Tips for Practical HPLC Analysis —Separation Know-How—

Total Page:16

File Type:pdf, Size:1020Kb

Tips for Practical HPLC Analysis —Separation Know-How— C190-E094 Tips for practical HPLC analysis —Separation Know-how— Shimadzu LC World Talk Special Issue Volume 2 ����� ������������� 2 ����� ������������� This is an compilation of articles related to tips for preparation of mobilephase and samples from introductory, laboratory and technical sections of past issues of the "LCtalk", Shimadzu's newsletter for HPLC users, Japanese version. Contents Page 1. Preparation of Mobile Phases 4 2. Differences between Acetonitrile and Methanol in Reversed Phase Chromatography 6 3. Preparing Mobile Phases - Solvent Mixing Ratio - 8 4. Preparing Buffer Solutions 9 5. pKa and Dissociation Equilibrium 10 6. Water Grade 11 7. Gradient Baseline for Acetonitrile Containing TFA 12 8. Ion-Pair Chromatography 14 - Choosing between Alkyl Sulfonate and Perchloric Acid - 9. Measuring Accurately with Electronic Balances 16 10. Causes of Quantitative Errors Originating in Sample Preparation 18 11. Peaks Caused by Dissolved Air in Sample Solvents 20 12. Influence of Sample Solvent on Peak Shape 22 13. Check Methods for Abnormal Increases in Solvent Delivery Pressure 23 14. Internal Standard Method 26 15. Formulas for Number of Theoretical Plates 27 3 ����� ������������� Preparation of Mobile Phases Aqueous solvents, organic solvents, and mixtures of these types of buffer solution that uses phosphoric acid, but that the counterions solvents are usually used as the mobile phase in high performance are unclear. If we assume that they are sodium ions, the next liquid chromatography (HPLC). Buffer solutions are often used as problem is that we do not know whether the "20 mM" refers to aqueous solutions. Specific preparation methods for some of the the concentration of the phosphoric acid or sodium phosphate. representative buffer solutions used in HPLC are given on page 9. If we think of this solution as "20 mM phosphoric acid (sodium) In general, however, there are many cases where the definition of buffer solution", we can consider "20 mM" to be the concentration buffer solutions is vague. There are also cases where, because of of phosphoric acid. If, however, we consider "20 mM" to be the differences between the instructions given in documentation and concentration of sodium, we can think of this solution as a "buffer the actual preparation methods used, disparities in mobile phases solution created by the pH adjustment of an aqueous solution occur that will affect the chromatograms and the analysis results. of 20 mM sodium dihydrogen phosphate". (The pH value of an There are many aspects of mobile phase preparation that can be aqueous solution of 20 mM sodium phosphate is roughly 5.0, so thought of as blind spots. This applies not just to buffer solutions in order to attain a pH value of 2.5, pH adjustment with some acid but also, for example, to solvent mixing methods. Here, using is required.) Depending on the acid used for pH adjustment, the phosphate buffer as an example, we will look at the effect that the ion-pair effect may occur, and there may be some influence on the mobile phase preparation method can have on analysis results. analysis results. We can see then that there are several possible interpretations for the term "buffer solution". 1) Preparation of Buffer Solutions Fig. 1 shows the effect on the analysis results of interpreting In general, how is something described as "20 mM phosphate the above example three different ways. The top line shows the buffer solution (pH 2.5)" actually prepared? We will look at several result obtained by interpreting "20 mM" as the concentration possible cases. First, let us assume that we are talking about a of phosphoric acid and using a solution prepared as "20 mM Peaks 1. Acetaminophen Peaks ������� �� 1: acetaminophen 2: dihydrocodeine 3: caffeine 2. Dihydrocodeine ���� � ���� Analysis Conditions �� Column: Shim-pack VP-ODS (150 mm × 4.6 mm I.D.) Mobile Phase: Buffer solution (pH 