AMMONIUM SULFATE CAS N°: 7783-20-2
AMMONIUM SULFATE CAS N°: 7783-20-2
AMMONIUM SULFATE CAS N°: 7783-20-2
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OECD SIDS<br />
<strong>AMMONIUM</strong> <strong>SULFATE</strong><br />
5. TOXICITY ID: <strong>7783</strong>-<strong>20</strong>-2<br />
DATE: 18.04.<strong>20</strong>06<br />
weighed between 6 and 14 mg (mean value 9.2 mg). Similar or<br />
higher increases in parathyroid weight were also found with<br />
all other chemicals tested in this study (ammonium<br />
hydroxide, carbonate, chloride, hydrophosphate, acetate,<br />
lactate, calcium chloride, hydrochloric acid, lactic and<br />
acetic acids, sodium ammonium phosphate, and sodium<br />
dihydrogen phosphate). The author considers this effect to<br />
be caused by metabolic acidosis that was induced by the<br />
various chemicals (though no experimental data relating to<br />
the latter were provided in the publication).<br />
Test condition: 10 females were treated with 100-<strong>20</strong>0 mg ammonium sulfate /<br />
kg bw, dissolved in 100-150 cm3 drinking water every second<br />
day. The dose was gradually increased over the experimental<br />
period of 5-16 months (no further details given). Each 4th<br />
week was scheduled as a recovery period without treatment.<br />
Reliability: (4) not assignable<br />
documentation insufficient for assessment<br />
19-JUL-<strong>20</strong>04 (136)<br />
Type:<br />
Sub-chronic<br />
Species: Syrian hamster Sex: male<br />
Route of administration: inhalation<br />
Exposure period:<br />
15 weeks<br />
Frequency of treatment: 6 hours/day, 5 days/week<br />
Doses:<br />
186.6 ug/m3 (analytical) (<strong>20</strong>0 ug/m3 , nominal)<br />
Control Group:<br />
other: BaP<br />
Method:<br />
other: see Test Condition<br />
Year: 1978<br />
GLP:<br />
no<br />
Test substance: other TS: ammonium sulfate, no further specified<br />
Remark:<br />
Result:<br />
The study evaluated the influence of ammonium sulfate as a<br />
cofactor in carcinogenesis studies employing benzo(a)pyrene as<br />
the prime agent. Additional information concerning influence<br />
on a metabolic enzyme (arylhydroxylase) and the body`s<br />
absorption and excretion of sulfate was also included (cf<br />
IUCLID section on toxicokinetics). NOTE: wrong units (mg<br />
instead of ug) were used in some parts of the publication by<br />
Godleski et al., 1984.<br />
Inhaled ammonium sulfate did not increase the incidence or<br />
severity of pneumonitis or pulmonary fibrosis in the hamster.<br />
This inhalation did increase the incidence of emphysema as<br />
examined microscopically but not the severity. The increase in<br />
emphysema incidence was not statistically significant (9.0 vs<br />
15.2%, EPA 1978). Another publication of this study described<br />
an increase in emphysema incidence, which is however of<br />
doubtful statistical significance. It was based on only 80<br />
animals per group (8.6 vs 16.1%, Godleski, 1984). Due to the<br />
higher number of animals used the EPA results are more<br />
reliable and 0.2 mg/ammonium sulfate/m3 cannot be regarded as<br />
a LOAEL. However it seems not acceptable to take 0.2 mg/m3 as<br />
the NOAEL from this study because the animals were not<br />
examined immediately after exposure but only after 2 years.<br />
Test condition: 80 approximately 10-week old animals were exposed for 6<br />
hours/day, 5 days/week for 15 weeks at an average<br />
concentration of 186.6 ug/m3 (nominal concentration <strong>20</strong>0<br />
ug/m3).<br />
After 2 years, histological sections of the respiratory tract<br />
UNEP PUBLICATIONS 179