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Appendix D - Dossier (PDF) - Tera

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date: 20–JUL–2005<br />

3. Environmental Fate and Pathways Substance ID: 71–43–2<br />

______________________________________________________________________________<br />

3. Pyruvic acid and biacetyl reacted only in presence of<br />

nitrogen oxides under influence of sunlight to produce<br />

peroxyacetylnitrate: in one run, from 0.72 ppm carbonyl<br />

(pyruvic acid), in 4 hours, a maximum concentration of 35<br />

ppb of peroxyacetylnitrate was formed.<br />

The methyl group of cresol appears not to be involved in the<br />

photochemical oxidation, so the reaction mechanism in terms<br />

of substitution with hydroxyl and nitro groups may also be<br />

valid for the degradation of benzene.<br />

Source: German Rapporteur<br />

Test condition: 1. Smog chamber containing ozone–free air were filled with<br />

nitrogen oxides and cresol diluted with nitrogen and exposed<br />

to sunlight in outdoor experiments for 3 – 5,5 hours.<br />

2. Ozone, o–cresol, and nitrogen dioxide were injected into<br />

the chamber protected against sun light and containing,<br />

ozone–free purified air for 2 – 4 hours. Control experiments<br />

with cresol in purified air alone or nitrogen oxides and<br />

ozone alone in air were also performed.<br />

3. Pyruvic acid and biacetyl alone in pure air (< 14 ppm<br />

nitrogen oxides) in the dark or in sunlight and a mixture of<br />

pyruvic acid or biacetyl with nitrogen oxides in sunlight<br />

were allowed to react for 2 to 5 hours to produce<br />

peroxyacetylnitrate.<br />

Test substance: No data<br />

Flag: Risk Assessment<br />

16–MAR–2004 (449)<br />

Memo: Ring–fission products of o–cresol as primary oxidation product<br />

of toluene in analogy to benzene.<br />

Method: Smog chamber experiments: sunlight irradiation on a 4 or 60<br />

cu m chamber covered with Teflon film.<br />

Remark: Used for Risk Assessment.<br />

Result: In an experiment with a 60 cu m chamber running for 5.5<br />

hours containing initial concentrations of 0.36 ppm nitrogen<br />

monoxide, 0.30 ppm nitrogen dioxide and 0.70 ppm o–cresol,<br />

the following products were observed: 156 ppm ozone (after<br />

5.5 hours), 7 ppb peroxyacetylnitrate, formaldehyde (31 ppb<br />

after 2 h, 47 ppb after 4 h), acetaldehyde (17 ppb after 2<br />

h, 15 ppb after 4 h), pyruvic acid (not quantified), and<br />

particulate matter (460 µg/m**3) consisting of<br />

hydroxynitrotoluenes, hydroxydinitotoluenes, and<br />

dihydroxynitrotoluenes.<br />

The methyl group of cresol appears not to be involved in the<br />

photochemical oxidation, so the reaction mechanism in terms<br />

of substitution with hydroxyl and nitro groups may also be<br />

valid for the degradation of benzene.<br />

Source: German Rapporteur<br />

Test condition: Smog chamber containing ozone–free air were filled with<br />

nitrogen oxides and cresol diluted with nitrogen and exposed<br />

to sunlight in outdoor experiments for 3 – 6 hours.<br />

Test substance: No data<br />

Flag: Risk Assessment<br />

16–OCT–2002 (448)<br />

<strong>Appendix</strong> D: Benzene SIDS <strong>Dossier</strong><br />

– 233/957 –

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