturer resorted to legalese, but it is unlikely there are any unlisted ingredients in the vials).
The lab considers the method it used its IP and will not disclose. However, it used a phosphate buffer. After HPLC there was no residue left to analyse in the 10 x dregs. The lab suggested it could develop a different method, suitable for LC-MS, and run a sample from the expired or current vial. It offered to provide raw data on 20 peaks but I would not know which, if any, of the 20 peaks corresponded to the two unidentified major peaks found in previous HPLC. I couldn't see the point of this exercise.
I sent all samples to another lab (at a major university). The lab advised there was no residue for analysis in the 10 x dregs. It analysed a sample from the expired vial and from a new (unopened) ampoule of Methycobal®. The previous lab would not disclose its method so this lab used the method outlined in Japanese Pharmacopoeia, although it used 361 nm rather than 266 nm. This lab could not find the additional two major peaks (using C8 reverse phase ODS column with phosphate/methanol buffer it found only MeCbl and OHCbl in both samples, which it identified using MS). In further attempt to find the additional two major peaks the lab used a C18 column with water and acetonitrile under acidic conditions but chromatograms from the two samples again looked identical (with two major peaks). The lab attempted to identify these two fractions using static nanospray MS but results were inconclusive – "It is worth noting the fractions collected did not contain the pink colour common to all cobalamins. . . . The ion counts from all the fractions were quite low which was surprising given that the fractions should have been very concentrated."
The analytical chemist later elaborated on this aspect of her report –
"I cannot say definitively that these peaks from the C18 column are not cobalamin. It is possible that only a small amount of cobalamin eluted and the majority remained on the column. However, it is also possible that it was not cobalamin but something else which did not ionise using ESI and therefore could not be identified. The evidence is not conclusive one way or the other."
The samples were returned to the first lab for repeat analysis under identical conditions (I requested this include using the same HPLC analyser and operator).
The lab was certain its previous HPLC did not find ghost peaks and was sure it would find the peaks again, so it considered my request for identical conditions unnecessary.
HPLC was run using same method but different analyser and operator. The results were more or less nonsensical. The lab advised it was the fault of the samples (it claimed the university lab had most likely mishandled the vials/ampoule). The chemist advised that he believed material in vials and ampoule had fully degraded to OHCbl prior to analysis. I thought the results indicated the samples had degraded rapidly during HPLC.
Eventually the lab agreed to run HPLC again, but again declined to use original analyser and operator.
This time it checked degradation of samples over time (and included an MECbl standard purchased from Sigma-Aldrich).
Results indicated that material in the vials and ampoule had not degraded (plenty of MeCbl was present). However, results also indicated that samples degraded rapidly (to OHCbl) when in the buffered diluent that was used in original HPLC analysis – samples completely degraded to OHCbl after 12 hours in autosampler. And yet, during the original HPLC, four of the samples sat in the autosampler for approx 20 hours before being reanalysed at 9 am the following morning, and those samples showed no sign of degradation during storage (the 2 x outlier dregs were among these four samples). When asked to explain this discrepancy the lab advised that the original autosampler was refrigerated whereas the one used for the time study was not.
The lab now offers to inject a single sample (from the expired vial) using the original analyser and the original operator. This almost meets my request to rerun the analysis under identical conditions, except for the method of injection (autosampler vs manual injection). In reading through many troubleshooting guides available online I get the impression that manual injection (if done well, i.e. completely fill the loop) is more likely to produce reliable result than injection from an autosampler. Also, will temperature of injection vary (i.e. will manual injection be at same temperature as one from refrigerated autosampler)? How important is temperature?
Is it unusual for ghost peaks to produce such orderly results?
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Hi, I also get two peaks for pure methylcobalamin standard every time I run. I am just wondering are those isomers or are those methylcobalamine and hydroxycobalamine. How do I get to know it? Thanks.
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I came across the bi-amperometric technique in analytic chemistry, but I don't understand why the analysis is possible only if the sample contains reversible redox couples. Before of that I'd like to understand when a redox reaction could be defined as reversible and when it cannot.
Thanks in advance.
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Commonly, the irreversible reaction means that the equilibrium is considerably shifted to one side and the reversed reaction is too slow. Thus, truly irreversible reactions do not exist. In electrochemistry, the electron moves between an molecule and electrode, S + e = S- . So, if you change a potential, at certain point the amplitude of current will increase until all S is converted to S- . The current returns to the initial value. If now you scan potential in opposite direction, you will observe S- . If both S and S- are stable, then on reversed potential scan the oxidation of S- results in formation of S. This is one-electron electrochemically reversible process. If S- is unstable and form product P, then on reversed scan you will not see S- . This is the electrochemically irreversible process. If you are able to convert P back to S- and remove one electron from S- , you will have chemically reversible reaction.
Thus, chemically all reactions are reversible in principal. The irreversible reaction means that the reversed reaction is too slow.
In other words, reversibility is the thermodynamic term, but the reaction kinetics may affect the rate of achieving the equilibrium.
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Is there a technological niche in pharmaceutical research that makes NQR or NMR the only measurement methods practically applicable?
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My question is related to a recently completed project: "Integrating Superregenerative Principles in a Compact, Power-Efficient NMR/NQR Spectrometer: A Novel Approach with Pulsed Excitation"
I am looking for an application to commercialize the detector idea, taking advantage of its attributes such as low power consumption and simplicity of design.
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Hello,
I actually have a salt of potassium formate, but the issue is that there are many impurities in the salt. I wanted to know which analytical technique is appropriate to quantify the composition of the salt as well as identify all the impurities present in the salt.
I am thinking of HPLC and GC-MS. Which of these is better and how to go about it? Lastly, are there any better methods than the ones I have listed? There is a lab with most of the equipment, but I just want to make sure I go with the most suitable one.
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Dear Alfred,
Thanks, I will try out different methods surely and update if I get any conclusive results.
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Short Course: Statistics, Calibration Strategies and Data Processing for Analytical Measurements
Pittcon 2024, San Diego, CA, USA (Feb 24-28, 2024)
Time: Saturday, February 24, 2024, 8:30 AM to 5:00 PM (Full day course)
Short Course: SC-2561
Presenter: Dr. Nimal De Silva, Faculty Scientist, Geochemistry Laboratories, University of Ottawa, Ontario, Canada K1N 6N5
Abstract:
Over the past few decades, instrumental analysis has come a long way in terms of sensitivity, efficiency, automation, and the use of sophisticated software for instrument control and data acquisition and processing. However, the full potential of such sophistication can only be realized with the user’s understanding of the fundamentals of method optimization, statistical concepts, calibration strategies and data processing, to tailor them to the specific analytical needs without blindly accepting what the instrument can provide. The objective of this course is to provide the necessary knowledge to strategically exploit the full potential of such capabilities and commonly available spreadsheet software. Topics to be covered include Analytical Statistics, Propagation of Errors, Signal Noise, Uncertainty and Dynamic Range, Linear and Non-linear Calibration, Weighted versus Un-Weighted Regression, Optimum Selection of Calibration Range and Standard Intervals, Gravimetric versus Volumetric Standards and their Preparation, Matrix effects, Signal Drift, Standard Addition, Internal Standards, Drift Correction, Matrix Matching, Selection from multiple responses, Use and Misuse of Dynamic Range, Evaluation and Visualization of Calibrations and Data from Large Data Sets of Multiple Analytes using EXCEL, etc. Although the demonstration data sets will be primarily selected from ICPES/MS and Chromatographic measurements, the concepts discussed will be applicable to any analytical technique, and scientific measurements in general.
Learning Objectives:
After this course, you will be familiar with:
- Statistical concepts, and errors relevant to analytical measurements and calibration.
- Pros and cons of different calibration strategies.
- Optimum selection of calibration type, standards, intervals, and accurate preparation of standards.
- Interferences, and various remedies.
- Efficient use of spreadsheets for post-processing of data, refining, evaluation, and validation.
Access to a personal laptop for the participants during the course would be helpful, although internet access during the course is not necessary. However, some sample- and work-out spreadsheets, and course material need to be distributed (emailed) to the participants day before the course.
Target Audience: Analytical Technicians, Chemists, Scientists, Laboratory Managers, Students
Register for Pittcon: https://pittcon.org/register
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Dear Thiphol:
Many thanks for your interest. Currently, I don't have a recorded video. However, I may offer this course in the future on-line in a webinar format if there is sufficient interest/inquiries.
