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Poly anaerobic conditions

Poly(starch-g-(1-amidoethylene)) copolymers can be formed by ceric-ion- initiated, free-radical polymerization of 2-propenamide on starch. Poly(starch- g-[partially hydrolyzed 1-amidoethylene]) can be formed by treatment of an aqueous solution of the copolymer with 0.5 M sodium hydroxide at 40UC under anaerobic conditions. Treatment of the copolymer under these conditions for 10 minutes produces a hydrolyzed copolymer with a degree of hydrolysis between 9 5 and 14 5 percent. [Pg.204]

In general, the main pollution problems associated with surfactants can be summarized as (1) foaming in river and wastewater treatment plants [314,326, 344,348,349,356,357], (2) transformation to bioactive metabolites (i.e., poly-ethoxylated alkylphenols, estrogenic compounds) under aerobic and anaerobic conditions [315,356], and (3) formation of certain cationics which are toxic to microorganisms at high concentrations [356,357]. [Pg.52]

Cell-free systems for methanogen ribosomes are based on the poly(U)- and poly(UG)-programmed system originally developed by Elhardt and Bock [121] for M vannielii. Aside from the tedious procedures involved in carrying out the initial cell fractionations under anaerobic conditions, the methanogen systems do not differ substantially from the classical E. coli cell-free system in their ionic requirements (10 mM Mg ", 10 mM and... [Pg.412]

In 1991, Deming and Novak reported the pronounced effect of molecular oxygen on the polymerization process [16]. Under anaerobic conditions, isocyanides underwent only slow polymerization in the presence of NiCl2, even in ethanol, affording poly(isocyanide)s in only moderate yields of 50-60% after 20 h. When the polymerization was carried out in air at 1 atm, the polymerization was completed within 1 h. Air at 1 atm was sufficient to main-... [Pg.88]

Figure 7. Electrolytic oxidation of 2,6-dimethylphenol. Key O, poly(2,6-dimethyl phenylene oxide) , oligo(2,6-dimethyl phenylene oxide) (1, 2,2 6,6 -tetramethylbiphenoquinone, 0,1 M dimethylphenol in 20% methanol-dichloro-methane containing 0,2 M tetraethyl ammonium bromide, current density 10 mA/cm platinum counter electrodes with saturated calomel reference under anaerobic condition at room temperature. Figure 7. Electrolytic oxidation of 2,6-dimethylphenol. Key O, poly(2,6-dimethyl phenylene oxide) , oligo(2,6-dimethyl phenylene oxide) (1, 2,2 6,6 -tetramethylbiphenoquinone, 0,1 M dimethylphenol in 20% methanol-dichloro-methane containing 0,2 M tetraethyl ammonium bromide, current density 10 mA/cm platinum counter electrodes with saturated calomel reference under anaerobic condition at room temperature.
Poly(2-ethyl-l-vinylimidazole) can be quaternized with ethyl and lauryl bromide. Under anaerobic conditions, the oxidation of thiophenol and 2-hydroxyethane thiol by lO-ethyl-3-raethylisoalloxazine in the presence of these micelle-like polymers, with greater than 29 mol % of lauryl group content, is 10 —I0 -fold faster than the corresponding reaction in a non-polymeric system. This is attributed to desolvation of the thiol anion, required for nucleophilic attack on the flavin, by formation of an ion pair. Strangely, the reaction with butane-1,4-dithiol is unaffected by the polymer. ... [Pg.335]

As has been discussed before, the gas content of a soil is proportional to the water content, because these two phases compete for the same pores. Therefore, the O2 content of a soil decreases (and CO2 increases) with increasing water content, as a consequence of soil respiration. The smaller the grains of a soil and therefore the finer its porosity, the slower will be the gas exchange within the soil. Anaerobic conditions are established under flooded conditions while a lower water content is conducive to aerobic conditions. Hardly any aerobic degradation of substances can be found in a water saturated soil [27]. Aerobic conditions are generally preferable for a fast biodegradation of plastics, even if exceptions do exist. The most notable example is the faster biodegradation of the poly hydroxy-butyrate-valerate under flooded anaerobic conditions [23]. [Pg.70]

Figure 26 Schematic of the catalytic cycle for the PyOD/poly (JUG-co-JUGA)-modified electrode in anaerobic conditions. Reproduced with permission from Dang, L. A. Haccoun, J. etal. Electrochim. Acta 2006, 51 (19), 3934-3943." ... Figure 26 Schematic of the catalytic cycle for the PyOD/poly (JUG-co-JUGA)-modified electrode in anaerobic conditions. Reproduced with permission from Dang, L. A. Haccoun, J. etal. Electrochim. Acta 2006, 51 (19), 3934-3943." ...
PLA may be fabricated into film for packaging and is also made into fibers useful for carpeting (24). PLA is indeed biodegradable, but only under controlled composting conditions. Biodegradation of poly (lactic acid) requires temperatures of about 140 °F for many days to insure decomposition, ultimately into CO and water. Unfortunately, such conditions are not typical of landfills (3) or of most backyard compost heaps. Hence, even plastic bags made from PLA will not quickly disappear from the natural environment. Anaerobic decomposition of PLA results in liberation of methane, an even more potent greenhouse gas than CO (25-28). [Pg.113]


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