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Sorbed

In sorjDtion experiments, the weight of sorbed molecules scales as tire square root of tire time, K4 t) ai t if diffusion obeys Pick s second law. Such behaviour is called case I diffusion. For some polymer/penetrant systems, M(t) is proportional to t. This situation is named case II diffusion [, ]. In tliese systems, sorjDtion strongly changes tire mechanical properties of tire polymers and a sharjD front of penetrant advances in tire polymer at a constant speed (figure C2.1.18). Intennediate behaviours between case I and case II have also been found. The occurrence of one mode, or tire otlier, is related to tire time tire polymer matrix needs to accommodate tire stmctural changes induced by tire progression of tire penetrant. [Pg.2537]

Figure C2.1.18. Schematic representation of tire time dependence of tire concentration profile of a low-molecular-weight compound sorbed into a polymer for case I and case II diffusion. In botli diagrams, tire concentration profiles are calculated using a constant time increment starting from zero. The solvent concentration at tire surface of tire polymer, x = 0, is constant. Figure C2.1.18. Schematic representation of tire time dependence of tire concentration profile of a low-molecular-weight compound sorbed into a polymer for case I and case II diffusion. In botli diagrams, tire concentration profiles are calculated using a constant time increment starting from zero. The solvent concentration at tire surface of tire polymer, x = 0, is constant.
On standing, gelatinous aluminium hydroxide, which may initially have even more water occluded than indicated above, is converted into a form insoluble in both acids and alkalis, which is probably a hydrated form of the oxide AI2O3. Both forms, however, have strong adsorptive power and will adsorb dyes, a property long used by the textile trade to dye rayon. The cloth is first impregnated with an aluminium salt (for example sulphate or acetate) when addition of a little alkali, such as sodium carbonate, causes aluminium hydroxide to deposit in the pores of the material. The presence of this aluminium hydroxide in the cloth helps the dye to bite by ad sorbing it—hence the name mordant (Latin mordere = to bite) dye process. [Pg.151]

Lahajnar, G., Zupancic, L, Rupprecht, A. Proton NMR relaxation and diffusion study of water sorbed in oriented DNA and hyaluronic acid samples. In Biophysics of Water (Franks, F., Mathias, S., eds) Wiley, New York (1982) 231-234... [Pg.126]

The amount of softwood xylan sorbed from alkati at kraft cooking temperatures (100—170°C) is proportional to the quantity of hemiceUulose present and inversely to the extent of branching (57). At neutral pH, the presence of carboxyl groups inhibits sorption compared to a control, but no difference is observed when ionization is suppressed (58). [Pg.31]

The amount of herbicide sorbed by a given soil is influenced by properties of both the soil and the herbicide. Important properties related to the soil s retention abiHty include clay mineralogy, organic matter content, soil pH, and iron and aluminum oxide content. These properties, in turn, affect the... [Pg.47]

Bipyridiniums. The bipyridinium herbicides (Table 2), paraquat and diquat, ate nonselective contact herbicides and crop desiccants. Diquat is also used as a general aquatic herbicide (2,296). Bipyridinium herbicides are organic cations and are retained ia the soil complex via cation exchange. They are strongly sorbed to most soils and are not readily desorbed (332). Both paraquat and diquat are not readily leached (293). [Pg.50]

Considerable research has been conducted to investigate the soil sorption and mobiUty of dinitroaniline herbicides. In general, these herbicides are strongly sorbed by soil (354), and sorption has been correlated to both soil organic matter and clay content (355). Dinitroaniline herbicides are not readily leached in most soils (356), although leaching of triduralin is enhanced by addition of surfactants (357). [Pg.52]

Acid amide herbicides are nonionic and moderately retained by soils. The sorption of several acid amide herbicides has been investigated (369). Acetochlor [34256-82-1] is sorbed more than either alachlor or metolachlor, which are similarly sorbed by a variety of soils. Sorption of all the herbicides is well correlated to soil organic matter content. In a field lysimeter study, metolachlor has been found to be more mobile and persistent than alachlor (370) diphenamid [957-51-7] and napropamide [15299-99-2] have been found to be more readily leached (356). [Pg.52]

Pyridine herbicides are not strongly sorbed to soils and ate readily leached. The mobiUty of flutoxypyt [69377-81-7] has been found to decrease with increasing incubation time (399) this is attributed to entrapment of the herbicide within the soil organic matter. [Pg.53]