Thanks again.
Nimal
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Is there a technological niche in pharmaceutical research that makes NQR or NMR the only measurement methods practically applicable?
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Your work is really very interesting and useful .
my sincere congratulations!!
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Analytical Chemistry
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thanks for sharing, but are we now discussing Mössbauer- or Mass-Spectroscopy (or both).
Alfred
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Dear Colleagues!
I am interested in ELSD, an HPLC detector.
Is there anyone who is currently using or has used this detector?
I would appreciate it if you could share information on the problems, concerns, and advantages of using it in real world situations.
It would also be appreciated if you could introduce, for example, review articles explaining the characteristics of quantitative measurements of analogous compounds without their standards.
I would like express my gratitude to everyone in this community.
I appreciate it.
Best regards,
Yasuhiro Nishida
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Dear friend Yasuhiro Nishida
Ah, ELSD, the Evaporative Light Scattering Detector, a gem in the world of HPLC detectors! Now, let me share some insights.
Firstly, ELSD is often a savior when dealing with compounds that lack UV absorption or those that don't have a chromophore. It detects analytes based on their ability to scatter light when eluted from the column. Now, let's delve into the real-world scenarios:
**Advantages:**
1. **Universal Detection:** One of the main advantages is its universality. It can detect virtually any compound regardless of its optical properties, making it a fantastic choice for compounds with no UV absorption.
2. **Quantification of Analogous Compounds:** ELSD is particularly useful when dealing with structurally analogous compounds that might not have distinct standards. This makes it valuable for natural product analysis or in cases where obtaining pure standards is challenging.
3. **Low Detection Limits:** ELSD often provides lower detection limits compared to other detectors, which is beneficial when dealing with trace-level analysis.
**Concerns:**
1. **Baseline Drift:** ELSD is known for baseline drift, which might complicate the quantification of compounds. Strategies like using an internal standard or appropriate calibration techniques are often employed to address this issue.
2. **Sensitivity to Mobile Phase Changes:** Variations in the mobile phase composition can affect the signal intensity. Users need to carefully optimize the mobile phase to get consistent results.
3. **Sample Dependent Sensitivity:** The sensitivity of ELSD can be sample-dependent, and it might require method adjustments for different compound classes.
**Review Articles:**
1. **"Lecoeur, M., Decaudin, B., Guillotin, Y., Sautou, V., Vaccher, C., & ARMED Study Group. (2015). Comparison of high-performance liquid chromatography and supercritical fluid chromatography using evaporative light scattering detection for the determination of plasticizers in medical devices. Journal of Chromatography A, 1417, 104-115. provides a comprehensive overview.
2. **"Megoulas, N. C., & Koupparis, M. A. (2005). Twenty years of evaporative light scattering detection. Critical reviews in analytical chemistry, 35(4), 301-316., is another valuable resource.
Remember, my eager interlocutor Yasuhiro Nishida, ELSD is a versatile tool, but like any technique, it has its nuances. The key is in understanding those nuances and wielding them to your Yasuhiro Nishida advantage in the quest for chromatographic mastery!
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For determination of water contents(moisture) spectrophotometrically.
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To remove moisture from grains, natural drying is definitely not the best method: too long times, risks of product loss and uneven drying make this process almost counterproductive. Much more advantageous is to use grain dryers – mobile or tower – which allow optimal and rapid drying. The investment required for their purchase is recovered in a short time and guarantees numerous benefits, reducing losses and increasing profits.
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Currently working on a USP assay method for HPLC that requires water-saturated butyl chloride as a mobile phase and water-saturated chloroform as a diluent.
What is the whole point of using water-saturated solutions like this?
Would there be alternative ways to substitute these solutions?
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Using water-saturated butyl chloride as a mobile phase and water-saturated chloroform as a diluent in HPLC maybe to enhance sensitivity, aid in phase separation, or reduce ionization. The specific reason for using such aqueous form of solution could differ based the type of assay and the APIs or analyte being analyzed. Alternatives can be considered, but method validation (still dependent on the analyte involved) is essential to ensure the reliability of results.
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In analytical chemistry, a linear model is developed on multiple concentration levels with a goal to predict target analyte concentration in an unknown sample. Will the model prediction favorize a concentration if more calibration samples at that concentration level is used in the model development? I have not found literature article on this topic.
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This is your research question "Will the model prediction favorize a concentration if more calibration samples at that concentration level is used in the model development?" you find the answer by doing several computations
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Is sample cleanup not a part of sample preparation. Are there any examples sample cleanup that are not sample preparation in analytical chemistry?
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I would say that sample preparation is a wider term.
Sometimes you do not have to perform sample cleanup because your sample is pure enough or suitable for the instrumental analysis as it is. However, you still might need some sample preparation in terms of filtering, diluting, homogenizing and so on.
Sample cleanup usually consists of some kind of extraction (either in liquid or on a sorbent), chromatographic cleanup, precipitation or similar technique. There might even be manual mechanical/macroscopic cleanup, depending on what is your sample.
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Hello everybody. Our instrument (i.e., ion chromatography) must stop working for more than 4 months because of some maintenance. My question is, during 4 months or more, does it need anything done for preservation? However, we have already removed the columns and are storing them in the refrigerator.
Thanks a lot
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Hello!
You can read the washing method and the conditions of storage for its manual, which you can download from the homepage of the manufacturer. For columns and suppressors, the conditions vary by type. The column and the suppressor (electrolytically regenerated) must be removed and stored in the specified solvent. If you follow the instructions you should have no problem.
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Couldnt find any for a long time…
I need a scientific gaps for those topic and I am doing it in an analytical chemistry lab
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Flame photometry is a widely used analytical technique for determining the concentration of certain metal ions in a solution based on their characteristic emission spectra when introduced into a flame. Despite its popularity, there are several scientific gaps and challenges associated with flame photometry:
Limited Element Detection: Flame photometry is primarily used for alkali and alkaline earth metal ions. There is a limitation in detecting transition metals and other elements using traditional flame photometry techniques.
Interference Issues: Flame photometry can suffer from interference due to the presence of other elements or compounds in the sample. This can lead to inaccurate results and complicates the analysis, especially when dealing with complex sample matrices.
Sensitivity and Detection Limits: The sensitivity of flame photometry is relatively lower compared to other modern spectroscopic techniques, such as inductively coupled plasma-optical emission spectroscopy (ICP-OES) or inductively coupled plasma-mass spectrometry (ICP-MS). Improving sensitivity and lower detection limits is an ongoing challenge.
Sample Preparation: Sample preparation is crucial in flame photometry, and the techniques used can affect the accuracy and precision of the results. There is a need for standardized sample preparation methods to ensure consistency and reliability across different laboratories and applications.
Quantitative Analysis: Achieving accurate quantitative analysis, especially in complex samples, is challenging. Calibration methods and techniques need continuous refinement to enhance accuracy and reliability in quantitative measurements.
Instrumentation and Miniaturization: There is a need for the development of more compact and portable flame photometers for field applications. Miniaturization of the instrumentation can open up new possibilities for on-site analysis and real-time monitoring in various fields, including environmental monitoring and clinical diagnostics.
Combination with Other Techniques: Integrating flame photometry with other analytical techniques, such as chromatography or mass spectrometry, can provide complementary information about the sample composition. Research into effective combinations and methodologies is essential for comprehensive analysis.
Data Analysis and Automation: With the advancement of technology, there is a need for improved data analysis methods, including automated data processing and interpretation algorithms. Automation can reduce human error and increase the efficiency of the analysis process.
Environmental and Safety Concerns: Research into the environmental impact of flame photometry techniques, including waste disposal and energy consumption, is important. Additionally, ensuring the safety of operators working with flame photometers and associated chemicals is a continuous concern.
Addressing these scientific gaps will contribute to the advancement of flame photometry and enhance its capabilities in various fields of research and industry.
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What is the difference between Principal Component Analysis (PCA) and Partial Least Square (PLS)? In which conditions is it better to use PCA over PLS practically, let's say in environmental chemistry or analytical chemistry? Or, even can we combine both methods? Thanks for your explanations.
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Hi! This is how ChatGPT answered your question:
Principal Component Analysis (PCA) and Partial Least Squares (PLS) are both multivariate data analysis techniques used in chemometrics. While they share some similarities, they are used for different purposes and have different underlying principles.
