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 />
segregated in welded stainless steel, 55-mesh wirecloth<br />
baskets (5.5 cm in diameter x 7.5 cm in depth). Each basket<br />
was suspended from a 1-rpm motor-driven mechanism that<br />
raised and lowered the baskets in the water column. A<br />
stainless steel band, slotted every 0.5 cm, facilitated the<br />
positioning of the baskets so that the submerged volumes<br />
changed from one-third to wo-thirds during each cycle.<br />
One-half of the volume of the sumerged basket was exchanged<br />
with the main tank volume every minute.<br />
TEST SOLUTION: The test chemical was added directly to the<br />
diluent water to give a nominal concentration of 100 mg/L.<br />
The test chemical concentrations were not analyzed. Once<br />
thetest solutions were prepared, the starting temperature,<br />
dissolved oxygen and pH values were determined for each<br />
exposure concentration. When the starting pH of the test<br />
soluton fell outside the extremes of 6.5 to 8.5, the pH was<br />
adjusted to 7.0 by the addition of 10% (v/v) NaOH or 10%<br />
(v/v) H2SO4.<br />
DILUTION WATER: Water quality was routinely monitored to<br />
characterize the diluent water and ensure its suitability<br />
according to the standard method for the examination of<br />
water and wastewater, 16th ed., American Public Health<br />
Association, Washington DC pp. 689-832. The chemical<br />
characteristics are reported in the publication and are in<br />
accordance with standards required by current testing<br />
guidelines. Activated carbon-filtered, dechlorinated and<br />
tempered industrial service water from Lake Ontario was used<br />
in all tests.<br />
PHYSICAL/CHEMICAL PARAMETERS:<br />
Determination of the temperature, dissolved oxygen and pH of<br />
each test solution were made in conjunction with the daily<br />
biological observation. The test temperature target was <strong>20</strong> +/-<br />
1 °C. If the dissolved oxygen concentration in a test chamber<br />
fell below 40% of the starting level in a test, the test was<br />
repeated with 0.05 L/min glass-sparger aeration All tests were<br />
conducted within the extremes of 6.5 to 8.5 pH units. The<br />
photoperiod duration was 16 h of light. The air-water<br />
interface of each tank received approximately 50 ft-c of<br />
cool-white fluorescent light.<br />
BIOLOGICAL PARAMETERS: biological observations were made<br />
daily. Survival, condition and behavioural information were<br />
recorded. Dead organism were removed when observed. If more<br />
than one-half of the population exposed in any treatment was<br />
found to be dead, additional aquaria containing lower<br />
concentrations of test soution were set up.<br />
EXPOSURE PERIOD: 96 hours.<br />
TEST CONCENTRATION: 100, 10, 1 and 0.1 mg/l<br />
STATISTICAL METHOD: The 96-h LC50 value was derived using an<br />
interpolation method as described by Stephan (Stephan CE:<br />
Methods for calculating an LC50: Aquatic toxicology and<br />
hazard evaluation. In: FL Mayer and JL Hamelink, eds., STP<br />
634. American Society for Testing and Materials,<br />
Philadelphia, PA, pp. 65-84). The linear interpolation uses<br />
98<br />
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