Big Chemical Encyclopedia

Chemical substances, components, reactions, process design ...

Articles Figures Tables About

Exposures in Water

The simplest and most economical type of durability testing is probably immersion in water. Even when the final application for an adhesive joint is in a protected and interior type service, it still may be assuring and practical to show that the joint can survive some limited degree of water contact or higher than ambient humidity exposure. We need to remember that component parts or even whole structures may be temporarily stored or shipped under conditions where water or high humidity may be present. This short exposure of a low durability joint may be enough to weaken it and make survival questionable for long-term service even under mild conditions. [Pg.270]

Because of the widespread use of aluminum/wood laminates in architectural applications, literally thousands of durability-type water-resistance tests have been conducted. Such testing was routinely conducted for more than 25 years at the Alcoa Laboratories to establish the data which could give confidence to manufacturers of such bonded structures. While some of this [Pg.271]


To prove the sensitivity enhancement when the attenuation band works within the transition region, a procedure similar to that of the previous paragraph by using chloroform exposure in water at room temperature was carried out. [Pg.68]

Tables 1-1 through 1-4 show the link between exposure to isophorone and known health effects. A Minimal Risk Level (MRL) is also included in Table 1-3. This MRL was derived from animal data for long-term exposure, as described in Chapter 2 and in Table 2-2. The MRL provides a basis for comparison with levels that people might encounter in food. If a person is exposed to isophorone at an amount below the MRL, it is not expected that harmful (noncancer) health effects will occur. Because this level is based on information that is currently available, some uncertainty is always associated with it. Also, because the method for deriving MRLs does not use any information about cancer, a MRL does not imply anything about the presence, absence, or level of risk of cancer. The information on health effects in humans or animals for short-term or long-term exposure to isophorone in air, for short-term exposure in food or water, and for long-term exposure in water was either not available or not suitable to derive MRLs. Tables 1-1 through 1-4 show the link between exposure to isophorone and known health effects. A Minimal Risk Level (MRL) is also included in Table 1-3. This MRL was derived from animal data for long-term exposure, as described in Chapter 2 and in Table 2-2. The MRL provides a basis for comparison with levels that people might encounter in food. If a person is exposed to isophorone at an amount below the MRL, it is not expected that harmful (noncancer) health effects will occur. Because this level is based on information that is currently available, some uncertainty is always associated with it. Also, because the method for deriving MRLs does not use any information about cancer, a MRL does not imply anything about the presence, absence, or level of risk of cancer. The information on health effects in humans or animals for short-term or long-term exposure to isophorone in air, for short-term exposure in food or water, and for long-term exposure in water was either not available or not suitable to derive MRLs.
The problem of osmotic cracking is well known for polyester boat and swimming pool users. After a more or less long time of exposure in water, blisters and cracks appear at the surface. Their formation can be detected sometimes gravimetrically (Fig. 14.10). It can be shown that the induction time of osmotic cracking, tb, is (Gautier et al., 1999) ... [Pg.455]

Fig. 11. (a) FE-SEM image of FHETMS/Si- OH patterned monolayer and (b) ESEM image of a water droplet on an FHETMS/Si-OH patterned monolayer after exposure in water vapor at 273 K. [Pg.207]

No. Polymer Concrete Control Samples After Exposure in Water After Drying... [Pg.13]

Characteristics of Polymer Concretes Depend on Time of Exposure in Water Environment... [Pg.14]

The small decrease or practically no change in density observed for material B in all exposures and for material A in exposures without water is as expected the density of cristobalite is 2.33 g/cm whereas the estimated density of the amorphous phase is 2.45 g/cm thus crystallization of Si02 should lead to a decrease in density. The most extensive crystallization was observed in material B after the bulk exposures in water vapour. Also the oxidation leads to the decrease in density, density of SiC is 3,17 g/cm and of amorphous Si02 2.2 g/cm. A thin oxidation layer formed on cut and plain SiC grain surfaces in all exposures. Despite that the oxidation was minor in material A and again the most effective in material B after the bulk exposures with water vapour. [Pg.159]

Oxidation stability on heating in air is gcxtd, and immersion in water and exposure to high humidity at temperatures up to lOOX has little effect on part dimensions. Steam sterilization is another advantage that is attributable to the resin s high heat stability. However, if the application requires continuous exposure in water, the temperature should be limited to bO C. Polyc arbonates are among the most stable plastics in a wet environment... [Pg.420]

Amey, M, D. H, Johnson, P. A. V. Improved chemistry Key to reduce occupational radiation exposure in water-cooled reactors. Nucler Europe Worldscan X, 34-36 (1990) Anthoni, S., Ridoux, P, Chevalier, C. Evaluation of corrosion products in a pressurized water reactor during shutdown. Proc. 5. BNES Conf. Water Chemistry of Nuclear Reactor Systems. Bournemouth, UK, 1989, Vol. 2, p. 35-39 Antipov, S. A., Dranenko, V. V., Konkov, V. F., Sokolov, I. B., Khaikovskij, A. A. Influence of fuel clad surface on performance under operational and accident conditions. Report... [Pg.333]

