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Particulate instrumentation

Design Considerations for Particulate Instrumentation by Laser Light Scattering (Pills) Systems... [Pg.295]

Cheremisinoff, P.N. Air/Particulate Instrumentation and Analysis Ann Arbor Science Ann Arbor, 1981. [Pg.3907]

The nebulization concept has been known for many years and is commonly used in hair and paint spays and similar devices. Greater control is needed to introduce a sample to an ICP instrument. For example, if the highest sensitivities of detection are to be maintained, most of the sample solution should enter the flame and not be lost beforehand. The range of droplet sizes should be as small as possible, preferably on the order of a few micrometers in diameter. Large droplets contain a lot of solvent that, if evaporated inside the plasma itself, leads to instability in the flame, with concomitant variations in instrument sensitivity. Sometimes the flame can even be snuffed out by the amount of solvent present because of interference with the basic mechanism of flame propagation. For these reasons, nebulizers for use in ICP mass spectrometry usually combine a means of desolvating the initial spray of droplets so that they shrink to a smaller, more uniform size or sometimes even into small particles of solid matter (particulates). [Pg.106]

An aerosol produced instrumentally has similar properties, except that the aerosol is usually produced from solutions and not from pure liquids. For solutions of analytes, the droplets consist of solute and solvent, from which the latter can evaporate to give smaller droplets of increasingly concentrated solution (Figure 19.1). If the solvent evaporates entirely from a droplet, the desolvated dry solute appears as small solid particles, often simply called particulate matter. [Pg.137]

The instrumental analyzer procedure, EPA Method 3A, is commonly used for the determination of oxygen and carbon dioxide concentrations in emissions from stationary sources. An integrated continuous gas sample is extracted from the test location and a portion of the sample is conveyed to one or more instrumental analyzers for determination of O9 and CO9 gas concentrations (see Fig. 25-30). The sample gas is conditioned prior to introduction to the gas analyzer by removing particulate matter and moisture. Sampling is conducted at a constant rate for the entire test run. Performance specifications and test procedures are provided in the method to ensure reliable data. [Pg.2199]

Figure 15-1 shows the Los Angeles, California, basin stationary air monitoring network, one of the most extensive in the United States (6). At most of these locations, automated instruments collect air quality data continuously. Five pollutant gases are monitored, and particulate matter filter samples are collected periodically. [Pg.218]

Remove particulate matter before sample enters instrument... [Pg.550]

Particle Sampler an instrument to measure particulate matter in ambient air. Particulate Matter dust, soot, other tiny bits of solid materials that are released into and move around in the air. See also fine particle, PM,o. [Pg.541]

With particles, the contaminant concentration in the duct is determined by isokinetic sampling with subsequent laboratory analysis use of a calibrated direct reading instrument. If the concentration distribution in the duct is uneven, a complete survey of the concentration distribution with the corresponding duct velocities and cross-sectional area is required. National and ISO standards provide information on isokinetic sampling and velocity measurements. In the case of particles, the airborne emission differs from the total emission, for example in the case of granular particulate. The contaminant settling on surfaces depends on particle distribution, airflow rates, direction in the space, electrical properties of the surfaces and the material, and the amount of moisture or grease in the environment. [Pg.1018]

In the measurement of emission gas mass concentration at sources, a gas sample is extracted via an automatic isokinetic particulate-sampling instrument. The monitoring system generates a direct, real-time emission particulate mass... [Pg.1289]

The concentrations monitored by these instruments range from a few milligrams to 4000 mg/m A flow diagram of a beta gauge particulate monitor is shown in Fig. 13.41. [Pg.1291]

Cascade impactor An instrument used to sample and separate particulates into a number of successive fractions of different sizes. [Pg.1420]

LIDAR An instrument that uses a laser-radar to study the concentration and location of particulate matter by the reflection or absorption of a laser beam. [Pg.1455]

Standardization. Standardization in analytical chemistry, in which standards are used to relate the instrument signal to compound concentration, is the critical function for determining the relative concentrations of species In a wide variety of matrices. Environmental Standard Reference Materials (SRM s) have been developed for various polynuclear aromatic hydrocarbons (PAH s). Information on SRM s can be obtained from the Office of Standard Reference Materials, National Bureau of Standards, Gaithersburg, MD 20899. Summarized in Table VII, these SRM s range from "pure compounds" in aqueous and organic solvents to "natural" matrices such as shale oil and urban and diesel particulate materials. [Pg.115]

Air-Classification Measurement Electronic airborne particle monitoring instruments count and size particulate matter in the sampled air with no consideration of whether the particles are viable or nonviable. Air classification is defined as the number of particles per cubic foot of air that are larger than 0.5 pm in diameter. Climet and HIAC-Royco are common instruments for airborne particulate monitoring). [Pg.414]

Instruments that measure scattered light, such as the Photo-Nephelometer (Coleman Instruments, Oak Brook, IL), are used to evaluate and set clarity standards for parenteral preparations. It is not possible to establish an overall standard value for all products (e.g., 30 ne-phelos) because the value itself is relative and influenced by many factors, including concentration, aging, stopper extracts, and the solubility characteristics of the raw materials. Nephelometer readings are insensitive to contamination by large (visible) particulates. [Pg.416]

These instruments employ a continuous flow of persulfate solution to promote oxidation prior to ultraviolet irradiation, and have a low system blank and low detection limit. Since all reactions take place in the liquid phase, problems suffered by combustion techniques, such as catalyst poisoning, reactor corrosion, and high-temperature element burnouts, are obviated. However, the ultraviolet-promoted chemical oxidation technique is not designed to handle particulate-containing samples, and tends to give incomplete oxidation for certain types of compounds such as cyanuric acid. [Pg.488]

Spray-forming, of particulate metal-matrix composites, 16 175 Spray functions, 23 174t Spray impact, 23 197 measurements, 23 194-195 Spraying processes, for sodium carbonate peroxohydrate, 18 412 Spraying techniques, in fluidized-bed encapsulation, 11 541-542 Spray instrumentation, 23 192-195 Spray irrigation... [Pg.877]

HPLC techniques were initially developed as liquid-liquid chromatographic methods and difficulties in maintaining the stationary phase were resolved by chemically bonding it to the particulate support. Subsequently a whole range of column materials have been developed that enable the basic HPLC instrumentation to be used for the major chromatographic techniques. [Pg.113]


See other pages where Particulate instrumentation is mentioned: [Pg.304]    [Pg.304]    [Pg.583]    [Pg.2201]    [Pg.48]    [Pg.545]    [Pg.111]    [Pg.94]    [Pg.588]    [Pg.15]    [Pg.76]    [Pg.119]    [Pg.10]    [Pg.827]    [Pg.280]    [Pg.497]    [Pg.101]    [Pg.257]    [Pg.385]    [Pg.365]    [Pg.327]    [Pg.187]    [Pg.784]    [Pg.785]    [Pg.789]    [Pg.163]    [Pg.524]    [Pg.5]    [Pg.314]    [Pg.267]   
See also in sourсe #XX -- [ Pg.295 ]




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