2.5) / Acetonitrile = 9/1 (v/v) Top (A): 20 mM phosphoric acid (sodium) 3. Caffeine Buffer solution (pH 2.5) Middle (B): 20 mM sodium dihydrogen phosphate � ��� Buffer solution (pH 2.5) (Phosphoric acid added for pH adjustment.) Bottom (C): 20 mM sodium dihydrogen phosphate ��� � � Buffer solution (pH 2.5) (Perchloric acid added for pH adjustment.) Flow Rate: 1 mL/min � Temperature: 40 °C Detection: 210 nm � � ��� Chemical Structures of Constituents Fig. 1 Influence of pH Adjustment Method Used for Buffer Solutions 4 ����� ������������� phosphoric acid (sodium) buffer solution (pH 2.5)" as the mobile (sodium) buffer solution (pH 2.5) to that of acetonitrile is 9:1; in phase. The middle and bottom lines show the results obtained by other words, amounts corresponding to this ratio are measured out interpreting "20 mM" as the concentration of sodium dihydrogen and mixed. On the other hand, if we consider this description to phosphate, and adjusting the pH value to 2.5 by respectively simply mean "10% acetonitrile", this implies that 20 mM phosphoric adding phosphoric acid and perchloric acid. As illustrated by acid (sodium) buffer solution (pH 2.5) is used, and is diluted with dihydrocodeine in this example, there are cases where the retention acetonitrile. Applying the latter interpretation changes the relative time and consequently the robustness of the analysis technique are volumes and consequently the amount of 20 mM phosphoric acid significantly affected. (sodium) buffer solution is larger. There is a tendency to think that Indicating the preparation method for buffer solutions so that the there is no significant difference between these two interpretations. solution can be accurately identified helps to prevent problems Fig. 2, however, shows how the mixing method used can have a resulting from differences in interpretation. significant effect on the analysis results (particularly retention times). In general, regarding the preparation of mobile phases for HPLC, it 2) Mixing Organic Solvents and Aqueous Solvents seems that the notation "A:B = 3:2 (V:V)", indicating that an amount Solutions obtained by mixing organic solvents and aqueous solvents of solution A corresponding to a relative volume of 3 and an amount are sometimes used as mobile phases. The way in which mixing is of solution B corresponding to a relative volume of 2 are separately performed can have a significant effect on the analysis results. As an measured out and mixed together, is commonly used. (In practice, example, let us consider a mixture that is 90% 20 mM phosphoric the total volume of the mixture will be less than a relative volume of acid (sodium) buffer solution (pH 2.5) and 10% acetonitrile. If we 5.) consider this description to indicate that the mixing ratio is 9:1, The problems mentioned above occur not only in the preparation this implies that the ratio of the volume of 20 mM phosphoric acid of mobile phases, but also in the preparation of sample solutions and other solutions. Also, different practices and conventions are used in different fields (e.g., pharmaceuticals, chemical industry), further adding to the potential causes of confusion. Official documents, such as the Japanese Pharmacopoeia, Standard Peaks Methods of Analysis for Hygienic Chemists, and Japanese Industrial 1: acetaminophen Standards (JIS) give general principles and definitions related to the 2: dihydrocodeine 3: caffeine preparation of solutions. It is advisable to refer to these documents and to strive on a daily basis to use notation that avoids confusion. Analysis Conditions Column: Shim-pack VP-ODS (150 mm × 4.6 mm I.D.) Mobile Phase: Top (A): 20 mM (phosphoric-acid) sodium buffer solution (pH 2.5) / Acetonitrile = 9/1 (v/v) Bottom (B): Acetonitrile diluted by a factor of 10 with 20 mM (phosphoric- acid) sodium buffer solution (pH 2.5) Flow Rate: 1 mL/min Temperature: 40 °C Detection: 210 nm Fig. 2 Influence of Mixing Method Used for Mobile Phase 5 ����� ������������� Differences between Acetonitrile and Methanol in Reversed Phase Chromatography 