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Exposure methods

In summary, intratracheal instillation of CNTs has shown that their potential in eliciting adverse pulmonary effects is influenced by exposure time, CNT dose, CNT biopersistence, surface defects, and metal contamination [71, 72]. Despite the use of surfactants, all studies showed that intratracheal instillation caused major difficulties due to the agglomerative nature of CNTs in a biological environment. More realistic exposure methods, namely inhalation rather than intratracheal administration, are therefore needed for determining the pulmonary toxicity [59, 65, 73]. Several investigations have been performed by using administration different from intra-... [Pg.185]

The horizontal exposure method is not very adequate for the OSU RHR calorimeter, because the heat reflected from the aluminum foil onto the sample is much lower than the heat generated by the glow bars. Since the OSU calorimeter is based on the adiabaticity of the measurements, any heat losses will represent inaccurate results. The reflection on the aluminum foil is also uneven. Moreover, the use of higher radiant energy causes problems with the mechanical functioning of the instrument (bending and buckling of the back plate). [Pg.526]

Belt-conveyor scales, 26 244—245 Belt filter press, 25 913 Belt saponification, in vinyl alcohol polymerization, 25 609-610 Benard instability, 11 764 Benazepril hydrochloride, molecular formula and structure, 5 149t Benchmark dose and margin-of-exposure method, 25 244... [Pg.91]

Derelanko, M.J., Gad, S.C., Gavigan, F.A., Babich, P.C. and Rinehart, W.E. (1987). Toxicity of hydroxylamine sulfate following dermal exposure Variability with exposure method and... [Pg.501]

The position and angle of the test pieces to the sun (for both radiation and temperature) is important. A wide range of exposure methods and angles are available at most test stations. The more conventional and widely used are ... [Pg.53]

Exposure. Methods for Determining Parent Compounds and Degradation Products in Environmental Media.Methods are available for measuring di-tt-octylphthalate and/or its metabolites (primarily the corresponding phthalate monoesters) in urine, blood, and tissues (Albro and Moore 1974 Lanina et al. [Pg.113]

Both the ELISA and Western blot suffer from the problem that antibodies may not appear in an aposed individual s blood until months after the initial exposure. Methods for using PCR to screen blood samples for HIV are being developed, PCR amplification of the HIV provirai DNA 7-ovides the ability to detect HIV at earlier stages of infection, because the viral nucleic acid is r resent immediately upon exposure. It is used to detect HIV infection in newborns whose mothers are HIV positive. [Pg.107]

Exposure. Methods for detecting chloroform in exhaled breath, blood, urine, and tissues are available. Nevertheless, it is difficult to correlate chloroform levels in biological samples with exposure, because of the volatility and short half-life of chloroform in biological tissues. Several studies monitored chloroform levels in environmentally exposed populations (Antoine et al. 1986 Hajimiragha et al. 1986 Peoples et al. 1979) however, the measured levels probably reflect both inhalation and oral exposure. Moreover, increased tissue levels of chloroform or its metabolites may reflect exposure to other chlorinated hydrocarbons. Studies to better quantitate chloroform exposure would enhance the database. [Pg.182]

Dietary administration is not recommended, except for materials of low toxicity and for which gavage administration is not practical. Rabbits generally have very variable food consumption, and dietary administration is not suitable. Inhalation dosing is appropriate for some substances both whole body and nose only exposure are possible for teratology studies (10) and it is recommended that the same exposure method is used as in previous toxicity studies. [Pg.62]

Optical Lithography. Lithographic processes can be classified according to the energy used to expose the resists and the equipment necessary to accomplish the process. Image quality depends on the exposure method, hardware, and resist material. In optical lithography, the resist is exposed to radiation within the near- to deep-UV region (200-450 nm). [Pg.335]

The exposure of humans to pesticides from residues In food is dependent both on the quantity of a food consumed and the residue levels therein. The Agency has traditionally used a simplified method of estimating chronic exposure to pesticide residues that was originally developed by the Food and Drug Administration. This exposure method is based on the assumptions of tolerance level residues in food and national average food consumption per capita. [Pg.13]

All of the previously mentioned exposure methods can be used to estimate either chronic exposure (over a period of years) or acute exposure (single day) for the United States population and population subgroups. Both chronic and acute assessments are usually based on a no observed adverse effect level (NOAEL) in an animal species. Acute exposure is defined relative to an acute (single dose) toxicological endpoint (usually a NOAEL) and may be expressed as a margin of exposure (MOE) or as a percentage of an acute reference dose that is based on a NOAEL and an uncertainty factor (see below). [Pg.414]

Another factor that influences strongly the evolution of polarization reversal in fe bulk crystals is the limited minimization of the depolarization field by means of screening charges. In the case of the afm tip of R 50 nm the screening charge is limited both by the size of the tip and its non-ohmic contact with the sample surface. Such an effect is especially pronounced in the case of indirect electron beam exposure method described in this paper. The strong limitation of the screening phenomenon provides a necessary condition for the observed effect of fdb [13-15],... [Pg.194]

A new ionization method called desorption electrospray ionization (DESI) was described by Cooks and his co-workers in 2004 [86]. This direct probe exposure method based on ESI can be used on samples under ambient conditions with no preparation. The principle is illustrated in Figure 1.36. An ionized stream of solvent that is produced by an ESI source is sprayed on the surface of the analysed sample. The exact mechanism is not yet established, but it seems that the charged droplets and ions of solvent desorb and extract some sample material and bounce to the inlet capillary of an atmospheric pressure interface of a mass spectrometer. The fact is that samples of peptides or proteins produce multiply charged ions, strongly suggesting dissolution of the analyte in the charged droplet. Furthermore, the solution that is sprayed can be selected to optimize the signal or selectively to ionize particular compounds. [Pg.61]

An inadequate method of treating the insects will also result in a nonlinear line. It is assumed that the applied dose will always be proportional to the dose received. If this is not the case, however, we can see that some of the insects, probably those given the higher doses, will receive proportionally less than others. This could happen in topical applications or with residual exposure methods. Therefore, caution and care are required in performing dose-response tests in resistance studies (Terriere, 1982). [Pg.98]


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See also in sourсe #XX -- [ Pg.19 , Pg.92 , Pg.93 , Pg.105 ]




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Corrosion testing continued exposure methods

Definition of PDE. Method for establishing exposure limits

Exposure analytical methods

Exposure-Assessment Methods

Residual exposure method

Risk assessment methods concentration-exposure time

Worker exposure field methods

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