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Skin effects analysis

Technical procedures to determine production rate, reservoir pressure, temperature, permeability, and skin effect, and to sample gas and liquids for analysis. [Pg.22]

Inasmuch as it was assumed that the skin effect manifests itself in an external area only, i.e. interaction between currents within the internal area is negligible, we can think that the inphase component is caused by currents within the external area only. Proceeding from this consideration we can rewrite some of eqs. 3.111-3.133 in a more general form. Validity of this step also follows from analysis of the integral equation 3.88 and its first approximation 3.89. [Pg.184]

With an increase in frequency the influence of the skin effect in parts of a medium located relatively close to a borehole becomes stronger and correspondingly Doll s theory cannot be applied. An increasing frequency, first of all, leads to the fact that the signal becomes more sensitive to the skin effect in an external area, i.e. in the bed. For this reason, function da is defined by the right-hand part of eq. 4.95 and therefore it depends on the frequency. From the analysis of the field of the magnetic dipole in a uniform medium (Chapter 2) follows, that with an increase in frequency the influence of relatively remote parts of the medium decreases. If the conductivities of the borehole and invasion zone essentially exceed that of the formation and the skin effect manifest itself practically in the latter, it cannot affect the value of the apparent conductivity, da- For this reason the relative contribution of the secondary field increases with frequency almost in the same manner as follows from Doll s theory. If the internal areas (borehole and invasion zone) are less conductive than the bed, the ratio of the secondary signal to the primary one increases slower than the frequency does. [Pg.226]

These examples, as well as a more detailed analysis, demonstrate that calculations based on the exact solution which takes into account the skin effect are necessary in order to investigate the vertical responses of the introduction probe. [Pg.347]

For a more accurate evaluation of parameters of a medium, when probes 6F1M, 4F1 and 4F1.1 allow us to determine the formation resistivity, it is necessary to calculate the apparent conductivity for these probes in media with cylindrical interfaces. Results of such analysis are described below. Let us notice that calculations have been performed proceeding from the approximate theory which takes into account the skin effect in the external area. [Pg.416]

The start of every selection process should be an identification of the hazardous chemicals and an exposure risk analysis. The risk analysis may identify other methods of mitigation potential exposure that may reduce or eliminate the need to rely on CPC. You should assess exposure from skin absorption and skin effect from burns, sensitization, and/or other chemical hazards. Assessments should also consider biological, heat, fire, and mechanical hazards that may factor into the selection of CPC. Also, the hazards presented by CPC should be considered. CPC may contribute to heat stress, reduced mobility, obscured vision, difficulty in communication, lessened hand function (dexterity, grip, tactility), poor comfort, and skin illnesses. CPC may also affect the efficacy of other PPE worn, for example, ear muffs and respirators. Also, the other potential hazards (e.g., heat and flame) should be identified in the early stage of selection. [Pg.17]

TPO A plaques from each of the injection molding parameter sets were analyzed. Based on the results from the TPO A analysis, only plaques from Conditions 3 and 5 in Table 1 were tested for TPO B measuring the effects of barrel temperature and back pressure). The microtomed specimens were taken from identical core regions on each plaque to minimize variables originating from the flow effects of the tool itself and to avoid skin effects. The micrographs were taken in the transverse to flow direction in all cases. [Pg.2614]

The effects of pH on electrokinetic velocities in micellar electrokinetic chromatography was studied by using sodium dodecyl sulfate solutions [179]. Micellar electrokinetic capillary chromatography with a sodium dodecyl sulfate pseudostationary phase has been used to determine the partition constants for nitrophenols, thiazolylazo dyes, and metal chelate compounds [180]. A similar technique was used to separate hydroquinone and some of its ether derivatives. This analysis is suitable for the determination of hydroquinone in skin-toning creams [181]. The ingredients of antipyretic analgesic preparations have also been determined by this technique [182], The addition of sodium dodecyl sulfate improves the peak shapes and resolution in chiral separations by micellar electrokinetic chromatography [183]. [Pg.274]

Rohsenow DJ, Monti PM, Colby SM, et al Naltrexone treatment for alcoholics effect on cigarette smoking rates. Nicotine Tob Res 5 231-236, 2003 Rose JE, Levin ED Concurrent agonist-antagonist administration for the analysis and treatment of drug dependence. Pharmacol Biochem Behav 41 219—226, 1991 Rose JE, Behm FM, Westman EC, et al Mecamylamine combined with nicotine skin patch facilitates smoking cessation beyond nicontine patch treatment alone. Clin Pharmacol Ther 56 86-99, 1994... [Pg.337]