1. Acetonitrile Is More Expensive inconsistency. There is not much difference in the price and so, if The organic solvents acetonitrile and methanol are often used as the possible, we should use the HPLC-type. mobile phase in reversed-phase chromatography. Commercial prices of these solvents are relatively expensive, particularly Acetonitrile for 3. The Pressure with Acetonitrile Is Lower HPLC. Acetonitrile appears more often, however, in related literature The pressure applied to the column varies with the type of organic and conditions specified by HPLC manufacturers. Here, we will be solvent and the mixing ratio. Fig. 3 shows some examples illustrating the looking at the reasons for this. relationship between the mixing ratio and the delivery pressure for water/ acetonitrile and water/methanol mixtures. The pressure for methanol 2. HPLC-Type Acetonitrile Has Less Absorbance increases significantly with the proportion of water, whereas the increase Fig. 1 and 2 show absorption spectra for acetonitrile and methanol for acetonitrile is not so marked. Therefore, if acetonitrile is used, undue (commercial HPLC type and special grade). “HPLC type” does not pressure is not applied to the column for the same flow rate. indicate that the solvent has a high absolute purity. This type is created by removing impurities that have UV absorbance and the The two points given above explain why acetonitrile is used. Are there absorbance for specified wavelengths is suppressed so as to lie not, then, any benefits obtained by using methanol, other than the below certain levels. It can be seen that, out of these four reagents, lower price? Other aspects are compared below. HPLC-type acetonitrile has the lowest absorbance (particularly for short wavelengths). Using an organic solvent with lower absorbance 4. In General, Acetonitrile Has a Higher Elution Capacity as the mobile phase results in less noise in UV detection, and so If acetonitrile and methanol are mixed together with water in the same HPLC-type acetonitrile is suitable for high-sensitivity analysis in the proportion, in general, the elution capacity will be higher for acetonitrile.
Recommended publications
  • Use of Solvents for Pahs Extraction and Enhancement of the Pahs Bioremediation in Coal- Tar-Contaminated Soils Pak-Hing Lee Iowa State University
    Iowa State University Capstones, Theses and Retrospective Theses and Dissertations Dissertations 2000 Use of solvents for PAHs extraction and enhancement of the PAHs bioremediation in coal- tar-contaminated soils Pak-Hing Lee Iowa State University Follow this and additional works at: https://lib.dr.iastate.edu/rtd Part of the Environmental Engineering Commons Recommended Citation Lee, Pak-Hing, "Use of solvents for PAHs extraction and enhancement of the PAHs bioremediation in coal-tar-contaminated soils " (2000). Retrospective Theses and Dissertations. 13912. https://lib.dr.iastate.edu/rtd/13912 This Dissertation is brought to you for free and open access by the Iowa State University Capstones, Theses and Dissertations at Iowa State University Digital Repository. It has been accepted for inclusion in Retrospective Theses and Dissertations by an authorized administrator of Iowa State University Digital Repository. For more information, please contact [email protected]. INFORMATION TO USERS This manuscript has been reproduced from the microfilm master. UMI films the text directly from the original or copy submitted. Thus, some thesis and dissertation copies are in typewriter fece, while others may be from any type of computer printer. The quality of this reproduction is dependent upon the quaiity of the copy submitted. Broken or indistinct print colored or poor quality illustrations and photographs, print bleedthrough, substeindard margins, and improper alignment can adversely affect reproduction. In the unlilcely event that the author did not send UMI a complete manuscript and there are missing pages, these will be noted. Also, if unauthorized copyright material had to be removed, a note will indicate the deletion.