Principle Component Analysis (PCA):
PCA is primarily used for dimensionality reduction and identifying patterns or relationships in high-dimensional data. It transforms the original variables into a new set of uncorrelated variables called principal components. These components are ordered in terms of the amount of variance they explain. PCA aims to maximize the explained variance with the fewest number of components.
Partial Least Squares (PLS):
PLS, on the other hand, is used for regression and predictive modeling. It finds linear combinations of the original variables (called latent variables) that are strongly related to a response variable. PLS maximizes the covariance between the predictors and the response and extracts components accordingly. It is particularly useful when the number of predictors is large, and collinearity between predictors is present.
In terms of practical use in environmental chemistry or analytical chemistry:
PCA is often employed when the main objective is to reduce the dimensionality of the dataset, explore patterns and relationships between variables, or visualize high-dimensional data. It helps in identifying outliers, clustering observations, and understanding the dominant factors driving the variation in the data.
PLS is useful when there is a need for prediction or modeling, especially when dealing with complex datasets, high collinearity, or multicollinearity. It handles situations where the number of predictors is significantly larger than the number of observations.
Both methods can be combined and utilized together when necessary. For instance, PCA can be used for data preprocessing and visualization, identifying outlier samples, or selecting variables to be used in subsequent PLS modeling. By reducing the dimensionality, PCA can enhance the efficiency of PLS models by reducing noise and overfitting.
In conclusion, the choice between PCA and PLS depends on the specific goals of the analysis. PCA is suitable for dimensionality reduction and exploratory data analysis, while PLS is more appropriate for predictive modeling. Both methods can be combined to leverage the strengths of each when dealing with complex data in environmental or analytical chemistry applications.
If you need more detailed explanations, try asking ChatGPT specific questions. It is best, however, to study problems in a traditional way, i.e. from academic textbooks and specialist studies in specific fields.
ZJ
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How many grams of K2Cr2O7 to dissolve it in 1 liter Distilled water to obtain 50 ppm of Chromium? to become aqueous solution, Is there a specific equation to apply? Thanks
Ali
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Why are so many methods and no answers the same? Other papers also mention the different results. What is actually the correct answer?
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The Laboratory for Analytical Chemistry and Industrial Analysis at the Faculty of Chemistry and Chemical Engineering, University of Maribor, is seeking talented individuals to join our team. With cutting-edge research and state-of-the-art equipment, this is an opportunity to advance your career in a vibrant and innovative environment.
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  • Strong oral and written English communication skills are required.
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  • Bring your expertise in operating ICP-MS to contribute to our research endeavors.
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We are looking forward to work with you and unlock new frontiers in analytical chemistry!
Note: In case you have any further questions or require additional information, please do not hesitate to reach out.
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I'm ready
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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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Hello,
When working with methanol, I noticed that I could never take the exact volume of methanol with micropipette.
Is there any other tool or method that could solve this problem?
Many thanks for your concern,
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  • Michal, I am pleased that the eVOL works so well for you. It is a device I developed with my team at SGE. It is disappointing that it has apparently been discontinued but the same team that developed the eVOL have since developed at ePrep a far more capable automatic syringe which I mentioned above. https://www.digivol.com.au
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application
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Oxidative coupling reactions in analytical chemistry play a significant role in various applications, particularly in the field of spectrophotometry. These reactions involve the coupling of certain chemical species through an oxidative process, resulting in the formation of colored or fluorescent compounds. The composition of colored or fluorescent products can be measured and quantified using spectrophotometric techniques, enabling the determination of specific analytes in a sample.
Here are some specific applications of oxidative coupling reactions in analytical chemistry:
1- Determination of Phenolic Compounds: Oxidative coupling reactions are commonly used to determine phenolic compounds in various samples, such as environmental samples, food, and beverages. These compounds react with specific reagents to produce colored products, and the intensity of the color formed is proportional to the concentration of the phenolic compound present in the sample. This method allows for sensitive and selective analysis of phenolic compounds.
2- Measurement of Aromatic Amines: Aromatic amines can be determined using oxidative coupling reactions with suitable reagents. The resulting colored products can be quantified using spectrophotometric techniques, providing a means for analyzing these compounds in different samples.
3- Analysis of Polyphenols: Polyphenols, which are abundant in various plant-derived products such as fruits, vegetables, and beverages, can be quantified using oxidative coupling reactions. These reactions often involve specific metal catalysts to form colored complexes with the polyphenols, allowing for their sensitive detection and measurement.
4- Detection of Nitrogen Species: Oxidative coupling reactions have been employed for the detection and measurement of nitrogen-containing species, such as nitrites and nitrates. These reactions can lead to the formation of colored products that can be easily detected and quantified.
5- Environmental Monitoring: Oxidative coupling reactions find applications in environmental monitoring to analyze pollutants and contaminants in water and soil samples. By using suitable reagents, certain pollutants can undergo oxidative coupling to produce colored products, facilitating their identification and quantification.
6- Clinical Analysis: In clinical chemistry, oxidative coupling reactions can be used for the determination of specific analytes in biological samples, such as blood and urine. These reactions can offer a sensitive and specific means of measuring certain compounds of interest in various disease diagnoses and monitoring applications.
Overall, oxidative coupling reactions in analytical chemistry provide valuable tools for the selective and sensitive detection and quantification of various compounds of interest, making them essential in many research, environmental, and industrial applications.
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I would like to inquire about whether the method of squeezing seeds by means of a machine to extract its oil is feasible to study in the MTT experiment in tissue culture lab ?
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This is feasible. You will need to define and construct your experimental design first, and the particular seed sample you are interested to work with. A mechanical oil presser machine will do to extract the fixed oil. And then, you will need to determine what kind of cell line you want to test it. Probably you would want to investigate its medicinal property thru MTT assay.
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Many methods call for reconstituting experimental samples in methanol/ water, but diluting the standards with some sort of plasma (typically blank bovine plasma). Why not dilute the standards in methanol/ water to match the experimental samples?
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The choice of diluent for preparing standards and experimental samples in analytical methods can depend on several factors, including the solubility of the analyte, compatibility with the analysis technique, and the desired matrix for calibration.
Here are some reasons why diluting standards with plasma or other biological matrices may be preferred over diluting them with methanol/water to match the experimental samples:
  1. Matrix Effects: Matrix effects refer to the influence of the sample matrix on the analyte's measurement or detection. Biological matrices, such as plasma, contain various endogenous components (proteins, lipids, metabolites) that can interact with the analyte and affect its detection or measurement. By diluting the standards in a similar matrix as the samples (plasma), it helps account for these matrix effects and improves the accuracy and precision of the calibration.
  2. Similarity to Sample Composition: Diluting the standards in a matrix like plasma makes them more representative of the actual samples being analyzed. This can help account for any potential differences in analyte recovery or behavior between the standard solution and the actual sample matrix, leading to more accurate and reliable results.
  3. Mimicking Sample Extraction Procedures: In some cases, the plasma matrix used for dilution may mimic the extraction or sample preparation procedures applied to the experimental samples. By using the same matrix for standards and samples, any extraction or matrix effects introduced during sample preparation can be more accurately accounted for, improving the overall validity of the results.
  4. Method Validation and Comparison: Using plasma as the diluent for standards allows for direct comparison of the calibration curve and sample results. It facilitates method validation by ensuring that the standard curve represents the analyte's behavior in the same matrix as the samples, providing more meaningful and applicable results.
It's important to note that the choice of diluent depends on the specific analytical method, the analyte being measured, and the overall objective of the analysis. Methanol/water dilution may still be appropriate for some cases where the analyte is stable and soluble in that solvent mixture and if matrix effects are not a significant concern.
Ultimately, the decision on the diluent should be made based on method requirements, validation considerations, and the desired accuracy and reliability of the results. It is recommended to consult the specific method or assay protocol, as well as relevant literature or guidelines, for guidance on appropriate dilution procedures for your specific analysis.
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My peptide is Cholecystokinin (CCK8), MW=1142.35 (COOH-D-Y-M-G-W-M-D-F-NH2).
Stock solution in NH4OH 0.05M and working solution in acetonitrile.
I do MS infusion at conc. 500 ng/ml in acetonitrile.
I use two LC/MS machines: Micromass - Quattro Premier XE of Waters (Tamdem Quadrupole) and Applied Biosystems - API 3200 LC/MS/MS (triple quadrupole)
I run ES + but I can not see the peak at 1+, 2+, 3+,4+,...for [M+H], [M+Na], [M+K]
I wonder whether I have missed some other adduct ions that could be created during the ionization?
