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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 />

Result:<br />

Test condition:<br />

In this study, 27 commercial inorganic and organic chemicals<br />

were tested simultaneously in seven aquatic species.<br />

A LC50 value could not be determined because the proportion<br />

killed at the highest dose level (100 mg/L) was less than<br />

50%. No further details reported.<br />

TEST ORGANISMS: Water flea (Daphnia magna) of first and<br />

second larval instar. The test organisms were acclimated to<br />

the control diluent water in the breeding/rearing tanks<br />

(time period not reported). Food was withheld for the 24<br />

hours preceding start of the test. Juveniles as uniform in<br />

size as possible were collected from the colonies. Ten<br />

juvenile organisms were exposed to the test chemical in each<br />

treatment. Biological loading was kept below 0.5 gram wet<br />

weight per liter of test solution.<br />

TEST VESSEL: The assay was performed in seamless glass,<br />

30.5-cm cuboidal, Pyrex chromatographic jars to which <strong>20</strong><br />

liters of test solution was added. The test organisms were<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 the<br />

test 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 />

96<br />

UNEP PUBLICATIONS

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