    [Show full text]
  • EPA Method 8315A (SW-846): Determination of Carbonyl Compounds by High Performance Liquid Chromatography (HPLC)
    METHOD 8315A DETERMINATION OF CARBONYL COMPOUNDS BY HIGH PERFORMANCE LIQUID CHROMATOGRAPHY (HPLC) 1.0 SCOPE AND APPLICATION 1.1 This method provides procedures for the determination of free carbonyl compounds in various matrices by derivatization with 2,4-dinitrophenylhydrazine (DNPH). The method utilizes high performance liquid chromatography (HPLC) with ultraviolet/visible (UV/vis) detection to identify and quantitate the target analytes. This method includes two procedures encompassing all aspects of the analysis (extraction to determination of concentration). Procedure 1 is appropriate for the analysis of aqueous, soil and waste samples and stack samples collected by Method 0011. Procedure 2 is appropriate for the analysis of indoor air samples collected by Method 0100. The list of target analytes differs by procedure. The appropriate procedure for each target analyte is listed in the table below. Compound CAS No. a Proc. 1b Proc. 2 b Acetaldehyde 75-07-0 X X Acetone 67-64-1 X Acrolein 107-02-8 X Benzaldehyde 100-52-7 X Butanal (Butyraldehyde) 123-72-8 X X Crotonaldehyde 123-73-9 X X Cyclohexanone 108-94-1 X Decanal 112-31-2 X 2,5-Dimethylbenzaldehyde 5779-94-2 X Formaldehyde 50-00-0 X X Heptanal 111-71-7 X Hexanal (Hexaldehyde) 66-25-1 X X Isovaleraldehyde 590-86-3 X Nonanal 124-19-6 X Octanal 124-13-0 X Pentanal (Valeraldehyde) 110-62-3 X X Propanal (Propionaldehyde) 123-38-6 X X m-Tolualdehyde 620-23-5 X X o-Tolualdehyde 529-20-4 X p-Tolualdehyde 104-87-0 X a Chemical Abstract Service Registry Number.
    [Show full text]
  • Development Team
    Paper No: 16 Environmental Chemistry Module: 01 Environmental Concentration Units Development Team Prof. R.K. Kohli Principal Investigator & Prof. V.K. Garg & Prof. Ashok Dhawan Co- Principal Investigator Central University of Punjab, Bathinda Prof. K.S. Gupta Paper Coordinator University of Rajasthan, Jaipur Prof. K.S. Gupta Content Writer University of Rajasthan, Jaipur Content Reviewer Dr. V.K. Garg Central University of Punjab, Bathinda Anchor Institute Central University of Punjab 1 Environmental Chemistry Environmental Environmental Concentration Units Sciences Description of Module Subject Name Environmental Sciences Paper Name Environmental Chemistry Module Name/Title Environmental Concentration Units Module Id EVS/EC-XVI/01 Pre-requisites A basic knowledge of concentration units 1. To define exponents, prefixes and symbols based on SI units 2. To define molarity and molality 3. To define number density and mixing ratio 4. To define parts –per notation by volume Objectives 5. To define parts-per notation by mass by mass 6. To define mass by volume unit for trace gases in air 7. To define mass by volume unit for aqueous media 8. To convert one unit into another Keywords Environmental concentrations, parts- per notations, ppm, ppb, ppt, partial pressure 2 Environmental Chemistry Environmental Environmental Concentration Units Sciences Module 1: Environmental Concentration Units Contents 1. Introduction 2. Exponents 3. Environmental Concentration Units 4. Molarity, mol/L 5. Molality, mol/kg 6. Number Density (n) 7. Mixing Ratio 8. Parts-Per Notation by Volume 9. ppmv, ppbv and pptv 10. Parts-Per Notation by Mass by Mass. 11. Mass by Volume Unit for Trace Gases in Air: Microgram per Cubic Meter, µg/m3 12.