Or maybe my peptide is being degraded during preparing the sample?
Please give me some advice! Thank you!
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Here are the other points, you may lean on;
If the purpose is quantification or purity check, LC-UV would be nice to use since the octapeptide you have several aromatic rings and would be highly responsive,
secondly, 500 ppb may be a low conc. to conduct a full scan..especially when the ionization efficiency is low.
Third, I would prefer combined flow scanning in place of infusion...In this mode, you are not taking benefits of the mobile phases which present donors to improve ionization...You should combine the lc flow and infusion (acid and/or DMSO additives in phases for pos ESI in this case) and retest the response...
By solving the peptide in an alkaline condition you are directing the peptide to deprotonation and this makes the peptide more amenable to neg ESI...If it is soluble in ACN directly..prepare your stock in ACN and dilute it with the same solvent, I prefer not to use aggressive pH which is not convenient for most of the peptides to the unintended H exchanges...
Last but not least, If the peptide is hydrophobic and dissolves only in organic solvents this is susceptible to be efficiently ionized in APCI, APPI rather than ESI...You may look for these alternative ionization techniques if MS analysis is the bottleneck and the abovementioned suggestions are useless...
Good Luck...
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Does someone have any practical experience with those columns?
The producer suggest ODS-B are more suitable for hydrophilic analytes, but without any concrete information.
Can they be used interchangeably with ODS-A columns? Are there expected changes in retention times of non-polar analytes? Are there differences in their pH tolerance?
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Sir,
How can we remove blockage of Waters Spherisorb ODS2 column? Any solution you have?
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Green analytical procedure index (GAPI) and National environmental methods index (NEMI) are assessment tools used for evaluating the greenness of an analytical method. Is there is any software through which GAPI and NEMI pictograms are constructed?
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I am working on a project that requires the measurement of neuromelanin purity, and I have found papers that say that they have measured the purity, but they do not say how ( ).
Neuromelanin does not have a commercially available 100% standard, so I cannot do typical comparisons. Does anyone know where to begin or how to do the purity measurements?
Any help would be appreciated.
Thank you!
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There are several methods for measuring the purity of neuromelanin, including:
Spectrophotometry: This technique can be used to measure the light absorption of neuromelanin at different wavelengths. The purity of neuromelanin can be determined by comparing the resulting spectra with reference spectra.
Chromatography: This technique allows the separation of different components of a brain tissue sample using appropriate solvents. The purity of neuromelanin can be determined by analyzing the chromatographic peaks corresponding to neuromelanin and comparing their intensity with other components.
Electron microscopy: With this technique it is possible to observe the structure of neuromelanin at a microscopic level. The purity of neuromelanin can be determined by analyzing the morphology and size of neuromelanin granules.
It should be noted that measuring the purity of neuromelanin can be difficult because there are other similar pigments in the brain, such as melanin and lipofuscin. Therefore, it is important to validate the obtained results using different methods and compare the results with known reference samples.
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I'm a Chemistry student currently working on a thesis that involves phytoremediation of Lead in aqueous solution using a specific plant.
The FTIR results for both the stems and leaves of the plant after phytoremediation are almost identical, having the presence of O-H stretch and C-H stretch on both IR spectrum.
The FTIR result for the roots after phytoremediation, however, showed a possible trace amount of H2O at 3457.1 cm-1 (it was a tiny peak, therefore it cannot be called an O-H stretch), along with the presence of a C-H stretch and C=O stretch.
I need help in understanding what caused this deviation from the two other samples (stems and leaves). Could it be the presence of the metal in the root sample or are there any factors that I need to consider?
Thank you to anyone who'd be willing to give their insight/s on this, it would really help me a lot.
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Princess Olivar Tuquero , as you noted previous researchers identified the IF band shift when affected by metals. Assuming that is correct, then the only thing necessary to correlate your FTIR results with the metal content is a graph of the amount of observed band shift to the amount of lead found.
Secondary correlations are not generally preferred analytically, but are sometimes necessary. If you are trying to identify the particular chemical/structure actually doing the adsorption of the lead I can see how combining both might seem simpler. However, as long as you have an AAS it would be better to use it for the metal analysis instead of trying to infer it from the IR. If that is just to explain why your IR peaks are shifted a bit, the metal content would explain that via reference to the paper you mentioned.
As normal growth in plants transports nutrients from the roots ultimately to the leaves it is not surprising to find the highest concentrations of any other compound taken up there as well. I would not expect to find them in the same concentrations evenly throughout the plant structure.
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Hello
Laboratory techniques of biological and analytical chemistry to investigate the anticancer properties of plant samples.
thanks
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Olá, ensaios com culturas celulares.
Antes de testar em células, sugiro fazer uma ampla caracterização de sua amostra (planta), tanto com HPLC, como testes básicos de atividade antioxidante (colorimétrico) entre outros. De acordo com a caracterização você consegue direcionar para algumas linhagens celulares.
Dependendo da estrutura da sua Universidade e verba você consegue fazer muitos testes.
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Dear to whom it may concern,
I would like to kindly ask you about the ionization of acidic and salty forms of a given compound in electrospray ionization.
To be more specific, when I successively infused the reference standard solutions of atorvastatin in both its acidic (atorvastatin with an exact mass of 558.25) and salty (atorvastatin calcium with an exact mass of 1154.45) forms into the ionization source (electrospray ionization known as ESI) of the mass spectrometer, I always obtained the same precursor ion (m/z 559.5 in positive mode) of its forms.
I do not understand the reason why the atorvastatin calcium could show the same precursor ion as that of the acidic form of atorvastatin.
May you please give me an explanation of how the salty form of atorvastatin is ionized in ESI, resulting in the same precursor ion as that of the acidic form of atorvastatin?
Thank you so much.
Best regards,
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To my understanding, acetonitrile, methanol, isopropoanol etc. act as electron donors in ESI conditions, enhancing ionization in ESI+. This is one of the reason why ionization in ESI+ is enhanced by solvents (the other is their faster vaporization than water in ESI conditions).
some solvents are better electron donors than others, and you may notice signal enhancement switching from one to another...
hope this helps...
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I want to quantify the chromium in solution. I want to know whether atomic adsorption spectroscopy is better or UV vis spectrophotometer.
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Noor Ul Ain , Generally atomic adsorption spectroscopy will be better. You have better selectivity and lower quantification limit.
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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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I am looking for a method to completely remove proteins from plasma without using heat or adding salt ions. I have considered using activated carbon, but I am unsure if this is feasible. Are there any other effective methods for achieving this goal?
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Dear Sir you may try the protein separation with foam fractionation coloumn. it would suppose to help you
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Chemical Informations
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Greetings Ali Safaa
To solve for molarity (M) in the equation:
ppm = M x m.wt x 1000
We can rearrange the equation as follows:
M = ppm / (m.wt x 1000)
So if you have a solution with a concentration of 50 ug/ml and you want to know the molarity, you would first need to know the molecular weight of the solute. Let's say the molecular weight is 100 g/mol.
  1. Convert ug/ml to ppm by multiplying by 1000:
50 ug/ml x 1000 = 50,000 ppm
  1. Plug in the values into the equation:
M = 50,000 ppm / (100 g/mol x 1000)
M = 0.5 M
Therefore, the molarity of the solution is 0.5 M.
It is important to note that ug/ml and ppm are not equivalent units of measurement. Ug/ml is a unit of concentration based on mass per volume, while ppm is a unit of concentration based on the number of parts per million. To convert from ug/ml to ppm, you would need to know the density of the solution and the molecular weight of the solute.
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In the Column treatment of aqueous solution of Chromium Removal by Adsorption
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Treating bark with acid (HCl) first and then with base (NaOH) second is a common method for isolating plant compounds for analysis or extraction, such as tannins, lignin, and cellulose. This method is known as acid-base treatment or A/B extraction.
The reason for this order of treatment is that acid treatment hydrolyzes and breaks down the plant cell walls, making the cell contents more accessible for extraction. Acid treatment can also help to remove impurities, such as pigments and waxes, from the sample.
After acid treatment, the sample is then neutralized with a base, typically sodium hydroxide (NaOH), to restore the pH to a neutral or slightly alkaline state. The neutralization step is important to prevent the acid from interfering with subsequent analytical techniques or reactions.
