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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 />

Remark:<br />

EC50(96h) = 380 mg/L (September 1977), 600 mg/L (December<br />

1977), 480 mg/L (June 1978), 400 mg/L (September 1978), 540<br />

mg/L (March 1979)<br />

Test condition: The animals were caught in the estuary of the River Crouch<br />

by the Laboratory`s research vessel using a modified 2 m<br />

beam 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 <strong>20</strong>0 shrimps 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. <strong>20</strong> shrimps of 40-70 mm (about 1-3 g)<br />

were then randomly added to each tank. Diseased animals were<br />

excluded. A further acclimatisation period of 2 hours was<br />

allowed before the test solutions were 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 given in<br />

the paper. The intended pH range was between 6 and 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 and September 1978, and<br />

March 1979.<br />

Reliability: (2) valid with restrictions<br />

Limited documentation, no analytical monitoring; pH not<br />

reported.<br />

Flag:<br />

Critical study for SIDS endpoint<br />

02-FEB-<strong>20</strong>04 (60)<br />

UNEP PUBLICATIONS 101

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