    [Show full text]
  • The Vertical Distribution of Soluble Gases in the Troposphere
    UC Irvine UC Irvine Previously Published Works Title The vertical distribution of soluble gases in the troposphere Permalink https://escholarship.org/uc/item/7gc9g430 Journal Geophysical Research Letters, 2(8) ISSN 0094-8276 Authors Stedman, DH Chameides, WL Cicerone, RJ Publication Date 1975 DOI 10.1029/GL002i008p00333 License https://creativecommons.org/licenses/by/4.0/ 4.0 Peer reviewed eScholarship.org Powered by the California Digital Library University of California Vol. 2 No. 8 GEOPHYSICAL RESEARCHLETTERS August 1975 THE VERTICAL DISTRIBUTION OF SOLUBLE GASES IN THE TROPOSPHERE D. H. Stedman, W. L. Chameides, and R. J. Cicerone Space Physics Research Laboratory Department of Atmospheric and Oceanic Science The University of Michigan, Ann Arbor, Michigan 48105 Abstrg.ct. The thermodynamic properties of sev- Their arg:uments were based on the existence of an eral water-soluble gases are reviewed to determine HC1-H20 d•mer, but we consider the conclusions in- the likely effect of the atmospheric water cycle dependeht of the existence of dimers. For in- on their vertical profiles. We find that gaseous stance, Chameides[1975] has argued that HNO3 HC1, HN03, and HBr are sufficiently soluble in should follow the water-vapor mixing ratio gradi- water to suggest that their vertical profiles in ent, based on the high solubility of the gas in the troposphere have a similar shape to that of liquid water. In this work, we generalize the water va•or. Thuswe predict that HC1,HN03, and moredetailed argumentsof Chameides[1975] and HBr exhibit a steep negative gradient with alti- suggest which species should exhibit this nega- tude roughly equal to the altitude gradient of tive gradient and which should not.
    [Show full text]
  • Package 'Marelac'
    Package ‘marelac’ February 20, 2020 Version 2.1.10 Title Tools for Aquatic Sciences Author Karline Soetaert [aut, cre], Thomas Petzoldt [aut], Filip Meysman [cph], Lorenz Meire [cph] Maintainer Karline Soetaert <[email protected]> Depends R (>= 3.2), shape Imports stats, seacarb Description Datasets, constants, conversion factors, and utilities for 'MArine', 'Riverine', 'Estuarine', 'LAcustrine' and 'Coastal' science. The package contains among others: (1) chemical and physical constants and datasets, e.g. atomic weights, gas constants, the earths bathymetry; (2) conversion factors (e.g. gram to mol to liter, barometric units, temperature, salinity); (3) physical functions, e.g. to estimate concentrations of conservative substances, gas transfer and diffusion coefficients, the Coriolis force and gravity; (4) thermophysical properties of the seawater, as from the UNESCO polynomial or from the more recent derivation based on a Gibbs function. License GPL (>= 2) LazyData yes Repository CRAN Repository/R-Forge/Project marelac Repository/R-Forge/Revision 205 Repository/R-Forge/DateTimeStamp 2020-02-11 22:10:45 Date/Publication 2020-02-20 18:50:04 UTC NeedsCompilation yes 1 2 R topics documented: R topics documented: marelac-package . .3 air_density . .5 air_spechum . .6 atmComp . .7 AtomicWeight . .8 Bathymetry . .9 Constants . 10 convert_p . 11 convert_RtoS . 11 convert_salinity . 13 convert_StoCl . 15 convert_StoR . 16 convert_T . 17 coriolis . 18 diffcoeff . 19 earth_surf . 21 gas_O2sat . 23 gas_satconc . 25 gas_schmidt . 27 gas_solubility . 28 gas_transfer . 31 gravity . 33 molvol . 34 molweight . 36 Oceans . 37 redfield . 38 ssd2rad . 39 sw_adtgrad . 40 sw_alpha . 41 sw_beta . 42 sw_comp . 43 sw_conserv . 44 sw_cp . 45 sw_dens . 47 sw_depth . 49 sw_enthalpy . 50 sw_entropy . 51 sw_gibbs . 52 sw_kappa .
