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m-Cresol - ipcs inchem

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OECD SIDS<br />

m- / p-CRESOL<br />

drowsiness, cramps, coma and death (Bruce et al. 1976, Cote et al. 1984, Minami et al. 1990,<br />

DECOS 1998).<br />

Skin contact has also resulted in effects on the nervous system, liver and kidneys, and caused<br />

human fatalities (DECOS 1998). A cresol solution, unintentionally poured over the trunk, caused<br />

gross haematuria, gastrointestinal bleeding, hypertension and septic shock with severe jaundice and<br />

renal failure (Lin and Yang 1992).<br />

Accidental dermal exposure of both legs and face of a 47 old man to m-cresol resulted in corrosion<br />

of 15 % of his body surface and he developed acute polyuric renal failure (Evers et al. 1994).<br />

Skin depigmentation (chemical leukoderma) has been reported after local exposure to cresols (NTP<br />

1991).<br />

No data on systemic effects following acute and short-term occupational exposure to cresol vapours<br />

or aerosol were located (DECOS 1998). 7 workers who were exposed to unknown concentrations of<br />

cresol vapour for 1½ to 3 years, suffered from frequent headaches, nausea and vomiting. Four of the<br />

workers had high blood pressure, impaired renal function, abnormal blood calcium levels an<br />

marked tremor (DECOS 1998).<br />

No epidemiological studies or case reports on occupationally exposure to cresols were found<br />

containing adequate details on exposure levels. Anomalous menstrual cycles and hormonal<br />

disorders were reported for women who were employed in the production of enamelled wire or of<br />

tricresyl phosphate and were exposed in the process to a variety of compounds, including<br />

chlorobenzenes and phosphoryl chloride. It was claimed that the incidence of perinatal child death<br />

was increased and that developmental disorders were frequent among the new-born babies. Since no<br />

data on exposure levels and duration of exposure are given, and data on controls were not provided,<br />

a relationship between the described effects and cresol exposure cannot be deduced (DECOS 1998).<br />

The human lethal dose (LD) is reported to be 50 - 500 mg/kg bw (Gleason et al. 1969).<br />

The development of tumours in persons who had been exposed occupationally to cresol<br />

(unspecified isomer) has been reported, and two cases of transitional cell bladder carcinoma were<br />

described after long-term exposure to cresol (Garrett 1975). Another case involved a worker in an<br />

oil refinery who was exposed to cresol, dichlorooctane and chromic acid for a long period and who<br />

developed a squamous epithelial carcinoma of the vocal cords (DECOS 1998). Since no<br />

information on exposure levels are available, and since co-exposure to other substances cannot be<br />

excluded, a carcinogenic potential of the cresol isomers cannot be deduced from these case reports<br />

(DECOS 1998).<br />

According to the results of studies in cancer patients, endogenous p-<strong>Cresol</strong> does not contribute<br />

significantly to the development of human bladder cancer (32 patients vs 32 age/sex-matched<br />

controls, Renwick 1988) or large bowl cancer (18 patients versus 10 normal healthy persons, Bone<br />

et al. 1976).<br />

Conclusion:<br />

In humans, the accidental oral uptake of cresols can induce irritation of mouth and throat,<br />

abdominal pains, vomiting, haemolytic anemia, increased heart rate, liver and kidney damage,<br />

headaches, facial paralysis, drowsiness, cramps, coma and death. Skin contact with cresols can<br />

result in corrosion, skin depigmentation, effects on the nervous system, liver and kidneys,<br />

gastrointestinal bleeding, and can cause human fatalities. There are some case reports about tumor<br />

development in connection with probable exposure against cresol isomers. Since co-exposures to<br />

other substances cannot be excluded, no conclusion on a carcinogenic potential can be deduced<br />

from these case reports.<br />

UNEP PUBLICATIONS 33

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