Calanus helgolandicus) accumulated more naphthalene after 24 hr when uptake was by diet as opposed to exposure in water without prey. Assessment of the importance of dietary accumulation is difficult in aquatic systems because prey can release compounds to the water, thus confounding the experimental design of assessing only dietary input. For most aquatic organisms, we would expect dietary uptake of LPAHs, such as via sediment ingestion, to have a minor impact on tissue concentrations for these compounds when prey and water are at steady state with each other. [Pg.98]

Ethyl iodide is a heavy liquid, of b.p. 72° and of d, 1 94 insoluble in water, When freshly distilled it is colourless, but on prolonged exposure to light it darkens in colour owing to the liberation of free iodine. Its chemical properties are almost identical with those of ethyl bromide given on pp. 102 and 103. [Pg.107]

Iodobenzene, as usually prepared, is a very pale yellow liquid of b.p. 188°, and d, 1 83. The freshly distilled pure liquid i colourless, but soon redevelops the yellow colour on exposure to light. Iodobenzene is insoluble in water. [Pg.185]

Pure phenol is a colourless crystalline substance, having m.p. 43°, and b.p. 182° on exposure to air, it slowly sublimes, and on exposure to light, develops a pink colour. It has a characteristic odour, and a limited solubility in water. Phenol in dilute aqueous solution has strongly antiseptic properties, but the crystalline substance should not be allowed to come in contact with the skin, as it may cause severe blistering. [Pg.197]

Physical properties. Majority are liquids except p toluidine and 1- and 2-naphthylamine. All are colourless when pure, but rapidly darken on exposure to air and light. All are very sparingly soluble in water, but dissolve readily in dilute mineral acids (except the naphthyl-amines, which are only moderately soluble in adds). They form colourless crystalline salts e.g., CjHjNH2,HCl) which are soluble in water these aqueous solutions usually have an add reaction owing to hydrolysis, and give the reactions of both the amine and the acid from which they are derived. Addition of alkali to the acid solution liberates the amine. [Pg.373]

Furfuryl alcohol, on long storage, becomes progressively darker and less water soluble, a change that is also caused by heat, acidity, and exposure to air. The reactions responsible for this change in water solubiUty may be retarded by the addition in small quantity of an organic or inorganic base. Commercial furfuryl alcohol, however, usually does not contain any additives. [Pg.80]

The dehydrogenation of 2-butanol is conducted in a multitube vapor-phase reactor over a zinc oxide (20—23), copper (24—27), or brass (28) catalyst, at temperatures of 250—400°C, and pressures slightly above atmospheric. The reaction is endothermic and heat is suppHed from a heat-transfer fluid on the shell side of the reactor. A typical process flow sheet is shown in Figure 1 (29). Catalyst life is three to five years operating in three to six month cycles between oxidative reactivations (30). Catalyst life is impaired by exposure to water, butene oligomers, and di-j -butyl ether (27). [Pg.489]

Manganese Hydroxide. Manganese hydroxide [18933-05-6] is a weaMy amphoteric base having low solubihty in water. Mn(OH)2 crystals are reported to be almost pure white and darken on exposure to air. Manganese dihydroxide occurs in nature as the mineral pyrochroite and can also be prepared synthetically by reaction of manganese chloride and potassium hydroxide that is scmpulously free of oxygen. The entire reaction is conducted under reducing conditions (36). [Pg.506]

Naphthalenol. 1-Naphthol, a-naphthol, or l-hydroxynaphthalene/P(9-/j5 -iJ forms colorless needles, mp 96°C, bp 288°C, which tend to become colored on exposure to air or light. It is almost insoluble in water, but readily soluble in alcohol, ether, and benzene. 1-Naphthol and 2-naphthol are found in coal tar (56). [Pg.497]

Maximum Permissible Body Burdens and Maximum Permissible Concentration of Radionuclides in Air and in Water for Occupational Exposure, ReportNo. NCRP, No. 22, National Council on Radiation Protection and Measurement, Washington, D.C., 1959. [Pg.246]


See other pages where Exposures in Water is mentioned: [Pg.98]    [Pg.113]    [Pg.339]    [Pg.16]    [Pg.540]    [Pg.118]    [Pg.923]    [Pg.270]    [Pg.430]    [Pg.98]    [Pg.113]    [Pg.339]    [Pg.16]    [Pg.540]    [Pg.118]    [Pg.923]    [Pg.270]    [Pg.430]    [Pg.30]    [Pg.34]    [Pg.145]    [Pg.155]    [Pg.272]    [Pg.222]    [Pg.240]    [Pg.513]    [Pg.449]    [Pg.279]    [Pg.365]    [Pg.366]    [Pg.434]    [Pg.468]    [Pg.77]    [Pg.2]    [Pg.43]    [Pg.223]    [Pg.230]    [Pg.276]   


SEARCH



Biogeochemical exposure pathways in soil-water systems

Biogeochemical exposure processes in the soil-water system

Exposure Classes, Toxicants in Air, Water, Soil, Domestic and Occupational Settings

© 2024 chempedia.info