Topal, U. et al.. Extraction of lycopene from tomato skin with supercritical carbon dioxide effect of operating conditions and solubility analysis, J. Agric. Food Chem., 54, 5604, 2006. [Pg.500]

Dermal Effects. Skin irritation was noted in wildlife officers at the RMA after they handled sick or dead ducks without gloves (NIOSH 1981). Although the investigators concluded that diisopropyl methylphosphonate contributed to the local effects, a number of other compounds were present. Analysis of the pond water indicated the presence of a number of organic and inorganic contaminants, including diisopropyl methylphosphonate (11.3 ppm) aldrin (0.368 ppm) dieldrin (0.0744 ppm) dicyclo-pentadiene, bicycloheptadiene, diethyl benzene, dimethyl disulfide, methyl acetate, methyl isobutyl ketone, toluene, and sodium (49,500 ppm) chloride (52,000 ppm) arsenic (1,470 ppm) potassium (180 ppm) fluoride (63 ppm) copper (2.4 ppm) and chromium (0.27 ppm). Because of the presence of numerous compounds, it is unclear whether diisopropyl methylphosphonate was related to the irritation. [Pg.64]

Skin irritation was noted in wildlife officers at the RMA who handled dead or sick ducks without gloves. Analysis of the pond water indicated the presence of a number of organic and inorganic contaminants, including diisopropyl methylphosphonate. Although the investigators concluded that diisopropyl methylphosphonate contributed to the effects, a number of other compounds were identified in the pond, the presence of which makes it unclear whether diisopropyl methylphosphonate was related to the irritation (NIOSH 1981). [Pg.88]

Sunbeds with fluorescent lamps that emit in the UVA and UVB are used for indoor tanning. They are supposed to simulate the solar UV spectrum and have therefore similar effects on the human skin. However, the intensity of radiation is often not monitored, and excessive exposure may cause serious dermatological health problems. A more detailed analysis reveals that the long-wave UV (UVA) is mainly responsible for the tanning while UVB radiation tends to be more dangerous. [Pg.167]

DiGiovanni, J. and T.J. Slaga. 1981a. Effects of benzo(e)pyrene [B(e)P] and dibenz(a,c)anthracene [DB(a,c)A] on the skin tumor-initiating activity of polycyclic aromatic hydrocarbons. Pages 17-31 in M. Cooke and A.J. Dennis (eds.). Chemical Analysis and Biological Fate Polynuclear Aromatic Hydrocarbons. Fifth International Symposium. Battelle Press, Columbus, OH. [Pg.1398]

Partial what-if analyses for the two example processes described in Section 4.0 are shown in Tables 4.9 and 4.10. Although for actual, more complex analyses, the what-if tables for each line or vessel would be separate, for these examples, a single table was developed. A preliminary hazard analysis (PHA) would identify that the intrinsic hazards associated with HF are its reactivity (including reactivity with water, by solution), corrosivity (including carbon steel, if wet), toxicity via inhalation and skin contact, and environmental toxicity. The N2 supply system pressure is not considered in this example. The specific effects of loss of containment could be explicitly stated in the "loss of HF containment" scenarios identified. Similarly, the effects of loss of chlorine containment, including the reactivity and toxicity of chlorine, could be specified for the second example. [Pg.47]

Setlow, R. B., The wavelengths in sunlight effective in producing skin cancer A theoretical analysis, Proc. Natl. Acad. Sci. USA 71, 3363-3366, 1974. [Pg.271]

Hematological Effects. Routine blood parameters (hemoglobin, erythrocyte, leukocyte and thrombocyte levels) measured in 11 hexachloroethane workers did not differ from those of the controls (Selden et al. 1994). Plasma hexachloroethane levels in these workers, who wore protective equipment, were 7.3 + 6.04 pg/L at the time of the hematological analysis and 0.08 0.14 gg/L before production resinned (Selden et al. 1993). Mild skin and mucous membrane irritation were reported in the exposed group, suggesting that exposure may have been through either the inhalation or dermal routes of exposure. [Pg.39]


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