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  • 1
    ISSN: 1520-5835
    Source: ACS Legacy Archives
    Topics: Chemistry and Pharmacology , Physics
    Type of Medium: Electronic Resource
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  • 2
    ISSN: 1520-5835
    Source: ACS Legacy Archives
    Topics: Chemistry and Pharmacology , Physics
    Type of Medium: Electronic Resource
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  • 3
    Electronic Resource
    Electronic Resource
    s.l. : American Chemical Society
    Macromolecules 24 (1991), S. 2129-2131 
    ISSN: 1520-5835
    Source: ACS Legacy Archives
    Topics: Chemistry and Pharmacology , Physics
    Type of Medium: Electronic Resource
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  • 4
    Electronic Resource
    Electronic Resource
    s.l. : American Chemical Society
    Macromolecules 25 (1992), S. 5867-5872 
    ISSN: 1520-5835
    Source: ACS Legacy Archives
    Topics: Chemistry and Pharmacology , Physics
    Type of Medium: Electronic Resource
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  • 5
    Electronic Resource
    Electronic Resource
    Oxford, UK : Blackwell Publishing Ltd
    Annals of the New York Academy of Sciences 446 (1985), S. 0 
    ISSN: 1749-6632
    Source: Blackwell Publishing Journal Backfiles 1879-2005
    Topics: Natural Sciences in General
    Type of Medium: Electronic Resource
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  • 6
    Electronic Resource
    Electronic Resource
    Springer
    Materials and structures 23 (1990), S. 352-357 
    ISSN: 1359-5997
    Source: Springer Online Journal Archives 1860-2000
    Topics: Architecture, Civil Engineering, Surveying
    Description / Table of Contents: Résumé On résume une série d'études destinées à déterminer la cause de l'odeur désagréable et de la détérioration de matériaux de revêtements de sols (‘sick building syndrome”). Les odeurs désagréables et la détérioration des revêtements de sols, c'est-à-dire le noircissement, etc... dans des bâtiments où pour la confection de chapes on s'est servi d'un béton contenant de la caséine sont imputables à la biodégradation de la molécule de protéine par différentes espèces deClostridia, qui se sont adaptées aux conditions extrêmes (haut pH: 12 et températures relativement basses: 17°C). Ces nouvelles propriétés desClostridia leur permenttent dans ces conditions extrêmes de transformer la molécule de caséine en acides organiques volatiles et en monoamines. On a discerné des acides organiques, tels que l'acide propionique, butyrique, etc... et des monoamines comme la triéthylène et di-iso-butylamine dans le béton biodétérioré. Les monoamines sont odorigènes et contribuent largement à l'odeur désagréable qui se dégage dans certains bâtiments construits entre 1979 et 1982. Les acides se trouvent chimiquement liés dans le béton. On ne peut donc les déceler par leur odeur désagréable. Une simulation de l'attaque du béton par une action biodégradante a montré qu'on obtenait en laboratoire (in vitro) les mêmes acides que ceux dont la présence avait été détectée dans un sol recouvert de béton.
    Notes: Abstract A summary is given of a series of studies performed in order to explain one cause of bad odour and spoilage of floor covering materials (‘sick building syndrome’). Bad odours as well as spoilage of floor covering materials, i.e. blackening etc., inside buildings with self-levelling concrete containing casein are due to the biodegradation of the protein molecule by different species ofClostridia, which have adapted themselves to the extreme environment, i.e. a high pH and a relatively low temperature (pH 12 and 17°C). These new characteristics ofClostridia make it possible, under these extreme conditions, for theClostridia to degrade the casein molecule to volatile organic acids and monoamines. Organic acids such as propionic acid, butyric acid etc, and monoamines such as triethylamine, di-iso-butylamine etc. have been detected in biodegraded concrete. The monoamines are odorous and contribute strongly to the bad odour experienced inside some buildings constructed between 1979 and 1982. The acids are chemically bound in the concrete and can therefore not be observed as bad odour. A simulation of the biodegradative attack on concrete showed that the same acids were produced in the laboratory (in vitro) as the one detected in the floor covered with concrete.
    Type of Medium: Electronic Resource
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  • 7
    Electronic Resource
    Electronic Resource
    Springer
    Polymer bulletin 12 (1984), S. 237-243 
    ISSN: 1436-2449
    Source: Springer Online Journal Archives 1860-2000
    Topics: Chemistry and Pharmacology , Mechanical Engineering, Materials Science, Production Engineering, Mining and Metallurgy, Traffic Engineering, Precision Mechanics , Physics
    Notes: Abstract Acrylates and methacrylates of 1,3(2,4-dihydroxyphenyl)-di(2H-benzotriazole) and 1,3(2,4,6-trihydroxyphenyl)-di(2H-benzotriazole) have been prepared by treating acrylic acid or methacrylic acid with N,N′-dicyclohexyl carbodiimide and then allowing this mixture to react with the phenolic ultraviolet absorbers to give 1,3[2-hydroxy-4-acryloxy(methacryloxy)phenyl]-di(2H-benzotriazole) and 1,3[2,6-dihydroxy-4-acryloxy(methacryloxy)phenyl]-di(2H-benzotriazole). The yield of the esters was from 10 to 30%; they were characterized by their infrared, 1H, and 13C NMR spectra; their polymerizability was demonstrated. The compounds had X of 330 to 335 nm with extinction coefficients ranging from 3.0 to 3.5×104 L/mol·cm.
