Identification of Unsaturated and 2H Polyfluorocarboxylate Homologous Series and Their Detection in Environmental Samples and as Polymer Degradation Products

2015 ◽  
Vol 49 (22) ◽  
pp. 13256-13263 ◽  
Author(s):  
John W. Washington ◽  
Thomas M. Jenkins ◽  
Eric J. Weber
1995 ◽  
Vol 78 (5) ◽  
pp. 1317-1321 ◽  
Author(s):  
Daniel Sharron ◽  
Kamal Swami ◽  
Robert L Jansing

Abstract A simplified purge-and-trap technique for detecting subnanogram amounts of the biocide tributyltin (TBT) and its degradation products dibutyltin (DBT) and monobutyltin (MBT) in aqueous environmental samples is described. Butyltin chlorides present in the sample were derivatized to volatile butyltin hydrides with NaBH4 and simultaneously purged by drawing ambient air through the purge vessel. Butyltin hydrides were trapped on a Porapak-N cartridge, eluted with dichloromethane, and analyzed by gas chromatography with flame photometric detection. Recoveries of the butyltin species ranged from 46 to 101%. Method detection limits for MBT, DBT, and TBT were 1.28, 0.39, and 0.24 ng/L, respectively. The major advantages of this technique are sensitivity, reduced analysis time, and a significant reduction in the amount of dichloromethane used. Results from the analysis of various surface water samples collected in New York are presented.


2007 ◽  
Vol 594 (1) ◽  
pp. 128-138 ◽  
Author(s):  
Maria Chiara Pietrogrande ◽  
Mattia Mercuriali ◽  
Luisa Pasti

2008 ◽  
Vol 34 (7) ◽  
pp. 629-632 ◽  
Author(s):  
V. I. Vettegren ◽  
A. V. Savitskiĭ ◽  
I. P. Scherbakov

1991 ◽  
Vol 26 (3) ◽  
pp. 243-360 ◽  
Author(s):  
R. James Maguire

Abstract Non-pesticidal organotin compounds in Canadian commerce are those of monomethyltin, dimethyltin, monobutyltin, dibutyltin, monooctyltin and dioctyltin. A review is presented of the uses, methods of analysis, environmental occurrence and aquatic toxicity of these compounds, which are scheduled for assessment under the Canadian Environmental Protection Act. It is likely that the most important non-pesticidal route of entry of these compounds to the environment will be through leaching of organotin-stabilized poly(vinyl chloride) by water. Monomethyltin and dimethyltin are widespread in the global environment. Monobutyltin and dibutyltin have been found frequently in harbours, marinas and shipping channels in Canada and elsewhere, arising largely as degradation products from the use of the antifouling agent tributyltin which is now regulated in Canada. There are few reports in the literature on the occurrence of butyltin species as a result of non-pesticidal uses or uses of tributyltin other than as an antifouling agent. Monooctyltin and dioctyltin have not been found to date in Canada or elsewhere in environmental samples. Judging from concentrations which have been reported to date, it appears that the mono- and di-methyltin, butyltin and octyltin species pose no threat to aquatic organisms in Canada vis-à-vis acute toxicity. Data on the persistence of these species in aquatic environments are in some cases fragmentary or non-existent, but in general it appears that these species would not be persistent in aquatic environments, with half-lives estimated to be less than a few months at 20°C.


e-Polymers ◽  
2012 ◽  
Vol 12 (1) ◽  
Author(s):  
Daniela Enescu ◽  
Alberto Frache

AbstractIn the present paper the influence of Flamestab® NORTM 116 (abbrev. FNOR), a sterically hindered N-alkoxyamine stabilizer, on the photo-oxidative stability of calcium carbonate reinforced polypropylene (abbrev. CCPP) used for production of plastic collars has been investigated. The samples, prepared by melt compounding, were exposed to artificial accelerated photo-ageing carried out at λ>300 nm and 45 °C in air. FT-IR and UV-VIS analysis revealed that the deterioration of neat CCPP takes place very rapidly in comparison with the composites containing FNOR. Hydroperoxides and various carbonyl species are formed as the main degradation products during the photo-oxidation process. Moreover, the intensity of the absorption bands grows with increasing of UV exposure time indicating that the material suffers a photo-oxidative degradation process. Indeed, addition of only 0.1 wt.-% FNOR did not significantly modify the length of the induction period of neat CCPP, but a strong efficiency was obtained by increasing the amount of FNOR (0.5 wt.-%) which shows an increase of eight times more as compared with neat CCPP. Therefore, it may be supposed that OIT is linked to the level of concentration of the stabilizer. This remarkable increase in composite stability demonstrated by a lengthening of OIT is typical for sterically hindered N-alkoxyamine stabilizers since they are very efficient at scavenging freeradicals formed as the polymer degrades. In other words, these UV stabilizers are converted to nitroxide radicals (see Scheme 1) which readily trap the polymer degradation species to produce alkoxyamines. Then, the formed alkoxyamines do subsequently react with peroxy radicals to regenerate the active nitroxide radical, thereby this process (called Denisov cycle) proceed in a regenerative cycle, thus retarding oxidative polymer degradation. The increase of absorbance in the carbonyl region as a function of irradiation time was used to determinate the photooxidation rate. It was found out that the photooxidation rate measured from the slope of linear part of the curves is significantly decreased for the CCPP/FNOR 0.5 composite compared to neat CCPP. In the light of the above mentioned findings, FNOR could be taken into consideration as an UV stabilizer for CCPP.


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