Big Chemical Encyclopedia

Chemical substances, components, reactions, process design ...

Articles Figures Tables About

Determining concentration

Determining Concentration by Turbidimetry In turbidimetry the measured transmittance, T, is the ratio of the transmitted intensity of the source radiation, fy, to the intensity of source radiation transmitted by a blank, Iq. [Pg.442]

Determining Concentration by Nephelometry In nephelometry, the relationship between the intensity of scattered radiation, hy and the concentration (% w/v) of scattering particles is given as... [Pg.443]

Determining Concentration bet s assume that the redox reaction at the working electrode is... [Pg.514]

Analysis of Standards The analysis of a standard containing a known concentration of analyte also can be used to monitor a system s state of statistical control. Ideally, a standard reference material (SRM) should be used, provided that the matrix of the SRM is similar to that of the samples being analyzed. A variety of appropriate SRMs are available from the National Institute of Standards and Technology (NIST). If a suitable SRM is not available, then an independently prepared synthetic sample can be used if it is prepared from reagents of known purity. At a minimum, a standardization of the method is verified by periodically analyzing one of the calibration standards. In all cases, the analyte s experimentally determined concentration in the standard must fall within predetermined limits if the system is to be considered under statistical control. [Pg.710]

Once these corrections are made, quantitative ema can be used to determine concentrations of elements in the near-surface region (ca 1 -lm) of samples of interest. [Pg.285]

In thermoluminescence dating, a sample of the material is heated, and the light emitted by the sample as a result of the de-excitations of the electrons or holes that are freed from the traps at luminescence centers is measured providing a measure of the trap population density. This signal is compared with one obtained from the same sample after a laboratory irradiation of known dose. The annual dose rate for the clay is calculated from determined concentrations of radioisotopes in the material and assumed or measured environmental radiation intensities. [Pg.419]

Mycotoxins, toxic metaboUtes of some fungi, can be assayed by immunochemical techniques to determine concentration in animal feed and foodstuffs. Some of the analytes assayed in kits and the detection limits are Hsted in Table 4 (45). These assays are especially advantageous for routine analysis of large samples of foodstuffs (45,46). [Pg.101]

The potentiometry sensor (ion-selective electrode) controls application for determination of polymeric surface-active substances now gets the increasing value. Potentiometry sensor controls are actively used due to simple instmment registration, a wide range of determined concentrations, and opportunity of continuous substances contents definition. That less, the ionometry application for the cation polymeric SAS analysis in a solution is limited by complexity of polycation charge determination and ion-exchanger synthesis. [Pg.108]

The procedure of simultaneous extracting-spectrophotometric determination of nitrophenols in wastewater is proposed on the example of the analysis of mixtures of mono-, di-, and trinitrophenols. The procedure consists of extraction concentrating in an acid medium, and sequential back-extractions under various pH. Such procedures give possibility for isolation o-, m-, p-nitrophenols, a-, P-, y-dinitrophenols and trinitrophenol in separate groups. Simultaneous determination is carried out by summary light-absorption of nitrophenol-ions. The error of determination concentrations on maximum contaminant level in natural waters doesn t exceed 10%. The peculiarities of application of the sequential extractions under fixed pH were studied on the example of mixture of simplest phenols (phenol, o-, m-, />-cresols). The procedure of their determination is based on the extraction to carbon tetrachloride, subsequent back-extraction and spectrophotometric measurement of interaction products with diazo-p-nitroaniline. [Pg.126]

To determine of Ce(IV) in acid soluble single crystals, a simple and sensitive method is proposed. The method is based on the reaction of tropeoline 00 oxidation by cerium(IV) in sulfuric acid solution with subsequent measurement of the light absorption decrease of the solution. The influence of the reagent concentration on the analysis precision is studied. The procedure for Ce(IV) determination in ammonium dihydrophosphate doped by cerium is elaborated. The minimal determined concentration of cerium equal to 0.04 p.g/ml is lower than that of analogous methods by a factor of several dozens. The relative standard deviation does not exceed 0.1. [Pg.198]

NAA is a quantitative method. Quantification can be performed by comparison to standards or by computation from basic principles (parametric analysis). A certified reference material specifically for trace impurities in silicon is not currently available. Since neutron and y rays are penetrating radiations (free from absorption problems, such as those found in X-ray fluorescence), matrix matching between the sample and the comparator standard is not critical. Biological trace impurities standards (e.g., the National Institute of Standards and Technology Standard Rference Material, SRM 1572 Citrus Leaves) can be used as reference materials. For the parametric analysis many instrumental fiictors, such as the neutron flux density and the efficiency of the detector, must be well known. The activation equation can be used to determine concentrations ... [Pg.675]

NRA exploits the body of data accumulated through research in low-energy nuclear physics to determine concentrations and distributions of specific elements or isotopes in a material. Two parameters important in interpreting NRA spectra are reaction Qvalues and cross sections. [Pg.681]