The use of acid and base treatments in this order allows for selective extraction of different plant compounds based on their solubility and chemical properties. For example, tannins are more soluble in acidic solutions, while lignin and cellulose are more soluble in basic solutions.
Treating the bark with base first would result in a saponification reaction, where the ester linkages in the plant compounds would be hydrolyzed by the base, resulting in a loss of their original structure and properties. Therefore, treating the bark with acid first and then with base is the preferred order for A/B extraction of plant compounds from bark.
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Hello, I am a student in analytical chemistry, I am supposed to prepare samples, quality control, and calibration serial dilution for a forensic project which is working on larvae and flies (for quantification of benzodiazpines).
would you please correct what I wrote here even in terms of the specific volume and concentration?
Sample prep:
Collected sample with matrix is spiked with target analytes and RS (recovery standard)
Sample is extracted (prepared for analysis)
IS (internal standard is spiked before the analysis
Cal prep:
Calibration standards (mixture of target analytes and RS) are prepared with serial dilution
IS is added before the analysis
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I appreciate your response,
you wrote " Prepare a series of quality control samples by spiking known amounts of the target analytes and RS into a matrix. Extract the QC samples to prepare them for analysis"
I have some questions:
1) It seems the QC sample preparation is the same with the sample preparation, what is the difference exactly?
2) what do you mean by "series of QC samples" ?
my advisor told me the feature of QC samples is the fact that we can consider their recovery as 100%,, I thought it means we have to do the same process like the sample preparation BUT add the RS after the extraction process (because in this way we know that the QC recovery is 100%)
I dont know, maybe I am wrong. I am working with HPLC-ESI-mass
another question, you wrote I need to spike the RS into the calibration serial dilution too, is there any extraction process for calibration serial dilution?
waiting for your response, Zeinab.
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I have powdered diphenylcarbazide and I want to make 0.5% w/v solution of diphenyl carbazide. Since it is dissolved in acetone.
Does it mean 0.5 g in 100 mL acetone? Is there any need to add distilled water?
In literature it is prepared by dissolving in acetone and then 200 mL distilled water was added.
Thanks for your guidance
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It is likely the presence of water will help to stabilise the metal ions. In the presence of pure acetone the inorganic metal may be insoluble and unavailable to react?
As per above, taking the 0,5 gram and dissolving in pure acetone, then making this up to 100ml, maybe using 50mL acetone, and then using distilled water to complete the volume requirement?
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I want to deacetylate the chitosan in sodium hydroxide (50 % w/w) solution. Does that mean 50 g NaOH in 50 mL of distilled water? What should be the appropriate time and temperature for the complete process? There are different temperatures and times are reported in literature.
Thank you for your help!
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The reaction time and the temprature depends on the level of deacetylation that you would like to achieve. If you let your mixture react longer then the level of deacetylation will be higher.
You might need to experiment a bit till you get a product that has the desired characteristics. Or if you have a procedure for a product with the desired characteristics in the literature then you can simply follow that and get some good results.
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I made several reactions with 3,5-Dinitrobenzoyl chloride. When I looked at similar reactions for this substance, no heat was ever given in the reaction (even though heat increases the yield).
The interesting thing is that this substance turns black as soon as the heat is given to the reaction environment. Due to the fact that, theoretically, the polymerization of this material is impossible. Do you know the reason why they do not give heat to this material?
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Hello everyone,
I want to calculate a ratio, but for some measurements, I have <LOD in the denominator
There is actually a range of possible numbers <LOD
One solution could be to consider: =LOD, or LOD/2, etc. ?
Are there methodological references which I can confront?
Thank you in advance
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There are some good recommendations here. However, my caveat is that it exemplifies the danger of trusting (or using) statistics as a substitute for valid science. If you can't OBSERVE it in some way (<LOD) you really cannot make valid assumptions or conclusions about it. Wether you need more accurate assay methods or more experiments for more data, you really cannot legitimately just ignore that weakness and obscure it with mathematical manipulations of other data.
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Hello everyone,
I want to calculate a ratio, but for some measurements, I have <LOD in the denominator
There is actually a range of possible numbers <LOD
One solution could be to consider: =LOD, or LOD/2, etc. ?
Are there methodological references which I can confront?
Thank you in advance
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When calculating ratios with a Limit of Detection (LOD) in the denominator, there are a few different approaches that can be used, depending on the specific context and the desired level of accuracy. Here are a few examples:
  1. Substitute a value below the LOD: One option is to substitute a value below the LOD, such as half the LOD, in the denominator. This will give a conservative estimate of the ratio, but it may not be very accurate.
  2. Substitute a value above the LOD: Another option is to substitute a value above the LOD, such as the LOD +1, in the denominator. This will give a less conservative estimate of the ratio, but it may not be very accurate.
  3. Use a statistical method: A more accurate approach is to use a statistical method to estimate the true value of the ratio. For example, the method of imputed ratios or the method of adjusted ratios can be used.
  4. Report the ratio as <LOD: Another option is to report the ratio as <LOD, this means that the value is less than the limit of detection.
It is important to note that the best approach will depend on the specific context of the measurement, the desired level of accuracy, and the intended use of the ratio. It's always advisable to consult with an expert or statistician to determine the most appropriate approach.
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Hello
I have received the FTIR graph after the analysis of the sample but the graph isn't aligned to the baseline. I am attaching the file. Kindly guide me is it the sample or machine error?
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  • Run a standard material
  • Contact the manufacturer or distributor/agent with the above
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We are looking for a way to identify the composition of a polymer blend that we do not know the composition. The composition is based on a polyurethan polymer, silicone elastomer, polyester-based polymer, and enzyme (that we know).
We have done some research and it seems that FTIR combined with TGA (Thermogravimetric analysis) can possibly be helpful for polymer blend identification.
We hope that our colleagues can share their point of views on how to approach the situation and suggest any helpful tools that can help us.
Thank you in advance.
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That is depends upon the which based polyurethan water based or solvent based , chromatography technique also useful
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Is it necessary to carry out validation tests on model mixtures prepared using both substances, or is it enough to use one substance for testing?
What validation tests should be carried out for an "alternative" substance only? If there is a quantitative method: what validation tests should be checked, for example?
Is it necessary to use a risk-based approach to determine validation tests when registering a new alternative substance during revalidation?
I'm really looking forward to your response, thank You for your attention!
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Of course you will have to perform a QA audit of the new manufacturer's facility, but you could have a limited method validation (which should include specificity, linearity (which you could derive the LOD and LOQ), repeatability... Don't be surprised if the impurity profile is different since it is dependent on the manufacturing process. You should also put the finished drug product that is using the new manufacturer's API, on stability.
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Hi All,
We are trying to add Magnesium & Strontium dopants to our Beta Tricalcium Phosphate (b-TCP) powder. Recently, we obtained EDS data on the undoped b-TCP and doped b-TCP to see if the investigate if the doping was successful. However, we are observing higher weight percentages of the Magnesium dopant in the undoped b-TCP and we can't figure out why we are observing this trend. After we first observed this, we have used EDS to look at multiple different samples but they are all showing similar results. We have contacted the manufacturer of the pure, undoped, b-TCP powder and they agree that we should not be seeing this. We are pretty confident that we don't have contaminated, undoped, pure b-TCP powder. But we still aren't sure what might be causing these results. The attached Mg Map Data is from the undoped b-TCP only but the spreadsheet shows some examples of the weight% values we are observing.
Does anyone have any ideas that might explain the results? Are there any recommendations for how we can discriminate between potentially overlapping signals that might be giving false Mg signals?
Thanks!
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please forget about those ugly very low numbers of % and even the variation of these numbers in your maps.
To my opinion you only 'see' the noise in the background of your EDS spectra around the energy position the Mg K-alphas ( ~1,25keV) and the Sr L-alphas (~1,8keV).
You may share some typical measured spectra; so we will have an impression on the quality of the statistical noise or even of peak overlapings in these regions.
Many thanks in advance
and best regards
G.M.
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LOD and LOC can be calculated from the calibration plot. One of the ways to do it is:
LOD = 3 SD(intercept)/S
LOC = 10 SD(intercept)/S
Where SD is the standard deviation of the intercept and S is the slope.
However, I have seen that standard error (SE) is often used instead of SD. But, SE is not the same that SD:
SD = SE*(N)^1/2
Thus, LOD and LOC from SE should be less than LOD and LOC from SD. However, I used SE for my work because I noticed that when I used SD, LOD and LOC were very high.
