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 />
5.1.3 Acute Dermal Toxicity<br />
Type:<br />
Species:<br />
Strain:<br />
Sex:<br />
Vehicle:<br />
Doses:<br />
Value:<br />
Method:<br />
GLP:<br />
Test substance:<br />
Remark:<br />
Result:<br />
LD50<br />
rat<br />
Wistar<br />
male/female<br />
other: water-acetone solution (no further detail reported)<br />
<strong>20</strong>00 mg/kg bw (limit test)<br />
> <strong>20</strong>00 mg/kg bw<br />
other: see Test Condition<br />
no data<br />
other TS: ammonium sulphate, commercial grade<br />
The study was undertaken to validate a screening test for<br />
the assessment of the acute dermal toxicity with a view to<br />
minimizing the use of animals in the acute toxicity testing.<br />
Two laboratories cooperated in this study.<br />
Approximative LD50 in males:<br />
in laboratory A > <strong>20</strong>00 mg/kg bw,<br />
in laboratory B > <strong>20</strong>00 mg/kg bw.<br />
Approximative LD50 in females:<br />
in laboratory A > <strong>20</strong>00 mg/kg bw,<br />
in laboratory B > <strong>20</strong>00 mg/kg bw.<br />
Test condition:<br />
Clinical signs, necropsy findings: not reported.<br />
Male and female Wistar rats of 5-6 weeks of age were treated<br />
with the test substance after at least 5 days of adaptation.<br />
Hair was first removed from an area of 3x4 cm2 on the back<br />
with an electric hair clipper, and then the test substances<br />
dissolved in acetone and water were applied in a single dose<br />
to the skin surface of the clipped backs of the animals. The<br />
application sites were not covered but the treated areas<br />
were prevented from being licked by using a plastic collar<br />
or by fixing the animals on a plastic plate, and all animals<br />
were individually housed in stainless-steel cages.<br />
Observation of animals, including body weight changes,<br />
mortality, gross lesion and behavioural and clinical<br />
abnormality, were performed for 14 days after exposure, and<br />
necropsy was carried out at the end of the test.<br />
The experiments were performed simultaneously in two<br />
different laboratories.<br />
Three male and three female rats were each given a dose of<br />
<strong>20</strong>00 mg/kg bw. If none of the animals died, further toxicity<br />
tests were not performed and the chemical was regarded as<br />
having an LD50 of greater than <strong>20</strong>00 mg/kg bw. If some of the<br />
animals died, a step 2 test was performed at the level of<br />
<strong>20</strong>0 mg/kg bw. If all animals survived in the step 2 test,<br />
the chemical was considered to have an LD50 greater than <strong>20</strong>0<br />
mg/kg bw. When some of the animals died, the step 3 test<br />
with <strong>20</strong> mg/kg bw was performed. If all the animals died at<br />
this dose level, it meant that he chemical had an LD50 of<br />
less than <strong>20</strong> mg/kg bw. If one or two animals died at the<br />
fixed dose level, the chemical was regarded as having an<br />
LD50 near that dose level, and the approximate LD50 of the<br />
chemical was indicated as ca. <strong>20</strong>, <strong>20</strong>0 or <strong>20</strong>00 mg/kg bw.<br />
Year of study: not reported.<br />
UNEP PUBLICATIONS 157