Bayliss et al. (1963) emphasize that they did not detect the nitrosoacidium ion in spectrophotometrically determinable concentrations. In our opinion, however, it may be more cautious to say that there is no spectroscopic evidence for two species on the more acidic side of that series of spectra with increasing acid concentrations. [Pg.47]

Spectrophotometric methods for determining concentration of Pu(111, IV, VI, and "polymer") in nitrate media have been reported.(30) Adaptation of such procedures to routine rapid in-line analysis of feed and raffinate solutions may be possible. [Pg.359]

We see that the experimentally determined concentration range converts into a pH range of 1. That is, the buffer acts most effectively within a range of 1 units of p/v, (Fig. 11.3). For instance, because the pKa of H2P04 is 7.21, a KH2P04/K2HP04 buffer can be expected to be most effective between about pH = 6.2 and pH = 8.2. [Pg.572]

Figure 2. Analytical procedure used for determining concentration of nucleic acids from fluorescence. Figure 2. Analytical procedure used for determining concentration of nucleic acids from fluorescence.
The problem describes a weak diprotic acid and asks for ion concentrations. To determine concentrations of all ions, we need to consider more than one equilibrium. This is done in stages, starting with the dominant equilibrium. We apply the seven-step strategy. The problem asks us for the concentrations of the ions in carbonated water, in which the major species are H2 CO3 and H2 O. [Pg.1253]

Now we are ready to organize the data and the unknowns and do the calculations. The spectator ion is easiest to deal with [K- -] = 2 [S03 -] = 2 (0.075 M) = 0.15 M There are multiple equilibria affecting ion concentrations, so we must work with more than one concentration table, starting with the dominant equilibrium. Set up a concentration table to determine concentrations of the ions generated by this reaction ... [Pg.1259]

Determining concentrations requires a quantitative equilibrium calculation, so we apply the seven-step strategy. The complexation equilibrium is given in the problem. [Pg.1324]

As the Nemst equation describes, cell potentials are linked quantitatively to concentrations. One practical consequence of this relationship is that potential measurements can be used to determine concentrations of ions in... [Pg.1395]

Many dehydrogenase enzymes catalyze oxidation/reduction reactions with the aid of nicotinamide cofactors. The electrochemical oxidation of nicotinamide adeniiw dinucleotide, NADH, has been studied in depthThe direct oxidation of NADH has been used to determine concentration of ethanol i s-isv, i62) lactate 157,160,162,163) pyTuvate 1 ), glucose-6-phosphate lactate dehydrogenase 159,161) alanine The direct oxidation often entails such complications as electrode surface pretreatment, interferences due to electrode operation at very positive potentials, and electrode fouling due to adsorption. Subsequent reaction of the NADH with peroxidase allows quantitation via the well established Clark electrode. [Pg.65]

R. Kuchenbuch and A. Jungk, A method for determining concentration profiles at the soil-root interface by thin slicing rhizospheric soil. Plant Soil 68 391 (1982). R. Schonwitz and H. Ziegler, Quantitative and qualitative aspects of a developing rhizosphere microflora of hydroponically grown maize seedlings. Z Pflanzenernahr. Bodenk. 749 623 (1986). [Pg.36]

R. Kuchenbuch and A. Jungk, A inethod for determining concentration profiles at the soil-root interface by thin slicing rhizospheric soil. Plant Soil 68 39 (1982). [Pg.196]

Two multi-residue methods are described. These methods have been used to determine concentrations of either parent herbicides or their metabolites in thousands of surface water and groundwater samples collected over the years 1995-2001 in corn-growing areas of the United States. " ... [Pg.349]

The method using GC/MS with selected ion monitoring (SIM) in the electron ionization (El) mode can determine concentrations of alachlor, acetochlor, and metolachlor and other major corn herbicides in raw and finished surface water and groundwater samples. This GC/MS method eliminates interferences and provides similar sensitivity and superior specificity compared with conventional methods such as GC/ECD or GC/NPD, eliminating the need for a confirmatory method by collection of data on numerous ions simultaneously. If there are interferences with the quantitation ion, a confirmation ion is substituted for quantitation purposes. Deuterated analogs of each analyte may be used as internal standards, which compensate for matrix effects and allow for the correction of losses that occur during the analytical procedure. A known amount of the deuterium-labeled compound, which is an ideal internal standard because its chemical and physical properties are essentially identical with those of the unlabeled compound, is carried through the analytical procedure. SPE is required to concentrate the water samples before analysis to determine concentrations reliably at or below 0.05 qg (ppb) and to recover/extract the various analytes from the water samples into a suitable solvent for GC analysis. [Pg.349]