    [Show full text]
  • Calculation Exercises with Answers and Solutions
    Atmospheric Chemistry and Physics Calculation Exercises Contents Exercise A, chapter 1 - 3 in Jacob …………………………………………………… 2 Exercise B, chapter 4, 6 in Jacob …………………………………………………… 6 Exercise C, chapter 7, 8 in Jacob, OH on aerosols and booklet by Heintzenberg … 11 Exercise D, chapter 9 in Jacob………………………………………………………. 16 Exercise E, chapter 10 in Jacob……………………………………………………… 20 Exercise F, chapter 11 - 13 in Jacob………………………………………………… 24 Answers and solutions …………………………………………………………………. 29 Note that approximately 40% of the written exam deals with calculations. The remainder is about understanding of the theory. Exercises marked with an asterisk (*) are for the most interested students. These exercises are more comprehensive and/or difficult than questions appearing in the written exam. 1 Atmospheric Chemistry and Physics – Exercise A, chap. 1 – 3 Recommended activity before exercise: Try to solve 1:1 – 1:5, 2:1 – 2:2 and 3:1 – 3:2. Summary: Concentration Example Advantage Number density No. molecules/m3, Useful for calculations of reaction kmol/m3 rates in the gas phase Partial pressure Useful measure on the amount of a substance that easily can be converted to mixing ratio Mixing ratio ppmv can mean e.g. Concentration relative to the mole/mole or partial concentration of air molecules. Very pressure/total pressure useful because air is compressible. Ideal gas law: PV = nRT Molar mass: M = m/n Density: ρ = m/V = PM/RT; (from the two equations above) Mixing ratio (vol): Cx = nx/na = Px/Pa ≠ mx/ma Number density: Cvol = nNav/V 26 -1 Avogadro’s
    [Show full text]
  • Lecture 3. the Basic Properties of the Natural Atmosphere 1. Composition
    Lecture 3. The basic properties of the natural atmosphere Objectives: 1. Composition of air. 2. Pressure. 3. Temperature. 4. Density. 5. Concentration. Mole. Mixing ratio. 6. Gas laws. 7. Dry air and moist air. Readings: Turco: p.11-27, 38-43, 366-367, 490-492; Brimblecombe: p. 1-5 1. Composition of air. The word atmosphere derives from the Greek atmo (vapor) and spherios (sphere). The Earth’s atmosphere is a mixture of gases that we call air. Air usually contains a number of small particles (atmospheric aerosols), clouds of condensed water, and ice cloud. NOTE : The atmosphere is a thin veil of gases; if our planet were the size of an apple, its atmosphere would be thick as the apple peel. Some 80% of the mass of the atmosphere is within 10 km of the surface of the Earth, which has a diameter of about 12,742 km. The Earth’s atmosphere as a mixture of gases is characterized by pressure, temperature, and density which vary with altitude (will be discussed in Lecture 4). The atmosphere below about 100 km is called Homosphere. This part of the atmosphere consists of uniform mixtures of gases as illustrated in Table 3.1. 1 Table 3.1. The composition of air. Gases Fraction of air Constant gases Nitrogen, N2 78.08% Oxygen, O2 20.95% Argon, Ar 0.93% Neon, Ne 0.0018% Helium, He 0.0005% Krypton, Kr 0.00011% Xenon, Xe 0.000009% Variable gases Water vapor, H2O 4.0% (maximum, in the tropics) 0.00001% (minimum, at the South Pole) Carbon dioxide, CO2 0.0365% (increasing ~0.4% per year) Methane, CH4 ~0.00018% (increases due to agriculture) Hydrogen, H2 ~0.00006% Nitrous oxide, N2O ~0.00003% Carbon monoxide, CO ~0.000009% Ozone, O3 ~0.000001% - 0.0004% Fluorocarbon 12, CF2Cl2 ~0.00000005% Other gases 1% Oxygen 21% Nitrogen 78% 2 • Some gases in Table 3.1 are called constant gases because the ratio of the number of molecules for each gas and the total number of molecules of air do not change substantially from time to time or place to place.