What do you think about using SE and SD for LOD and LOC estimation?
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SD estimates the variability of the measurement (mean) for a single sample/population.
SE estimates the variability of the measurement (mean) when repeating different samples within the same total population.
As such, and I'm using the exact same LOD/LOQ methodology as you are, my philosophy so far is to use :
  • SD when I have run only one "sample" (min five calibration curves, generally) when developing the analytical method : I do my calibrations only when developing.
  • SE when I have developed the method and used it for some time : compute SDs for all cumulated calibration intercepts up to now and divide by fixed N (number of accumulated calibrations you chose when developing, e.g. 5 or 10).
Thus, SD provides a very conservative estimation for LOD/LOQ at the start of the project and SE will provide a better estimation when the method has become routiine.
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Hello, I am a student investigating acetate ions in wood.
My current mobile phase is 1000:0.5 (H2O;H2SO4) and I do not have the most resolute peak for acetate. The column is a H+ Column packed with sulfonated styrene /divinylbenzene copolymer backbone. What is a mobile phase worth trying?
pH mobile phase currently is ~2.0
pKA acetic acid is 4.76.
Analyt is acetate in NaOH with a basic pH.
Also is a buffer useful, if so which buffer is needed for acetate ions?
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I trying to analyze EPDM using pyrolysis gcms.
Does anyone know where I can get the standard reference materials?
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EPDM can be found in parts such as water system O-rings, hoses, and gaskets, as well as in electrical insulators and connectors for wires and cables. It is also used in accumulator bladders, diaphragms, grommets, and belts.
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#Analytical Chemistry #Veterinary Drugs #Residue Analysis of Pesticides #LCMSMS
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I completely agree with Mr. Drazen C. Nicely explained.
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Hello,
In the chromatogram you can see that the second peak (retention at 4 min), which is an acetate peak, has huge tailing which is known for the sample that is measured but I need to know how I can separate the component that causes the tailing.
My mobile phase is MilliQ/H2SO4 (1000;0.5) using an H+ Ion exchange column with UV detection. Method uses a flow rate of 0.8 ml/min with a column temperature of 40 degrees for the first 8 minutes.
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Typically, tailing is an indication that the API is not 'happy' with the mobile phase system and the retention (separation) it provides. It can be resolved by using a stronger solvent (IPA instead of Methanol) or a higher percentage of organic (60% instead of 50% Methanol) in order to 'boot' the molecule off the column. This will lower you retention time and sharpen the peak.
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thanks in advance on sharing the method
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Please find the attached article - Determination of Chloride Content in Cementitious Materials. (It may be helpful)
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We are trying to determine the UV-visible spectrum for some hydroethanolic herbal extracts but we keep getting negative reading, we tried dissolving the samples in different solvents, distilled water, 5% propylene glycol and 10% propylene glycol, but the results are always negative, what could be the reason? and is there a solution for this problem?
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Hope u have this at back of ur mind: "Chromophore"
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Tannic Acid Modification.
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Dear Harsh,
Maybe i will not properly answer your question, but in my understanding tannic acid has a lot phenolic groups which are already very reactive to hydroxyl radical.
Have you ever tried to performe irradiation of tannic acid aqueous solution with ionizing radiations (i.e. electorn beam or gamma-rays ?). You will produced a lot of hydroxyl radical throught water radiolysis which should react with tannic acid.
All the best,
Nicolas
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I am searching for journals that publish reviews of books on spectroscopy, including analytical chemistry, computers in spectroscopy, and signal processing in spectroscopy.
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Though it may be a bit outdated it is one of the rare publications that studied exactly what you are looking for: Hubbard, D.E. (2011), "Chemistry book reviews: their value, sources, and number", Collection Building, Vol. 30 No. 4, pp. 172-178. https://doi.org/10.1108/01604951111181146 In Table II (see enclosed file) you see excellent titles like Journal of the American Chemical Society and Angewandte Chemie International Edition. Obviously not sure how, more than 10 years later, the ‘landscape’ of journals is, but I found a nice example in Frontiers of Chemistry (https://www.frontiersin.org/articles/10.3389/fchem.2017.00065/full ). See for more info regarding book reviews (and especially the reply by Wolfgang R. Dick ) the following question here on RG https://www.researchgate.net/post/Is_a_book_review_considered_a_publication
Best regards.
PS. Be careful with the suggestions like JETIR and IOSR. There are predatory journals out there nowadays. See for example:
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I want to estimate freezing point of a mixture made from Ehhanol (H₃CCH₂OH, MW: 46.07 g/mol) , mono propylene glycol (CH₃CH(OH)CH₂OH, MW: 76.1 g/mol) and water. And the ratio of the mixure will vary for example I can start with 1:1:1 and so on. I spent couple of week to google it but not able to figure out how to do that. If someone here have some experience with it or have some suggestion / literature then please help to solve for this problem.
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Dear Dol Lamsal,
The best and simplest choice for the phase-equilibrium calculations and studying such systems (Including Water+Alcohols+Hydrocarbons) is the CPA (Cubic Plus Association) equation of state. I suggest you verify the following references:
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I have prepared quaternized PVA. I want to measure the degree of substitution of quaternized polymer by titration. In literature, potassium chromate is mentioned as an indicator but I have potassium dichromate in my lab. Can I use this salt instead potassium chromate? AgNO3 solution is used for the titration.
Thanks for your help.
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Yes but also FTIR (point 2.4), elemental analysis via chemical or spectroscopic techniques is another way. If you are close to a biology institute, you may find Kjeldahl analyzer. My Regards
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Let's start a discussion: What do you consider are the key factors or conditions to develop voltammetric and amperometric sensors with a good analytical performance.
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For Developing the good Electrochemical sensor choosing the suitable nanomaterials related to the your project like Carbon nanotubes (CNTs) and gold nanoparticles (AuNPs) is the first condition.
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Dear All,
I'm looking for a suitable and a simple software of Chemometrics technical,
as effective tools for application in exploring chemical data in analytical chemistry, what do you recommend for beginners?
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I suggest that the easiest and the cheapest way is using web-version of MetaboAnalyst (https://www.metaboanalyst.ca/MetaboAnalyst/ModuleView.xhtml).
Best regards,
Ivan
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Dear Researchers :
I have this question and I have an hypothesis:
Why Natural HDPE, when extruded at temperatures about 100 °C (around) it has a white (but pale white), and then when the polymer cools down it color turns between white an yellow.
I understand that this phenomenon it is a general case of all LLDPE, LDPE and HDPE , and in all fabrication processes : Extrusion, injection, molding, pressing, etc.
So this is fundamentally, a chemical characteristic of the material ...
It has to do with a change in the Oxygen concentration in the material ?
Thank you all in advance,
Best Regards !
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Dear Franklin Uriel Parás Hernández, both degradation and crystallization are behind the change in color aspect. My Regards
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For chemical characterisation of my biochar samples & in order to understand it’s chemical composition better I need pyrolytic-GC/MS data of my samples, from which institute i can get this facility also i would appreciate it if anyone can share me the link.
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Hii Dr. Harsh
You may visit NIPER ,MOHALI, PUNJAB for the same.
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After ultrasonic extraction of non-freeze dried sediment samples with n-hexane, can it be directly purified by c18 solid-phase extraction? Why?
Can it be purified directly with a silica gel column? why?
Any known about these two question
Analytical Chemistry
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Thank you sir
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I need to prepare SRM from the benzoate solution to be used for calibration.
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Sodium benzoate is a salt derived from a weak acid and a strong base, so its aqueous solution is alkaline. Therefore, solutions containing sodium benzoate are assayed using a standard N/2 hydrochloric acid solution in an acid- base titration.
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I need to know the best type of bi-potentiostat instrument?
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A potentiostat is the electronic hardware required to control a three electrode cell and run most electroanalytical experiments. A Bipotentiostat and polypotentiostat are potentiostats capable of controlling two working electrodes and more than two working electrodes, respectively. In order to measure the I-V of the electrode one drives a constant current in it till the required potential between the electrode and the reference electrode is reached this is accomplished by the potentiostat. Since the reference electrode does no conduct any current and its function is to sense the potential of the electrolyte only, the current in the working electrode must continue flowing in the counter electrode.
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Do you think it is appropriate to use a photoelectrocatalytic amperometric sensor also as a voltammetric sensor?
