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Fuel Oils - IARC Monographs on the Evaluation of Carcinogenic ...

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262 <str<strong>on</strong>g>IARC</str<strong>on</strong>g> MONOGRAPHS VOLUME 45<br />

authors c<strong>on</strong>cluded that both exposure to kerosene stoves and cigarette smoking were<br />

str<strong>on</strong>gly associated with lung cancer in women in H<strong>on</strong>g K<strong>on</strong>g.<br />

ln a similar study in which 189 hospitalized women with a histologically c<strong>on</strong>firmed<br />

diagnosis <strong>of</strong> br<strong>on</strong>chial cancer were compared with 189 c<strong>on</strong>trol patients from <strong>the</strong><br />

orthopaedic wards <strong>of</strong> <strong>the</strong> sa me hospital, Chan et al. (1979) observed an odds ratio (estimated<br />

by <strong>the</strong> W orking Group) for use <strong>of</strong> kerosene stoves am<strong>on</strong>g all women <strong>of</strong> 1.6 (95% CI,<br />

0.99-2.6) and am<strong>on</strong>g n<strong>on</strong>smoking women <strong>of</strong> 2.1 (1.1-4.1).<br />

Koo et aL. (1983) c<strong>on</strong>ducted a case-c<strong>on</strong>trol study <strong>of</strong> 200 hospitalized women with lung<br />

cancer and 200 c<strong>on</strong>trol women from <strong>the</strong> general populati<strong>on</strong> matched for age, district <strong>of</strong><br />

residence and type <strong>of</strong> housing. Odds ratios were estimated for different types and levels <strong>of</strong><br />

exposure after c<strong>on</strong>trollng for smoking. Higher risks were observed am<strong>on</strong>g women with<br />

more than 30 years' use <strong>of</strong> kerosene for cooking (age-adjusted odds ratio for n<strong>on</strong>smokers,<br />

1.4; 95% CI, 1.1 - 1.9;p= 0.02; odds ratio for smokers, 2.5; 1.2-5.4;p=0.02). C<strong>on</strong>trols were<br />

more likely to have used liquid petroleum gas-type fueL.<br />

(The W orking Group c<strong>on</strong>sidered that <strong>the</strong> predominant inhalati<strong>on</strong> exposure <strong>of</strong> <strong>the</strong><br />

women in <strong>the</strong>se studies would have been to <strong>the</strong> combusti<strong>on</strong> products <strong>of</strong>kerosene and not to<br />

<strong>the</strong> product itself. ln view <strong>of</strong> a recent study from Shanghai, China (Gao et al., 1987),<br />

exposure to cooking oil may have c<strong>on</strong>tributed to <strong>the</strong> observed effects.)<br />

4.1 Exposure data<br />

4. Summary <strong>of</strong> Data Reported and Evaluati<strong>on</strong>l<br />

<str<strong>on</strong>g>Fuel</str<strong>on</strong>g> oils are complex and variable mixtures <strong>of</strong> alkanes and alkenes, cycloalkanes and<br />

aromatic hydrocarb<strong>on</strong>s, c<strong>on</strong>taining low percentages <strong>of</strong> sulfur, nitrogen and oxygen<br />

compounds. Kerosene fuel oils are manufactured from straight-run petroleum distilates<br />

from <strong>the</strong> boiling range <strong>of</strong> kerosene (5). O<strong>the</strong>r distilate fuel oils c<strong>on</strong>tain straight-run middle<br />

distillate (6), <strong>of</strong>ten blended with straight-run gas oil (7) and light vacuum distilates (19), and<br />

light cracked distilates (24, 30). The main comp<strong>on</strong>ents <strong>of</strong> residual fuel oils are <strong>the</strong> heavy<br />

residues from distillati<strong>on</strong> and cracking operati<strong>on</strong>s (8,21,31); various refinery by-products<br />

and heavy distilates (20,26,27) may be added. ln fuel oils c<strong>on</strong>sisting mainly <strong>of</strong> atmospheric<br />

distilates, <strong>the</strong> c<strong>on</strong>tent <strong>of</strong> three- to seven-ring polycyclic aromatic hydrocarb<strong>on</strong>s is generally<br />

less than 5%. ln fuel otls that c<strong>on</strong>tain high proporti<strong>on</strong>s <strong>of</strong> heavy atmospheric, vacuum and<br />

cracked distilates or atmospheric and vacuum residues, <strong>the</strong> c<strong>on</strong>tent <strong>of</strong> three- to seven-ring<br />

polycyclic aromatic hydrocarb<strong>on</strong>s may be as high as 10%; if large quantities <strong>of</strong> cracked<br />

comp<strong>on</strong>ents are incorporated, levels may approach 20%. <str<strong>on</strong>g>Fuel</str<strong>on</strong>g> oils are used mainly in<br />

industrial and domestic heating, as well as in <strong>the</strong> producti<strong>on</strong> <strong>of</strong> steam and electricity in<br />

power plants. Skin and inhalati<strong>on</strong> exposures to fuel oil may occur during its producti<strong>on</strong>,<br />

storage, distributi<strong>on</strong> and use and during maintenance <strong>of</strong> heating equipment. During <strong>the</strong><br />

cleaning <strong>of</strong> fuel oil tanks, high, short-term exposures to total hydrocarb<strong>on</strong> vapours have<br />

been measured at levels ranging from 100-1600 mg/m3.<br />

IThe numbers in square brackets are those assigned to <strong>the</strong> major process streams <strong>of</strong> petroleum refining in Table 2 <strong>of</strong> <strong>the</strong> m<strong>on</strong>ograph<br />

<strong>on</strong> occupati<strong>on</strong>al exposures in petroleum refining (p. 44).

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