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2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures

2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures

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Chem. Listy, 102, s265–s1311 (2008) Environmental Chemistry & Technology<br />

P09 VOLATILE DEGRADATION PRODuCTS OF<br />

POLyuREThANE FOAMS<br />

DAnIELA MáCOVá, TEREZA TOBIáŠOVá and JOSEF<br />

ČáSLAVSKý<br />

Institute of Chemistry and Technology of Environmental Protection,<br />

Faculty of Chemistry, Brno University of Technology,<br />

Purkyňova 118, 612 00 Brno, Czech Republic,<br />

xcmacova@fch.vutbr.cz<br />

Introduction<br />

Polyurethanes are the world’s sixth most abundant synthetic<br />

polymer. The most of their production represent flexible<br />

polyurethane foams. At the end of their life-cycle they are<br />

often deposited on waste dumps, where they degrade under<br />

the influence of various environmental factors; photodegradation<br />

and hydrolysis are the main routes. After that, their<br />

degradation products can be distributed in the environment.<br />

In common, synthetic polymers are not prone to environmental<br />

degradation. Therefore, they could stay there for a long<br />

time. Their degradability can be improved by addition of the<br />

biodegradable filler.<br />

The generation of volatile products has been reported<br />

from the photo- and thermal degradation of many polymers.<br />

1–4 Complex mixtures of degradation products of this<br />

type were for example identified in starch-based polymers 5 .<br />

Till now, there is no information about volatile compounds<br />

generated during photodegradation of synthetic polyurethane<br />

with biodegradable filler. Several studies have been developed<br />

on the UV degradation of aromatic polyurethane. Such<br />

photo-degradation has already exhibited formation of free<br />

radicals, recombination, scission of bonds, crosslinking and<br />

oxidation reactions 6,7 .<br />

This paper is focused on the identification of volatile<br />

photodegradation product of polyurethanes modified<br />

by biodegradable filler using Solid Phase Microextraction<br />

(SPME) and Gas Chromatography linked to Mass Spectrometry.<br />

The SPME method was selected in the experiment for<br />

its fastness, simplicity and environmental friendness.<br />

Experimental<br />

M a t e r i a l a n d S a m p l i n g<br />

Polyurethane foam modified with biodegradable filler<br />

like carboxymethyl cellulose, acetylated potato starch, cellulose<br />

acetate, 2-hydroxyethyl cellulose and wheat protein<br />

were prepared at the Institute of Material Chemistry at Faculty<br />

of Chemistry, Brno University of Technology.<br />

For sampling of volatile compounds the system consisting<br />

of quartz tube with Teflon cover and two SPME holders,<br />

the first with polyacrylic fibre (PA) 85 µm and the second with<br />

polydimethylsiloxane fibre (PDMS) 100 µm (both Supelco,<br />

USA) and UV lamp (high-pressure mercury discharge tube,<br />

λ = 254 nm), was set-up. The system is shown on Fig. 1.<br />

s351<br />

Fig. 1. System for sampling of VOCs formed by photodegradation<br />

of polymer<br />

G C - M S a n a l y s i s<br />

Separation and identification of volatile compouds from<br />

UV-induced polyurethane foam photodegradation was realized<br />

using Agilent 6890n gas chromatograph coupled with<br />

Agilent 5973 mass selective detector (Agilent Technologies,<br />

Germany). HP-5MS column 30.0 m × 0.25 mm × 0.25 μm<br />

was used for the separations. The injector and transfer line<br />

temperature was 270 °C. The GC oven temperature program<br />

for PDMS fibre was: 4 min at 40 °C, then increased<br />

at 15 °C min –1 to 100 °C, then 8 °C min –1 to 270 °C, then<br />

15 °C min –1 to 280 °C. For the compounds desorbed from<br />

PA fibre the column temperature program was slightly modified:<br />

4 min at 40 °C, increased at 10 °C min –1 to 230 °C, then<br />

15 °C min –1 to 280 °C. Injection/desorption of analytes from<br />

SPME fibres was realized in splitless mode. Helium was used<br />

as the carrier gas at a constant flow of 1 ml min –1 . Ion source<br />

temperature was 230 °C, electron ionization at 70 eV was<br />

used. Quadrupole analyzer of the MSD was operated in scan<br />

mode within a range 30–550 amu, solvent delay was 4 min.<br />

Identification of separated compounds was based on nIST 05<br />

spectral library search.<br />

Results<br />

Seven types of polyurethane foams with different fillers<br />

and reference foam without filler were irradiated by UV lamp<br />

during this study. Volatile compounds were sorbed on PA and<br />

PDMS fibers and desorbed, separated and detected by GC-<br />

MS technique.<br />

All identified compound are listed under chromatograms<br />

(Figs. <strong>2.</strong> and 3.). Many various compounds have been<br />

identified.<br />

Group of branched and non-branched aliphatic hydrocarbons<br />

containded: pentadecane, hexadecane, heptadecane,<br />

2,6,10,14-tetramethylpentadecane, 2,6,10,15,19,23-hexamethyl-2,6,10,14,18,22-tetracosahexaene<br />

(Squalene). These<br />

compounds are probably formed by homolysis of bonds in<br />

soft part of polyurethane.<br />

Group of ketone and fatty acid esters contained: 6,10dimethyl-5,9-undecadiene-2-one,<br />

methylester of dodecanoic<br />

acid and isopropylester of tetradecanoic acid.<br />

By photo-oxidation of alkenes hydroperoxides were<br />

formed – 1,3-dioxane and 2-methyl 1,3-dioxane.

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