    [Show full text]
  • Acetonitrile
    Fact Sheet Acetonitrile What is Acetonitrile Acetonitrile is a toxic, colorless liquid with an ether-like odor and a sweet, burnt taste. It is an extremely dangerous substance and must be handled with caution as it can cause severe health effects and/or death. It is also known as cyanomethane, ethyl nitrile, ethanenitrile, methanecarbonitrile, acetronitrile cluster and methyl cyanide. Acetonitrile is easily ignited by heat, sparks or flames and gives off highly toxic hydrogen cyanide fumes when heated. It dissolves easily in water. It can react with water, steam or acids to produce flammable vapors that can from explosive mixtures when exposed to air. The vapors are heavier than air and can travel to low or confined areas. Containers of the liquid can explode when heated. Acetonitrile is used to make pharmaceuticals, perfumes, rubber products, pesticides, acrylic nail removers and batteries. It is also used to extract fatty acids from animal and vegetable oils. Before working with acetonitrile, employee training must be provided on safe handling and storage procedures. Pregnant women should avoid contact with acetonitrile. Exposure Exposure usually occurs in the industries where acetonitrile is produced or used. Though unlikely, the general population may be exposed by due to chemical spills, accidents or releases. It is also found in cigarette smoke and automobile exhaust. Acetonitrile changes to cyanide with the body. Route of exposure can occur by: . Breathing ─Inhalation of acetonitrile vapors can cause adverse health effects. Eating/Drinking ─Ingestion of acetonitrile is not a likely route of exposure due to its irritating effects. Skin/Eye Contact ─Acetonitrile vapors and liquids can be absorbed through the skin or eyes.
    [Show full text]
  • An Extractive Distillation System for Benzene-Acetonitrile Separation Using Dimethyl Sulfoxide As an Entrainer Bloch Sohil Y
    An Extractive Distillation System for Benzene-Acetonitrile Separation Using Dimethyl Sulfoxide as an Entrainer Bloch Sohil Y. & Mehulkumar Sutariya Sardar Vallabhbhai National Institute of Technology, Surat Email: [email protected] Unit System: Pressure-Kpa; Molar Flow-kg/hr; Other-SI Background Hydrocarbons like Acetonitrile and Benzene are important raw materials in the manufacturing of polymeric products and as a solvent. They often require high-purity Acetonitrile and Benzene. Acetonitrile is widely used mainly as a solvent in the purification of butadiene in refineries it is widely used in battery applications because of its relatively high dielectric constant and ability to dissolve electrolytes. For similar reasons it is a popular solvent in cyclic voltammetry. Acetonitrile plays a significant role as the dominant solvent used in the manufacture of DNA oligonucleotides from monomers.Industrially, it is used as a solvent for the manufacture of pharmaceuticals and photographic film.The mixer of Acetonitrile and Benzene can not be seperated out by the simple distillation column because of the less difference between their boiling point (near 1.5 K) and same boiling point behaviour of azeotrope. Extractive Distillation of Close Boiling Compounds Extractive distillation is the method of separating close boiling compounds from each other by carrying out the distillation in a multiple columns in the presence of an added liquid or liquid mixture.1 This Liquid or Liquid mixture is known as extractive agent or entrainer. The presence of the entrainer alter the volatility of compounds and thus the degree of separation is increase with the same numbers of plate. This entrainer must have high boiling point than the compounds which are going to separated.
    [Show full text]
  • NMR Chemical Shifts of Common Laboratory Solvents As Trace Impurities
    7512 J. Org. Chem. 1997, 62, 7512-7515 NMR Chemical Shifts of Common Laboratory Solvents as Trace Impurities Hugo E. Gottlieb,* Vadim Kotlyar, and Abraham Nudelman* Department of Chemistry, Bar-Ilan University, Ramat-Gan 52900, Israel Received June 27, 1997 In the course of the routine use of NMR as an aid for organic chemistry, a day-to-day problem is the identifica- tion of signals deriving from common contaminants (water, solvents, stabilizers, oils) in less-than-analyti- cally-pure samples. This data may be available in the literature, but the time involved in searching for it may be considerable. Another issue is the concentration dependence of chemical shifts (especially 1H); results obtained two or three decades ago usually refer to much Figure 1. Chemical shift of HDO as a function of tempera- more concentrated samples, and run at lower magnetic ture. fields, than today’s practice. 1 13 We therefore decided to collect H and C chemical dependent (vide infra). Also, any potential hydrogen- shifts of what are, in our experience, the most popular bond acceptor will tend to shift the water signal down- “extra peaks” in a variety of commonly used NMR field; this is particularly true for nonpolar solvents. In solvents, in the hope that this will be of assistance to contrast, in e.g. DMSO the water is already strongly the practicing chemist. hydrogen-bonded to the solvent, and solutes have only a negligible effect on its chemical shift. This is also true Experimental Section for D2O; the chemical shift of the residual HDO is very NMR spectra were taken in a Bruker DPX-300 instrument temperature-dependent (vide infra) but, maybe counter- (300.1 and 75.5 MHz for 1H and 13C, respectively).
