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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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