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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 />

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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