    Type of Medium: Electronic Resource
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  • 8
    ISSN: 1432-0614
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology , Process Engineering, Biotechnology, Nutrition Technology
    Notes: Summary Reports on malodour in buildings constructed in the late 1970s gave rise to thorough investigations on the possible role of vapours of chemical compounds emitted by building materials. The odour could be related to the use of casein as an additive to improve the fluidity of concrete materials used as a self-levelling floor topping compound. Casein was suggested to be degraded by microorganisms, resulting in an accumulation of malodorous substances in the topping compounds. Bacteria isolated from biodeteriorated concrete materials containing caseins exhibited unusual tolerance towards high pH. Two dominant species were found among a total of 80 sporeforming, anaerobic isolates from concrete and raw products of caseins, namely Clostridium bifermentans and Clostridium sporogenes. C. bifermentans had a maximal pH tolerance of 12.2 while C. sporogenes could reproduce up to pH 11.7. The study includes the identification of the clostridia with API multitest as well as an investigation of the volatile organic acid and monoamine patterns. About 100 cfu clostridia/g material could be obtained during the isolation procedures.
    Type of Medium: Electronic Resource
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  • 9
    ISSN: 1434-4475
    Keywords: 2(2-Hydroxyphenyl)2H-benzotriazole ; Polymerizable stabilizers ; Ultraviolet spectra
    Source: Springer Online Journal Archives 1860-2000
    Topics: Chemistry and Pharmacology
    Description / Table of Contents: Zusammenfassung 2(2,4-Dihydroxyphenyl)2H-benzotriazol wurde mit 50% Ausbeute über die Kondensation vono-Nitrobenzoldiazoniumchlorid mit Resorcin, gefolgt von reduktiver Cyclisierung der ursprünglich erhaltenen Azoverbindung mit Zn/NaOH, erhalten. Die Kondensation des Diazonium-Salzes hatte unter sorgfältig kontrollierten Bedingungen und im sauren Medium zu erfolgen, da ansonsten „Bis“-Kondensation auftrat, die nach der reduktiven Cyclisierung 2(2,4-Dihydroxyphenyl)1,3-2H-dibenzotriazol ergab. 2(2,4-Dihydroxyphenyl)2H-benzotriazol wurde mit Acryoyl- bzw. Methacryloylchlorid zur Reaktion gebracht, wobei die Monoacetylierungsprodukte in über 60% Ausbeute gewonnen wurden. Die beiden Monomeren wurden homopolymerisiert und mit Styrol, Methylmethacrylat undn-Butylacrylat zu Polymeren hohen Molekulargewichts copolymerisiert. Die Inkorporierung von 2[2-Hydroxy-4-acryloxy (bzw. 4-methacryloxy)]2H-benzotriazol in das Copolymer erfolgte zwischen 1 und 10 mol% der Comonomer-Mischung. Die UV-Spektren der Monomeren, Homo- und Copolymeren sind angegeben.
    Notes: Abstract 2(2,4-Dihydroxyphenyl)2H-benzotriazole has been prepared in about 50% yield by condensation ofo-nitrobenzenediazonium chloride with resorcinol followed by reductive cyclization of the initially obtained azo compound with zinc and sodium hydroxide. The condensation of the diazonium salt had to be carried out under carefully controlled conditions and in acidic medium, otherwise “bis”-condensation occurred which, after reductive cyclization, yielded 2(2,4-dihydroxyphenyl)1,3-2H-dibenzotriazole. 2(2,4-Dihydroxyphenyl)2H-benzotriazole was allowed to react with acryloyl or methacryloyl chloride. Monoacylation in the 4-position occurred by interfacial acylation technique and 2[2-hydroxy-4-acryloxy (or 4-methacryloxy)]2H-benzotriazole was obtained in over 60% yield. The two monomers were homopolymerized and copolymerized with styrene, methyl methacrylate, andn-butyl acrylate to polymers of high molecular weight. Incorporation of 2[2-hydroxy-4-acryloxy (or 4-methacryloxy)]2H-benzotriazole into the copolymer was from 1 to 10 mol% of the comonomer mixture. The ultraviolet spectra of monomers, homo- and copolymers were also determined.
    Type of Medium: Electronic Resource
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  • 10
    Electronic Resource
    Electronic Resource
    Springer
    Journal of polymers and the environment 4 (1996), S. 51-53 
    ISSN: 1572-8900
    Keywords: Chromatographic fingerprinting ; degradation products ; stage II product ; catabolism
    Source: Springer Online Journal Archives 1860-2000
    Topics: Chemistry and Pharmacology , Energy, Environment Protection, Nuclear Power Engineering , Mechanical Engineering, Materials Science, Production Engineering, Mining and Metallurgy, Traffic Engineering, Precision Mechanics
    Notes: Abstract The degradation products of polymers are identifiable by chromatography. The degradation product patterns (or “fingerprints”) formed depend on the type of polymer, the degradation mechanism(s), and also the type of additive present in the material. The chromatographic fingerprint of biotically aged degradable low-density polyethylene (i.e., LDPE+starch+prooxidant) shows, in particular, the absence of low molecular weight carboxylic acids, which suggests an assimilation of these carboxylic acids by the microorganisms. The degradation products of natural polymers are usually intermediates that are used again in the anabolic cycles. It is possible to transfer the terminology from the natural polymers, where the catabolism of natural polymers consists of three stages, and apply this also to the degradable synthetic polymers. During stage I the natural polymers degrade to their major building blocks (e.g., amino acids, glycerol, hexoses, pentoses, etc.), during stage II these products are collected and converted to a smaller number of even simpler molecules [e.g., acetyl-coenzyme A (CoA)]. In stage III, finally, the acetyl-CoA enters the citric acid cycle, where energy is gained in parallel with the release of CO2 and H2O.
    Type of Medium: Electronic Resource
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