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 />
limited documentation<br />
Flag:<br />
Critical study for SIDS endpoint<br />
26-JAN-<strong>20</strong>04 (57) (58)<br />
Type:<br />
flow through<br />
Species:<br />
other: Sciaenops ocellatus (Red Drum, a warmwater marine<br />
fish), early life stage test<br />
Exposure period: 10 day(s)<br />
Unit:<br />
Analytical monitoring: yes<br />
LC50: = 27<br />
Limit Test: no<br />
Method:<br />
GLP:<br />
Test substance:<br />
other: see Test Condition<br />
no data<br />
other TS: ammonium sulfate, no further details<br />
Remark:<br />
1. Nominal concentrations of ammonium sulfate were used as<br />
the source of ammonium and ammonia in the experiments. The<br />
results reported as ammonia concentrations have been<br />
calculated from the total ammoniacal N using the formulas of<br />
Whitfield as modified by Bower and Bidwell (1979). (See:<br />
C.E. Bower and J.P. Bidwell (1979). Ionization of ammonia in<br />
seawater: effects of temperature, pH, and salinity. Journal<br />
of the Fisheries Research Board of Canada 35, 1012-1016.)<br />
The LC50 value reported here has been back-converted, using<br />
linearly extrapolated conversion ratios derived from the<br />
nearest available tabulated entries for total ammoniacal<br />
nitrogen and ammonia, and not from a back conversion using<br />
the equations of Bower and Bidwell. The error caused by this<br />
procedure is less than 4%.<br />
2. Once lethal concentrations were established for eggs and<br />
first-feeding larvae, three week old postlarvae were<br />
evaluated for 1 week for changes in ammonia toxicity with<br />
age and development. Post larvae were less sensitive than<br />
newly hatched larvae. Whereas a concentration of 7.7 mg N<br />
L-1 (calculated 0.55 mg/L ammonia) killed all newly hatched<br />
larvae within 1 week, a slightly higher exposure was<br />
tolerated by 3 week old fish.<br />
Result: The 96 hour LC50 (95% confidence limits) was 5.6 (4.2 - 7.4)<br />
mg/L total N (approximately converted from 0.39 (0.29 -<br />
0.53) mg ammonia per litre, as calculated by the method of<br />
Bower and Bidwell.)<br />
Test condition: TEST ORGANISMS: Eggs were obtained from laboratory spawnings<br />
induced by manipulations of photoperiod and temperature<br />
cycles. Fertilised red drum eggs were exposed to controlled<br />
concentrations of ammonium sulfate in static tests that were<br />
maintained for up to 14 days. Culture methods are described<br />
in Holt et al (1981). (Holt, J., Godbout, R., and C. R.<br />
Arnold (1991) Effects of temperature and salinity on egg<br />
hatching and larval survival of red drum Sciaenops<br />
ocellatus. United States National Marine Fisheries Service<br />
Fishery Bulletin 79, 569-573.)<br />
TEST VESSEL: The test was a static test.PHYSICAL/CHEMICAL<br />
PARAMETERS: The pH of the seawater used varied from 8.0 to<br />
8.2. Salinity varied from 2.8 to 3.2%. Background<br />
concentrations of un-ionized ammonia were 0.001-0.018 mg/L.<br />
deg C temperature was maintained at either 25 or 26 deg C<br />
+/- 0.5 0C. Dissolved oxygen varied from 5.4 to 6.4 mg/L.<br />
TEST CONDITION: Three replicates of each concentration and<br />
UNEP PUBLICATIONS 83