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 />
4. ECOTOXICITY ID: <strong>7783</strong>-<strong>20</strong>-2<br />
DATE: 18.04.<strong>20</strong>06<br />
Result:<br />
96-h LC50 (September 1977): 210 mg/L,<br />
96-h LC50 (December 1977): <strong>20</strong>0 mg/L<br />
96-h LC50 (June 1978):130 mg/L<br />
Test condition: The fish were caught in the estuary of the River Crouch by<br />
the Laboratory`s research vessel using a modified 2 m beam<br />
trawl with 10 mm mesh in the cod end. On arrival in the<br />
laboratory the animals were tranferred to polyethylene stock<br />
tanks at a maximum density of 100 fish per tank.<br />
Water at the test emperature of 15 °C was used to slowly<br />
fill the tanks and any dead or injured animals were removed.<br />
The animals were maintained in well aerated, gently flowing<br />
sea water for 2-4 days before the start of the test. They<br />
were not fed during their period in the laboratory, which<br />
never exceeded 9 days.<br />
Test tanks were filled with 10 L of sea water and aerated<br />
for at least 1 hour. Ten fish of 50-100 mm total length<br />
(about 2-8 g) were then randomly added to each tank.<br />
Diseased animals were excluded. A further acclimatisation<br />
period of 2 hour was allowed before the test solutions were<br />
added.<br />
Test solutionswere made up by gently stirring a measured<br />
amount of the well mixed test substance into the sea water<br />
in the test tanks.<br />
Ammonium sulfate was added to the test tanks as 10% w/v<br />
solution in distilled water. Four concentrations were set up<br />
initially, with controls of clean sea water. Duplicates were<br />
used at each concentration.<br />
The concentrations chosen started at 10,000 uL/L (1%) and<br />
decreased at half-logarithmic intervals (ie 3300, 1000 and<br />
330 uL/L).<br />
Test solutions were renewed daily to discard metabolites and<br />
counteract losses of the test substance due to absorption by<br />
the test organisms, degradation or volatilization.<br />
The dissolved oxygen concentration in each test tank was<br />
measured and recorded daily. If the dissolved oxygen<br />
concentration in any of the test tanks dropped below 70% air<br />
saturation value then the test was repeated with additional<br />
aeration.<br />
The pH of the test solution was measured and recorded 1 and<br />
24 hours after the start of the test, but is not reported in<br />
the paper. The intended pH range was between pH 6 and pH 8.<br />
Each test continued for 96 hours.<br />
The tanks were inspected at frequent intervals, including<br />
24, 48, 72 and 96 hours after adding the test solution, and<br />
dead animals (defined as those not responding to gentle<br />
prodding) were recorded and removed. At the time of each<br />
observation and for each tank the cumulative percentage<br />
mortality was calculated. The time for 50% lethality (LT50)<br />
and the LC50s were determined. 95% confidence limits on the<br />
LT50 were calculated according to the method of Litchfield<br />
(1949).<br />
The three tests with ammonium sulfate were carried out in<br />
September and December 1977, June 1978.<br />
Reliability: (2) valid with restrictions<br />
limited documentation, nominal concentrations; pH not given.<br />
Flag:<br />
Critical study for SIDS endpoint<br />
26-JAN-<strong>20</strong>04 (60)<br />
Type:<br />
static<br />
86<br />
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