Sulfonylurea herbicides ate weak acids and, in general, ate not strongly sorbed to soils. Sorption of chlotsulfuton and metsulfuron—methyl is inversely related to soil pH (407) and is positively correlated to soil organic matter (408). [Pg.53]

Aliphatic-Garboxylics. There are only two herbicides present in this class, trichloroacetate [76-03-9] (TCA) and dalapon [75-99-0]. These are used primarily for the selective control of annual and perennial grass weeds in cropland and noncropland (2,299). Dalapon is also used as a selective aquatic herbicide (427). Dalapon and TCA are acidic in nature and are not strongly sorbed by sods. They are reported to be rapidly degraded in both sod and water by microbial processes (2,427). However, the breakdown of TCA occurs very slowly when incubated at 14—15°C in acidic sods (428). Timing not only accelerates this degradation but also increases the numbers of TCA-degrading bacteria. An HA has been issued for dalapon, but not TCA (269). [Pg.54]

Sorbe, Sicherheitstechnische Kenndaten Chemischer Stoffe, Ecomed VedagsgeseUschaft GmbH, Landsberg/Lech, 1983, p. 11. [Pg.14]

Calcium carbonate (calcite) scale formation in hard water can be prevented by the addition of a small amount of soluble polyphosphate in a process known as threshold treatment. The polyphosphate sorbs to the face of the calcite nuclei and further growth is blocked. Polyphosphates can also inhibit the corrosion of metals by the sorption of the phosphate onto a thin calcite film that deposits onto the metal surface. When the polyphosphate is present, a protective anodic polarization results. [Pg.340]

Some of the most difficult heterophase systems to characterize are those based on hydrocarbon polymers such as mbber-toughened polypropylene or other blends of mbbers and polyolefins. Eecause of its selectivity, RuO staining has been found to be usehil in these cases (221,222,230). Also, OsO staining of the amorphous blend components has been reported after sorption of double-bond-containing molecules such as 1,7-octadiene (231) or styrene (232). In these cases, the solvent is preferentially sorbed into the amorphous phase, and the reaction with OsO renders contrast between the phases. [Pg.418]

Fig. 1. Normal soda Bayer hydrate heated for one hour. A, change in surface area B, total water, LOI plus sorbed water after exposure to 44% rh and C,... Fig. 1. Normal soda Bayer hydrate heated for one hour. A, change in surface area B, total water, LOI plus sorbed water after exposure to 44% rh and C,...

See other pages where Sorbed is mentioned: [Pg.2536]    [Pg.419]    [Pg.34]    [Pg.47]    [Pg.47]    [Pg.48]    [Pg.49]    [Pg.49]    [Pg.50]    [Pg.52]    [Pg.52]    [Pg.53]    [Pg.53]    [Pg.53]    [Pg.53]    [Pg.53]    [Pg.53]    [Pg.54]    [Pg.54]    [Pg.54]    [Pg.299]    [Pg.77]    [Pg.142]    [Pg.84]    [Pg.454]    [Pg.340]    [Pg.351]    [Pg.351]    [Pg.446]    [Pg.105]    [Pg.161]    [Pg.379]    [Pg.147]    [Pg.151]    [Pg.218]   
See also in sourсe #XX -- [ Pg.108 ]

See also in sourсe #XX -- [ Pg.149 ]

See also in sourсe #XX -- [ Pg.87 , Pg.107 , Pg.110 ]




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Ability to sorb

Abiotic hydrolysis, sorbed

Abiotic hydrolysis, sorbed pesticides

Analyte stability sorbed

Atoms and Other Molecules Sorbed onto Solids

Heparin sorbed

Humic sorbed

Irreversibly sorbed phenolic acids

Metal Ions and Complexes Sorbed Onto Solids

Moisture, sorbed

Molecules Sorbed Onto Solids

Noble Gases Sorbed Onto Solids

Nonlinearly sorbing components, overall

Organic Compounds Sorbed Onto Solids

Oxygen sorbed into zeolite

SORBED ORGANICS

Sediment sorbed pesticides

Sediment, sorbed hydrophobic halocarbons

Silica particle sorbed water

Silica sorbed

Soil-sorbed atrazine

Sorbed components

Sorbed halocarbons

Sorbed onto Solids

Sorbed pesticides, abiotic

Sorbed species

Sorbed species, spillover

Sorbed substrates, uptake

Sorbed systems

Sorbing radionuclide retardation

Species specifically sorbed

Specifically sorbed carbonate-bound

Surface area sorbing

System humic acid sorbed

Water Sorbed Onto Solids

Water sorbed

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