The method for chloroacetanilide soil metabolites in water determines concentrations of ethanesulfonic acid (ESA) and oxanilic acid (OXA) metabolites of alachlor, acetochlor, and metolachlor in surface water and groundwater samples by direct aqueous injection LC/MS/MS. After injection, compounds are separated by reversed-phase HPLC and introduced into the mass spectrometer with a TurboIonSpray atmospheric pressure ionization (API) interface. Using direct aqueous injection without prior SPE and/or concentration minimizes losses and greatly simplifies the analytical procedure. Standard addition experiments can be used to check for matrix effects. With multiple-reaction monitoring in the negative electrospray ionization mode, LC/MS/MS provides superior specificity and sensitivity compared with conventional liquid chromatography/mass spectrometry (LC/MS) or liquid chromatography/ultraviolet detection (LC/UV), and the need for a confirmatory method is eliminated. In summary,... [Pg.349]

It follows from the equation (3.28) that the liquid technique to determine concentration of dissolved oxygen or oxygen of extraneous gases being analyzed (nitrogen, hydrogen, inert gases, hydrocarbons, etc.) which are in equilibrium with liquid polar solvent (water, alcohols, etc.), is applicable as well. This means that relation... [Pg.215]

As part of its Radionuclides in Food Program, the FDA determined concentrations of radionuclides in their Total Diet Study, as well as food originating from the vicinity of nuclear reactors including raw vegetables, food crops (primarily fruits), fish, and milk. While not specifically analyzed for 241Am, concentrations of... [Pg.186]


See other pages where Determining concentration is mentioned: [Pg.723]    [Pg.486]    [Pg.284]    [Pg.400]    [Pg.2168]    [Pg.2320]    [Pg.30]    [Pg.206]    [Pg.206]    [Pg.16]    [Pg.572]    [Pg.275]    [Pg.336]    [Pg.44]    [Pg.1252]    [Pg.1254]    [Pg.103]    [Pg.441]    [Pg.597]    [Pg.15]    [Pg.195]   
See also in sourсe #XX -- [ Pg.246 ]

See also in sourсe #XX -- [ Pg.246 ]




SEARCH



Actinides concentration, determination

Analytical techniques, concentration determinations

Anionic surfactant concentrations quantitative determination

Antigen concentration determination

Bovine serum albumin concentration determination

Calcium concentration determination

Carbon dioxide concentration determined

Carbonyl concentration, determination

Chromatographic determination model, concentrations

Compound concentration determination

Concentration Determination through Standard Solution Addition

Concentration change determination

Concentration dependence, determination

Concentration determination amine

Concentration determination analysis

Concentration determination calibration methods

Concentration determination ethanol

Concentration determination glucose

Concentration determination glycerol

Concentration determine

Concentration determine

Concentration factors, determination

Concentration polarization determination

Concentration, determination

Concentration, determination

Concentration-Response Plots and IC50 Determination

Concentration-depth gradient determination

Critical micellar concentration determination

Critical micelle concentration determination

Critical micelle concentrations, determination micelles

Determination of Aluminum Ion Concentration

Determination of Calcium Ion Concentration

Determination of Chloride Ion Concentration

Determination of Minimal Alveolar Anesthetic Concentration (MAC)

Determination of Potassium Ion Concentration

Determination of SLO Concentrations

Determination of concentration

Determination of critical micelle concentration

Determination of hydrogen ion concentration

Determination of lattice concentrations

Determination of maximum additive concentration

Determination of sample concentrations

Determination of surfactant concentration by H-NMR

Determination of the Product Concentration at Various Times

Determining the optimum concentration rate

Drinking water factors determining lead concentration

Drug concentration determination

Enzymatic analysis, concentration determination

Enzyme concentration determination

Equilibrium concentrations determining

Equilibrium monomer concentration determination

Experiment 8 Determination of Concentration by Oxidation-Reduction Titration and an Actual Student Lab Write-Up

Factors Determining the Lead Concentration in Drinking Water

How Allowable Residue Concentrations Are Determined

Hydrogen concentration determination

Hydroxyl group concentration determination

Indirect Concentration Determination

Intracellular concentrations, determination

Macromolecular therapeutics concentration determination

Magnesium , concentrations determination

Manganese concentration determinations

Mass concentration determining

Maximum additive concentration determination

Maximum plasma concentration determination

Metabolite concentrations, determination

Metabolite concentrations, determination lines

Metallic element concentrations, determination

Minimum bactericidal concentration determination

Minimum inhibitory concentration determination

Oxygen atoms, concentration determination

Oxygen atoms, concentration determination rate constants

Oxygen atoms, concentration determination reaction mechanisms

Oxygen atoms, concentration determination reactions

Oxygen, determination equilibrium concentrations

Parameters Determining Helium Concentration in Groundwater

Peak plasma concentration determination

Pectate concentration determination

Plasma concentration determination

Plasma concentration versus time plots determination

Protein concentration determination

Rate-concentration graphs, determination

Reference standard material concentration determination

Serum concentration, determination

Solution concentration potential-determining ions

Steady state concentration determination

Suspension concentration determination

The determination of concentration

Theory for concentration determination with the x-ray gravitational sedimentation technique

Titration Procedures for Determining Concentrations

Total arsenic concentration analytical determination

Total salt concentration, determination

Water, determination Waters, concentrated

© 2024 chempedia.info