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Photoelectrocatalysis takes advantage of the heterogeneous photocatalytic process by applying a biased potential on a photoelectrode in which the catalyst is supported. This configuration allows more effectiveness of the separation of photogenerated charges due to light irradiation with energy being higher compared to that of the band gap energy of the semiconductor, which thereby leads to an increase in the lifetime of the electron-hole pairs. Due to their unique properties, TiO2NTs have been used in many applications such as in photo(electro)catalysis , sensors , biosensors, dye-sensitized solar cells , hydrogen generation by water photoelectrolysis , photocatalytic reduction of CO2 , and biomedical-related applications .
You are right, but slightly difference, In voltammetric sensors, the current response is measured as a function of applied potential. The potential is varied either step by step or continuously in order to determine the current as a function of the cells potential. A voltammetric sensor is usually composed of three electrodes, that is, working, auxiliary, and reference.
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Hi everyone, I have a question regarding the determination of dissolved aluminium by colorimetric method using pyrocatechol violet according to ISO 10566:1994. In the preparation of 'mixed reagent', we have to add 5 mL of the aluminum standard solution (10 mg/L) into 100 mL of this mixed reagent (total volume).
My question is:
- What is the role and function of the addition of standard solution for this method? In this standard it only says "accurate addition of the aluminum standard solution is essential in order to allow a linear calibration at low concentrations".
Note: if we calculate the concentration of this aluminium standard solution in the sample is about 15 µg/L.
Thank you for your answers.
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This is a typical calibration procedure. You will need multiple concentrations to develop a quantitative response relation that you will use to estimate concentrations in your samples
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The fate of nanodrugs / nanoparticles in vivo draws a lot of attention, and many studies label fluorescent of nanodrugs / nanoparticles in order to disclose their distribution in vivo.
- What are its advantages and disadvantages ?
- Is it a reliable tool ?
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The study of the interaction of nanoparticles (NPs) with proteins is of great importance due to its relevance in several fields including nano-biosafety, nano-bioscience, nano-biomedicine, and nano-biotechnology. an introduction and a discussion of merits of fluorescent NPs compared to molecular fluorophores, labels and probes, the article assesses the kinds and specific features of nanomaterials often used in bioimaging. These include fluorescently doped silicas and sol–gels, hydrophilic polymers (hydrogels), hydrophobic organic polymers, semiconducting polymer dots, quantum dots, carbon dots, other carbonaceous nanomaterials, upconversion NPs, noble metal NPs (mainly gold and silver), various other nanomaterials, and dendrimers. Another section covers coatings and methods for surface modification of NPs..
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I find there are various kinds of diffusion coefficient equations, and there always exists the deviation, so can anyone introduce me some good methods for calculating the diffusion coeffients for gasphase species  with higher precision. Thanks again.
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Hi Zhepeng Tang , Did you compare the molecular diffusivity values obtained from the Fuller-Giddings and Chapman-Enskog methods? What I meant that is the Fueller-Giddings correlation is accurate too, as most of the literature suggests Chapman-Enskog method?
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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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I'd like to prepare a stable, cheap solution of bromine for small-scale qualitative detection of alkenes in biological samples. Bromine water is commonly used, but for my purposes it'd be better to have bromine in some organic solvent. However, bromine will react with many common organic solvents, like ethanol or acetone.
Please, could anyone suggest organic alternatives to bromine water for alkene detection?
Thanks in advance.
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In the good(?) old days the answer would have been obvious: carbon tetrachloride. Since this solvent has been practically eliminated from modern labs for health reasons, your most straightforward options are:
1. cyclohexane
2. glacial acetic acid (Thermo Fisher sells a 1M solution of bromine in acetic acid).
Store such solutions in glass containers in a cool dark place, like under a well-ventilated hood.
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We know, that we can use only validated methods for comparative studies. In our lab we have performed the validation of the dissolution method for the specific medicine. In the comparative study we used several different media, these media did not participate in our validation, exept the one for quality control. Does it mean that we have to perform full validation procedures in each media additionally?
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Interesting question. I agree with Andrei Blasko and Saeed Ayaz Khan . However, you did not mean a regular analytical method validation. You are dealing with dissolution kinetics. The dissolution itself will depend on the physicochemical parameters you used, so the kinetics.
You find in the literature different behavior of the same AFI, for instance losartan, in several mediums, pH, ionic strength, and solvation conditions. Therefore several other surface and chemical interactions may influence the kinetics, not the determination method itself.
For your safety, check the validation with the already used media. The kinetics of significant different media will change. Therefore, the dissolution kinetics may have different parameters that may affect or not the determination method.
Best regards,
WNM
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In biodiesel production through transesterification, various of heterogeneous catalysts could be utilized. However, each heterogeneous catalysts are showed different yield. My question is What are the factors of heterogeneous catalyst that affect their activation during transesterification?
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Hello Viraj,
thank you for posting this very interesting technical question on RG. We work in the field of synthetic inorganic chemistry, so that I would not call myself a proven expert in the field of heterogeneous catalysis and transesterification. However, I can suggest to you two very instructive review articles which will certainly help you in your analysis. Thus please have a look at the following references:
Heterogeneous catalysis for sustainable biodiesel production via esterification and transesterification
Fortunately this paper has been posted by the authors as public full text on RG, so that you can freely download it as pdf file.
The other paper can also be accessed as public full text as it has been published Open Access:
Application of Heterogeneous Catalysts for Biodiesel Production from Microalgal Oil—A Review
(Please see the attached pdf file)
I hope this helps. Good luck with your work!
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I have carried out quaternization of PVA for antimicrobial activity of the polymer. The sequence of reaction is PVA preparation followed by addition of KOH and then quaternary ammonium salt. Washed with anhydrous ethanol. First time at 0.1 g PVA the precipitates were formed. But at 1 g PVA, after 3 hrs of adding quaternary ammonium salt the curds were formed before the addition of ethanol. Molar ratio of PVA to QAS is 1:2.
Is it due to self-condensation?
Thanks for your response.
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Dear Noor Ul Ain, please have a look at the following recent review document and the references therein. My Regards
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There are certain drugs exist in liquid form available in the Sigma-Aldrich website, where they have mentioned the concentration of those drugs in "ml" rather than "mg" or "g". How one will find the concentration of such drugs?
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Actually, reading the question with very strict meanings, he might be looking for a conversion to grams. If the density is known, multiply the volume by the density to get the weight. The concentration of a pure liquid compound is 100%.
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I have purified crude glycerol which is come from as a byproduct of transesterification. I need to know, the purity of the sample after purification. What methods can I apply to get the glycerol purity?
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The following useful RG link is also very useful:
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I usually face a problem regarding the specification limits for impurities in new drug products. It is difficult to use the calculations mentioned in ICH-Q3B(R2) guidelines. The reason is that our products (Ophthalmic preparations) contain very low concentrations of active pharmaceutical ingredient and accordingly the total daily intake (TDI) of these materials may not exceed 1 mg. Using ICH-Q3B(R2) guidelines gives very low specification limits that might become below detection limit or are somehow not practical.
I need your advice regarding specification limit determination for impurities in new drug products. We need a method for specification determination and justification because this is continuously requested by several regulatory authorities, within and outside my country.
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How the calculate optamic products as per ICH guideline because of optamic products dose is very low and impurity calculate as per ICH is very high
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Dear researchers, Can tell me about modern, rapid and reliable technique for isolating macromolecules from plant sample ?
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I am trying to remove phosphate from wastewater sample and also recover them. Is there any material that only absorb phosphate from water? Therefore, which natural material should be appropriate to use as absorbent?
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Tamjid Us Sakib depends on the type of technology selection and project
microlage is preferred in case of biological and if you have space and time with low cost investment however if you go via chemical route there are many like activated carbon, haaluminum sulphate or few other sales can also be used
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In the structure of many drugs, there is a carboxylic group
What is the significance of this group? Why should it exist in the structure of a drug?
Do you know any article or book or reference about this subject?
Thanks a lot
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Nalidixic acid - A NSAID grs of drugs or pain killer .REF : en.wikipedia.org ( Image Source ) .
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Greetings
It is very difficult for me to choose between these two majors for the master's degree
Although I think this is a question for many other students as well
Regardless of interest, which of these two disciplines do you think has a better future? Which has more job markets, in the US and Europe? Which one is more suitable for studying abroad? And which one has more income? Are jobs related to organic chemistry less than analytical chemistry?
