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Other Poly hydrocarbons

The distribution of the products obtained from this reaction depends upon the reaction temperature (Figure 5.1-4) and differs from those of other poly(ethene) recycling reactions in that aromatics and alkenes are not formed in significant concentrations. Another significant difference is that this ionic liquid reaction occurs at temperatures as low as 90 °C, whereas conventional catalytic reactions require much higher temperatures, typically 300-1000 °C [100]. A patent filed for the Secretary of State for Defence (UK) has reported a similar cracking reaction for lower molecular weight hydrocarbons in chloroaluminate(III) ionic liquids [101]. An... [Pg.209]

Adamantane and other tertiary hydrocarbons have been converted by applying this method [nitrosonium tetrafluoroborate/pyridinium poly(hydrogen fluoride) (PPHF)] into the corresponding fluorohydrocarbons in excellent yields.88... [Pg.622]

Schaufele at Esso Research in Lynden, N. J and the other at Southampton. It is not intended to observe any chronological order in this paper but rather to consider polymers under chemical types commencing with the most fundamental of all, the poly-hydrocarbons. [Pg.157]

In addition, the presence additional chlorinated compounds in the PET mixed plastics such as 3P/PVC/PET and MWP were found to be chlorine derivatives of benzoic acids. Kulesza and German [36] reported the influence of poly(vinyl chloride) on poly(ethylene terephthalate) pyrolysis. They reported that the chloroesters of terephthalic and benzoic acids were found with PVC and PET mixtures (1 1). In our present investigation, the PVC/PET ratio was 1 1 and contains the other plastics such as PE, PP and PS. The ratio of mixed plastics PP PE PS PVC PET was 3 3 3 1 1 and this composition was prepared are similar to the real municipal waste from Sapporo, Japan. 2-Methyl benzoylchloride was identified as one of the additional chlorinated hydrocarbons observed in 3P/PVC/PET and MWP degradation than 3P/PVC degradation chlorinated hydrocarbons. The other chlorinated hydrocarbons could not be identified in 3P/PVC/PET and MWP degradation. It is evident from the studies that the new chlorine compounds obtained due to the presence of PET in plastic samples in either model mixed on MWP. [Pg.523]

The microstructure of anionic polymerization of other poly(l,3-diene)s with lithium as counterion in hydrocarbon media is also predominantly 1,4 microstructure [3], However, higher amounts of cm-1,4-microstructures are obtained with more sterically hindered diene monomers. Thus, using conditions that provide polyisoprene with 70% cm-1,4, 22% trans-, A, and 7% 3,4 microstructure, 2-/-propyl-1,3-butadiene and 2-n-propyl-l,3-butadiene provide 86% and 91% cm-1,4 enchainment, respectively. Both... [Pg.145]

Due to the higher oxygen permeability (Table 1) unsubstituted poly(norbornene) (P2) is much easier oxidized than the poly(norbornene-esters) P3 - P6 or -imids Pll - P13. An exceptionally high 02 permeability was found in poly(cyclooctene) (PI), which has no tertiary carbon atoms and is therefore, nevertheless, oxidatively relatively stable. Loose packing due to a high content of macrocycles might be the reason for the high 02-permeability of PI, compared to other rubbery hydrocarbon polymers. [Pg.121]

Like poly(trimethylene diselenide), other higher hydrocarbon diselenide polymers were prepared either by hydrolysis of respective selenocynate... [Pg.111]

The microstmcture of anionic polymerization of other poly (l,3-diene)s with lithium as counterion in hydrocarbon media is... [Pg.578]

Currently, almost all acetic acid produced commercially comes from acetaldehyde oxidation, methanol or methyl acetate carbonylation, or light hydrocarbon Hquid-phase oxidation. Comparatively small amounts are generated by butane Hquid-phase oxidation, direct ethanol oxidation, and synthesis gas. Large amounts of acetic acid are recycled industrially in the production of cellulose acetate, poly(vinyl alcohol), and aspirin and in a broad array of other... [Pg.66]