    [Show full text]
  • Interactions Between Polymers and Nanoparticles : Formation of « Supermicellar » Hybrid Aggregates
    1 Interactions between Polymers and Nanoparticles : Formation of « Supermicellar » Hybrid Aggregates J.-F. Berret@, K. Yokota* and M. Morvan, Complex Fluids Laboratory, UMR CNRS - Rhodia n°166, Cranbury Research Center Rhodia 259 Prospect Plains Road Cranbury NJ 08512 USA Abstract : When polyelectrolyte-neutral block copolymers are mixed in solutions to oppositely charged species (e.g. surfactant micelles, macromolecules, proteins etc…), there is the formation of stable “supermicellar” aggregates combining both components. The resulting colloidal complexes exhibit a core-shell structure and the mechanism yielding to their formation is electrostatic self-assembly. In this contribution, we report on the structural properties of “supermicellar” aggregates made from yttrium-based inorganic nanoparticles (radius 2 nm) and polyelectrolyte-neutral block copolymers in aqueous solutions. The yttrium hydroxyacetate particles were chosen as a model system for inorganic colloids, and also for their use in industrial applications as precursors for ceramic and opto-electronic materials. The copolymers placed under scrutiny are the water soluble and asymmetric poly(sodium acrylate)-b-poly(acrylamide) diblocks. Using static and dynamical light scattering experiments, we demonstrate the analogy between surfactant micelles and nanoparticles in the complexation phenomenon with oppositely charged polymers. We also determine the sizes and the aggregation numbers of the hybrid organic-inorganic 1 2 complexes. Several additional properties are discussed, such
    [Show full text]
  • Stability Studies of Selected Polycyclic Aromatic Hydrocarbons in Different Organic Solvents and Identification of Their Transformation Products
    Polish J. of Environ. Stud. Vol. 17, No. 1 (2008), 17-24 Original Research Stability Studies of Selected Polycyclic Aromatic Hydrocarbons in Different Organic Solvents and Identification of Their Transformation Products D. Dąbrowska1, A. Kot-Wasik2, J. Namieśnik*2 1Polish geological institute, Central Chemical laboratory, warsaw, Poland 2Department of Analytical Chemistry, gdansk university of technology, ul. Narutowicza 11/12, 80-892 gdańsk, Poland Received: May 7, 2007 Accepted: October 1, 2007 Abstract one of the problems in an hPlC laboratory is the preservation of samples and extracts prior to analysis without any changes. It has been found that degradation processes cannot be eliminated entirely, but they can be slowed down considerably. Photodegradation kinetics of fluorene, anthracene and benzo(a)pyrene were studied in various organic solvents. Solvents known as good media to store PAhs for a long time were selected with respect to avoid degradation. in the case of fluorene, 9-fluorenone and 9-hydroxyfluorene were detected as main photoproducts. Formation of anthraquinone and 1,8-dihydroxyanthraquinone during the degradation of anthracene was observed. Benzo(a)pyrene-4,5-dihydrodiol and one of the isomers of hydroxy-BaP-dione as products of benzo(a)pyrene photodegradation have been identified. Keywords: polycyclic aromatic hydrocarbons, photodegradation, degradation products, sample stability Introduction 4 or more rings and their metabolites, have a variety of mutagenic and carcinogenic effects on microorganisms, Polycyclic aromatic hydrocarbons (PAhs) are ubiq- plants and animals, and are classified as compounds with uitous contaminants originating from natural and anthro- significant human health risks [6]. pogenic pyrolysis of organic matter such as forest fires, In the environment, primary removal processes of low automobile exhaust, coal and oil refining processes.t heir molecular weight PAhs are microbial degradation and abundance and persistence in several polluted environ- evaporation.
    [Show full text]