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Sampling monitor types

A sensitive and rapid chromatographic procedure using a selective analytical detection method (electrospray ionization-mass spectrometry in SIM mode) in combination with a simple and efficient sample preparation step was presented for the determination of zaleplon in human plasma. The separation of the analyte, IS, and possible endogenous compounds are accomplished on a Phenomenex Lima 5-/rm C8(2) column (250 mm x 4.6 mm i.d.) with methanol-water (75 25, v/v) as the mobile phase. To optimize the mass detection of zaleplon, several parameters such as ionization mode, fragmentor voltage, m/z ratios of ions monitored, type of organic modifier, and eluent additive in the mobile phase are discussed. Each analysis takes less than 6 min. The calibration curve of zaleplon in the range of 0.1-60.0 ng/ml in plasma is linear with a correlation coefficient of >0.9992, and the detection limit (S/N = 3) is 0.1 ng/ml. The within- and between-day variations (RSD) in the zaleplon plasma analysis are less than 2.4% (n = 15) and 4.7% (n = 15), respectively. The application of this method is demonstrated for the analysis of zeleplon plasma samples [14]. [Pg.363]

I Tracking of Oil Spills on Water Surveillance of Other Types of Spills Monitoring of Atmospheric and Environmental Conditions Sampling/Monitoring of Environmental Contamination Documentation of Activities during Emergencies... [Pg.132]

Types of sampling programs that could be used to meet the above objectives are exploratory sampling, monitoring, and presence/absence sampling. [Pg.14]

Two types of sampling monitors are in general use air samples are used to assess the airborne contamination levels at selected points. In the case of particulate materials a volume of air is drawn through a filter paper on which the particulates are deposited. An alarm may be set on increase of activity. [Pg.328]

Fig. 7 Schematic of an automated direct probe system for molecular weight determination that features an ion trap MS. Samples are dissolved in a suitable solvent and injected via an automated syringe system onto the DEP wire. The probe is injected into the MS via an automated isolation valve system and the temperature is ramped to the programmed temperature. After sample analysis the probe is removed from the source and heated to a high temperature to clean the DEP wire in preparation for the next sample. This type of integrated, open-access MS-based application provides routine, unattended support for medicinal chemistry needs such as reaction monitoring and the optimization of reaction conditions. (Courtesy of Scientific Instrument Services, Ringoes, NJ.)... Fig. 7 Schematic of an automated direct probe system for molecular weight determination that features an ion trap MS. Samples are dissolved in a suitable solvent and injected via an automated syringe system onto the DEP wire. The probe is injected into the MS via an automated isolation valve system and the temperature is ramped to the programmed temperature. After sample analysis the probe is removed from the source and heated to a high temperature to clean the DEP wire in preparation for the next sample. This type of integrated, open-access MS-based application provides routine, unattended support for medicinal chemistry needs such as reaction monitoring and the optimization of reaction conditions. (Courtesy of Scientific Instrument Services, Ringoes, NJ.)...
General information on monitor types and configurations is given in CESSAR-DC Section 11.5.1.2.1. Typically a monitor consists of components such as a microprocessor, one or more detectors, a shielded detection chamber, a sample pump, flow instrumentation, and associated tubing and cabling. Sufficient shielding is provided to ensure that the required sensitivity is achieved at... [Pg.374]

Recordkeeping The anployer must keep an accurate record of all measurements taken to monitor employee exposure to asbestos. This record is to include the date of measmanent, operation involving exposure, sampling and analytical methods used, and evidence of their accuracy number, duration, and results of samples taken type of respiratory protective devices worn name, social security number, and the results of all employee exposure measurements. This record must be kept for 30 years. [Pg.317]

Depending on the isotopes monitored and the nature of the sample, several types of mass bias correction models can be used when coupling chromatography to MC-ICP-MS. Some studies report the use of internal mass bias correction with an exponential law when an invariant isotope ratio is available (as is the case, for example, for Sr or Nd) [27, 29-31]. It is the simplest model, as merely another isotope ratio of the element of interest is used for the correction. [Pg.504]

Diffusivities of various elements ate determined experimentally. Dopant profiles can be determined. The junction depth can be measured by chemically staining an angle-lapped sample with an HE/HNO mixture. The -type region of the junction stains darker than the n-ty e region. The sheet resistivity can also be measured using a four-point probe measurement. These two techniques ate used for process monitoring. [Pg.349]

Health and Safety. Remover formulas that are nonflammable may be used in any area that provides adequate ventilation. Most manufacturers recommend a use environment of 50—100 parts per million (ppm) time weighted average (TWA). The environment can be monitored with passive detection badges or by active air sampling and charcoal absorption tube analysis. The vapor of methylene chloride produces hydrogen chloride and phosgene gas when burned. Methylene chloride-type removers should not be used in the presence of an open flame or other heat sources such as kerosene heaters (8). [Pg.551]


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See also in sourсe #XX -- [ Pg.549 ]




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