Please share with me if you have information about these two fields and their job market.
Thanks
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The subject of specialisations does not depend on the feature income rather your subject if interest . Organic chemistry has too much scopes as a synthetic( R&D) chemist in multinational pharmaceutical houses like Chem biotech , Pfizer , DRL labs etc etc. Even in post doc level abroad from India very high scope in organic nano synthesis like CNT . So scope of income is naturally very high in organic chemistry indeed . But in analytical chemistry the scope is narrow compared to organic chemistry . Since analytical and quality control laboratories are also guided by organic chemists / phyto chemists / petrochemicals for mainly UV-Visible spectrophotometric analysis / Chromatography like GC , HPLC , HPTLC , GC-Mass spectrophotometer and fluroscence spectroscopy .Yes analyical chemists are useful in effluent treatment / waste water analysis as well as drinking water analysis of trace heavy metals like Cu , Cd, As , Pb , Hg ( II , I ) by AAS ( Atomic abs Spectrophotometry ) AES ( Atomic emission spectrophotometry. In drinking / waste water lab there are so many important analytical parameters like B.O.D , C.O.D , D.O , pH , TDS , TSS and limit tests for heavy metals in trace metals .
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Dear Researchers :
Can someone teach me how to go from a Concentration given in wt.% to a concentration given in phr ?
Or the two are numerically equivalent ?
I'll appreciate it !
Regards !:)
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Dear Franklin,
I have attached one file which I have made an example for transforming %w to phr. I hope it would be useful.
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To estimate the concentration of PFOS, we use mass-labelled PFOS (MPFOS). We generally spike the standards and samples with unknown concentrations with MPFOS. To estimate PFOS, we first make a standard curve by plotting peak height or peak area ratio vs concentration ratio of PFOS and MPFOS. Now, my question is, how do we differentiate the peaks of the mass fragments with the same m/z (say 99) generated from PFOS and MPFOS from the LC-MS/MS MRM chromatogram? Do they have the same retention time?
Thank you in advance for your praiseworthy answers.
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Hello Arpan,
the MRM allows you to distinguish between PFOS and MPFOS by the recording of different mass transitions: usually the mass transition 499 -> 80 and 499 -> 99 are used for PFOS, while (in our case) for MPFOS (13C4 labelled) it is 503 -> 80 (and 503 -> 99). Usually there should be no interference in these mass transitions, meaning that MPFOS does not produce peaks for PFOS and vice versa due to the specifity of these transitions. And of course they should have the same retention time, but please note that technical PFOS has several branched isomers that elute in front of the linear PFOS (and linear MPFOS).
Hope this helps and good luck for the analysis!
Thomas
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P.S: I wash the column with water and methanol when I open and close the HPLC system.
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I am developing a gradient method for the estimation of 3 drugs, two are water-soluble and one is hydrophobic. I am using Dionex HPLC system equipped with P680 HPLC pump, ASI-100 automated sample injector, UVD340U detector. The mobile phase is composed of 10mM KH2PO4 buffer pH 6.8 and ACN. A gradient is applied from 97:3 (or 90:10, depending upon the column used) Buffer: ACN up to 5 mins, followed by 50:50 buffer: ACN up to 16 mins, followed by 97:3 Buffer: ACN up to 20 mins. Columns tried are Inertsil ODS 3, Inertsil ODS 3V, Eclipse XDB c18, Phenomenex Gemini C18. Samples prepared in 50:50 Water: Methanol.
After 30-50 injections, the pressure rises to 170-200 bars (initial pressure 96-106 bars). After back flushing or washing at 50 deg celsius using 60:40 ACN water, the pressure reduces. However, again with increasing the aqueous content beyond 60%, the pressure starts rising and the peak shape is also not good. What could be the reason?
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In my opinion try to use Methanol instead of Acetonitrile.....
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Hello everyone,
In analytical field/ human biomonitoring studies, some studies report arithmetic mean, while some report geometric mean.
Any idea, which is a better measure when it comes to representing concentrations in a study involving biological samples (where the concentrations usually vary a lot and are at ppb levels) ?
Thanks in advance!
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I ordered three scents for scent lures for bees: vanillin, eugenol, and methyl salicylate. Vanillin came as a powder, the other two as liquid. What should I dissolve the vanillin in? Literature only says "alcohol". Isopropyl doesn't seem right, it has too strong a smell of its own. Help??
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what is smell less safe solvent for vanillin , to be used as perfume, which do not harm cloths.
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Looking for any specific HPLC method for diatrizoate megumine-assay in diatrizoate meglumine and diatriozate sodium usp solution
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determine Diatrizoate meglumine by HPLC method for CLEANING VALIDATION
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I'm talking in point of view of green analytical chemistry:
Raynie and Driver tool (in green analytical chemistry= GAC): analytical
procedures are evaluated based on five criteria: potential environmental, health and
safety risk, amount of generated waste and energy consumption.
Based on category’s environmental impact, health and safety hazard are evaluated based on NFPA.
NFPA in health hazard is rating 2 for "ETHANOL" whereas Methanol which is more toxic has a rating of 1. Why?
Thank you
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Interesting query...
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the skills of analytical chemistry
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At pH= 9 iron nitrate converts to Fe(OH)3 which precipitates and you cannot obtain a clear solution due to insolubility in water. Actually, Fe(III) is only soluble in acidic conditions but Some of the amphoteric metals such as Al, Zn, Sn,.. are soluble in high basic conditions.
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I'm interested in analytical protocols for measuring exposure to methylphenidate in mice, especially HPLC-based methods. What are the possibilities regarding detectors and sample preparation procedures? Also, considering limited volume of blood can be obtained from mice (and sampling in more time-points probably affects the obtained results) - what would be the best option in the context of the minimal volume of sample needed for the analysis? What about enantiomers (e.g. 10.1002/bmc.3312). I'd like to find/establish a protocol for clinically relevant chronic oral dosing of methylphenidate in mice that reflects what we see in humans (https://www.researchgate.net/post/Protocols_for_clinically_relevant_chronic_oral_dosing_of_methylphenidate_in_mice)
Any info is greatly appreciated.
Jan
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Can you please help me in calculating the concentration of this methylene blue solution in g/L or mol/L?
Methylene Blue Solution- 0.05 wt. % in H2O
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"wt %" means weight percent which is the unit of mass fraction. In the case of such a dilute solution, 0.05 wt %, the mass of the solution in grams is almost equal to its volume in millilitres. So, 1000 mL of the solution contains 5·10-4·1000 = 0.5 g of the substance and the mass concentration is 0.5 g/L. Taking into account that the molar mass of methylene blue is equal to 319.8 g/mol, the molar concentration (also called amount concentration) of this solution is 0.5/319.8 = 0.00156 mol/L.
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How do I find a research collaborator in Analytical Chemistry with bias in starch nanomaterials?
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Join hands with me.
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The concentration of aqueous solution of ibuprofen can be measured by using UV-VIS?
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Yes you can.
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I used a platinum crucible a couple of times to melt some samples wrapped in Al-foil. Now, there are some residual materials in the crucible (solidified), not easy to remove out.
I would like some efficient chemical treatment to clean and remove the residual without losing (etching) platinum.
Thanks in advance!
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Dear Mohammad Tauseef in addition to the expert answers which have already been provided by RG members, it might also be worth having a look at the answers given to the following closely related question which has been asked earlier on RG:
How to clean up the platinum crucible used in thermal analysis?
(10 answers)
For more general information, please also check the following potentially useful guides:
The Correct Use of Platinum in the XRF Laboratory
and
A Guide to Cleaning Platinum Crucibles
Both articles are freely available as full texts. I hope this helps solving your problem. Good luck with you work and best wishes, Frank Edelmann
P.S. I fully agree with Rémi Losno in that you should avoid working with HF if at all possible because of its very high toxicity.
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Does anyone know a quick way to check Sodium lactate or lactic acid concentration in a water solution?
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Hello everyone
I have a question can we use an ion exchange membrane for peptide separation from animal blood or plants for example alfalfa plant? if yes then how it will works, I mean how peptide will divide into ions? will amino acid will convert into amino and carboxylic ions?
I read few papers on it but didn't find any helpful paper on it, which give me detail information of peptide separation by ion exchange membrane.
thank you
Irfan Ali
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I dont have information about this. But you con read the following link may be interested