Unlike most crystalline polymers, PVDF exhibits thermodynamic compatibiUty with other polymers (133). Blends of PVDF and poly(methyl methacrylate) (PMMA) are compatible over a wide range of blend composition (134,135). SoHd-state nmr studies showed that isotactic PMMA is more miscible with PVDF than atactic and syndiotactic PMMA (136). MiscibiUty of PVDF and poly(alkyl acrylates) depends on a specific interaction between PVDF and oxygen within the acrylate and the effect of this interaction is diminished as the hydrocarbon content of the ester is increased (137). Strong dipolar interactions are important to achieve miscibility with poly(vinyhdene fluoride) (138). PVDF blends are the object of many papers and patents specific blends of PVDF and acryflc copolymers have seen large commercial use. [Pg.387]

Synthetic oils have been classified by ASTM into synthetic hydrocarbons, organic esters, others, and blends. Synthetic oils may contain the following compounds diaLkylben2enes, poly(a-olefins) polyisobutylene, cycloaUphatics, dibasic acid esters, polyol esters, phosphate esters, siUcate esters, polyglycols, polyphenyl ethers, siUcones, chlorofluorocarbon polymers, and perfluoroalkyl polyethers. [Pg.368]

Many similar hydrocarbon duids such as kerosene and other paraffinic and naphthenic mineral oils and vegetable oils such as linseed oil [8001-26-17, com oil, soybean oil [8001-22-7] peanut oil, tall oil [8000-26-4] and castor oil are used as defoamers. Liquid fatty alcohols, acids and esters from other sources and poly(alkylene oxide) derivatives of oils such as ethoxylated rosin oil [68140-17-0] are also used. Organic phosphates (6), such as tributyl phosphate, are valuable defoamers and have particular utiHty in latex paint appHcations. Another important class of hydrocarbon-based defoamer is the acetylenic glycols (7), such as 2,4,7,9-tetramethyl-5-decyne-4,7-diol which are widely used in water-based coatings, agricultural chemicals, and other areas where excellent wetting is needed. [Pg.463]

As a class the aliphatic polyalkenamers have low values due to a combination of low chain stiffness and low interchain attraction. The presence of double bonds has the effect of increasing the flexibility of adjacent single bonds (see Chapter 4) and overall this leads to a reduction in. Thus in the sequence from polydecenamer down to polypentenamer an increase in the double bond concentration leads to a lowering of Tg. On the other hand the Tg of polybutenamer, i.e. poly butadiene, is somewhat higher than that of polypentenamer, presumably because the proportion of stiff links, i.e. double bonds, becomes sufficiently high to override the flexibilising effect on adjacent chains. Consequently the polypentenamers have the lowest Tg values known for hydrocarbon polymers (cis- -114°C, trans- -97°C). [Pg.305]

In addition to its water solubility poly(vinyl pyrrolidone) is soluble in a very wide range of materials, including aliphatic halogenated hydrocarbons (methylene dichloride, chloroform), many monohydric and polyhdric alcohols (methanol, ethanol, ethylene glycol), some ketones (acetyl acetone) and lactones (a-butyrolactone), lower aliphatic acids (glacial acetic acid) and the nitro-paraffins. The polymer is also compatible with a wide range of other synthetic polymers, with gums and with plasticisers. [Pg.475]

The high thermal and chemical stability of fluorocarbons, combined with their very weak intermolecular interactions, makes them ideal stationary phases for the separation of a wide variety of organic compounds, including both hydrocarbons and fluorine-containing molecules Fluonnated stationary phases include per-fluoroalkanes, fluorocarbon surfactants, poly(chlorotrifluoroethylene), polyfper-fluoroalkyl) ethers, and other functionalized perfluoro compounds The applications of fluonnated compounds as stationary phases in gas-liquid chroma... [Pg.1029]


See other pages where Other Poly hydrocarbons is mentioned: [Pg.422]    [Pg.422]    [Pg.443]    [Pg.422]    [Pg.422]    [Pg.443]    [Pg.402]    [Pg.8]    [Pg.9]    [Pg.93]    [Pg.402]    [Pg.28]    [Pg.93]    [Pg.119]    [Pg.44]    [Pg.1826]    [Pg.1028]    [Pg.52]    [Pg.246]    [Pg.161]    [Pg.18]    [Pg.363]    [Pg.68]    [Pg.248]    [Pg.304]    [Pg.360]    [Pg.477]    [Pg.367]    [Pg.273]    [Pg.62]    [Pg.268]    [Pg.32]    [Pg.916]   


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Other Hydrocarbons

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