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Weighted concentration of effective

Figure 3. Weighted concentration of effective strands for a typical polyol-urethane coating using the kinetics of Figure 2. Figure 3. Weighted concentration of effective strands for a typical polyol-urethane coating using the kinetics of Figure 2.
Figure 4. Weighted concentration of effective strands versus humidity at constant cure time for different initial ratios of isocyanate to hydroxy. The cure time is chosen so that at equal isocyanate and hydroxy and H=0, the extent of reaction is 85%. Figure 4. Weighted concentration of effective strands versus humidity at constant cure time for different initial ratios of isocyanate to hydroxy. The cure time is chosen so that at equal isocyanate and hydroxy and H=0, the extent of reaction is 85%.
Figure 5. Weighted concentration of effective strands versus bake temperature for a typical high solids polyol crosslinked with hexamethoxymethylmelamine. The ratio of methoxy to hydroxy groups is given by "R". For the dashed lines, the extent of methoxy self-condensation is assumed to be zero. The solid lines use the self-condensation data of T. Nakamichi, Prog. Org. Coat., 14, 23 (1986). Figure 5. Weighted concentration of effective strands versus bake temperature for a typical high solids polyol crosslinked with hexamethoxymethylmelamine. The ratio of methoxy to hydroxy groups is given by "R". For the dashed lines, the extent of methoxy self-condensation is assumed to be zero. The solid lines use the self-condensation data of T. Nakamichi, Prog. Org. Coat., 14, 23 (1986).
THIS CROSSLINK DENSITY IS CALLED THE WEIGHTED CONCENTRATION OF" EFFECTIVE STRANDS. ... [Pg.207]

PRINT "THE WEIGHT CONCENTRATION OF EFFECTIVE STRANDS -" LINK 3350 PRINT 3360 PRINT 3370 GOTO 2220... [Pg.212]

Cardiovascular Effects. Information regarding cardiovascular effects in humans after inhalation exposure to chromium and its compounds is limited. In a survey of a facility engaged in chromate production in Italy, where exposure concentrations were 0.01 mg chromium(VI)/m3, electrocardiograms were recorded for 22 of the 65 workers who worked in the production of dichromate and chromium trioxide for at least 1 year. No abnormalities were found (Sassi 1956). An extensive survey to determine the health status of chromate workers in seven U.S. chromate production plants found no association between heart disease or effects on blood pressure and exposure to chromates. Various manufacturing processes in the plants resulted in exposure of workers to chromite ore (mean time-weighted concentration of 0-0.89 mg chromium(ni)/m3) water-soluble chromium(VI) compounds (0.005-0.17 mg chromium(VI)/m3) and acid-soluble/water-insoluble chromium compounds (including basic chromium sulfate), which may or may not entirely represent trivalent chromium (0-0.47 mg chromium/m3) (PHS 1953). No excess deaths were observed from cardiovascular diseases and ischemic heart disease in a cohort of 4,227 stainless steel production workers from 1968 to 1984 when compared to expected deaths based on national rates and matched for age, sex, and calender time (Moulin et al. 1993). No measurements of exposure were provided. In a cohort of 3,408 individuals who had worked in 4 facilities that produced chromium compounds from chromite ore in northern New Jersey sometime between 1937 and 1971, where the exposure durations of workers ranged from <1 to >20 years, and no increases in atherosclerotic heart disease were evident (Rosenman and Stanbury 1996). The proportionate mortality ratios for white and black men were 97 (confidence limits 88-107) and 90 (confidence limits 72-111), respectively. [Pg.63]

In the case of macromolecule-macromolecule interactions, the relationship between the Rayleigh factor and weight concentration of macromolecules is complicated by the fact that the coefficient B is needed to account for this effect (Equation (4.7)). [Pg.127]

Weinbauer, M. G., and Peduzzi, P. (1995). Effect of virus-rich high molecular weight concentrates of seawater on the dynamics of dissolved amino acids and carbohydrates. Mar. Ecol. Prog. Ser. 127, 245-253. [Pg.467]

A typical antifoam consists of an oil (polydimethylsiloxane or hydrocarbon), dispersed hydro-phobic solid particles (e.g., hydrophobized silica), or a mixture of both. The oil-solid mixtures are often called antifoam compounds. The weight concentration of the solid particles in compounds is around several percent (typically between 2 and 8). A strong synergistic effect between the oil and the solid particles is observed in the compounds — in most cases, the latter are much more efficient than either of their individual components, if taken separately. The compounds are used at a concentration below 0.1 wt%, whereas the oils are used at higher concentrations (up to several percent) due to their lower antifoam efficiency. The antifoams are usually preemulsified in the form of oil drops or mixed oil-solid globules of micrometer size. [Pg.265]

Sect. 3.1 with various weight concentrations of aD2-8CB, i.e. Xlc = 0.28, 0.08 and 0.006. The last of the listed samples represented a control sample. Although it contained practically no 8CB molecules it underwent the swelling with solvents, which resulted in the extraction of the nonreacted mesogens, the crosslinkers and the short polymer segments, and was thus free of all the additives that might have induced the plasticizing effect. [Pg.180]

FIGURE 8-46 Effect of the size of the pump impeller on the correction factor for head Rif for slurry at a weight concentration of 42%. (From Sellgren and Addie, 1992.). [Pg.485]

The amounts of HDPE in a blend and the shear rate were chosen as independent variables in this study. Experiments were carried out in the melt state at 190°C. A Goodrich method was used for determination of effective instrument dimensions, which allows one to employ the Daane et al procedure in order to relate torque-rheometer data to more fundamental rheological values. The same HDPE/LDPE ratios were used in the study of mechanical behavior of HDPE/LDPE system of injected specimens. As said previously, DSC thermograms were used to determine weight concentration of two crystalline components both in HDPE/LDPE blends and wastes. [Pg.63]

Hydrogen selenide in a concentration of 1.5 ppm is intolerable to man. Selenium occurs in some solid in amounts sufficient to produce serious effects on animals feeding on plants, such as locoweed, grown in such soils. Exposure to selenium compounds (as Se) in air should not exceed 0.2 mg/m3 (8-hour time-weighted average - 40-hour week). [Pg.97]


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Effect of concentration

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Weighted concentration of effective strands

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