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 />
Reliability:<br />
SITE DESCRIPTION The rice fields are located in the Eastern<br />
Iberian Peninsula, surrounding the coastal lagoon of "La<br />
Albufera" near Valencia, Spain. A detailed description of<br />
the site and of the rice crop cycle is given in the<br />
following references:1) Quesada A, Sánchez Maeso E, and<br />
Fernández Valiente E, 1995. New incubation device for in<br />
situ measurement of acetylene-reducing activity in<br />
ricefields. J. Appl. Phycol. 1, 195-<strong>20</strong>0.2) Quesada A,<br />
Sánchez Maeso E, and Fernández Valiente E, 1995. Seasonal<br />
variation of chemical properties of rice field soils from<br />
Valencia, Spain. Commun. Soil Sci. Plant Anal . 26,<br />
1-19.The text mentions the alkaline condition of soils and<br />
sediments.The field trials were conducted in three<br />
consecutive crop seasons, using plots of 5m x <strong>20</strong>m size,<br />
laterally isolated by plastic sheets embedded into the soil<br />
at a depth of 10cm. Ammonium sulfate was applied at 0,<br />
17.5, 35, 70, and 140 kg N ha-1. A basal dose of 100 kg/ha<br />
P2O5 was supplied, as superphosphate, to all plots. A<br />
randomised complete block design with four replicates was<br />
employed. Basal P and N doses were applied as a single<br />
broadcast application and covered by about 3 cm soil, 1-2<br />
days before flooding. After the initial flood, around mid<br />
May, plots were hand sown at 180 kg/ha seed (rice variety<br />
Senia), pre-soaked in tapwater. Grain and straw yield and N<br />
content in plants were determined at maturity.Soil<br />
cyanobacterial population was measured from cores collected<br />
from each plot, at 4-5 weekly intervals throughout the<br />
growth cycle. Four in situ measurements of nitrogenase<br />
activity were made in May, June, July, and September of each<br />
year.<br />
(2) valid with restrictions<br />
incomplete documentation of soil and of treatment regime<br />
Flag:<br />
Critical study for SIDS endpoint<br />
11-MAY-<strong>20</strong>03 (84)<br />
Type:<br />
Species:<br />
Unit:<br />
Method:<br />
GLP:<br />
Test substance:<br />
Remark:<br />
Result:<br />
Test condition:<br />
122<br />
field<br />
other bacteria: nitrogen-fixing legume bacteria and<br />
nitrogen-fixing blue green algae<br />
Analytical monitoring: yes<br />
other: see Test Condition<br />
no data<br />
other TS: ammonium sulfate as fertiliser, no further details<br />
The result is attributed to the low pH (4.4) of the soil,<br />
which results from ammonium sulfate addition. Toxic metal<br />
ions (e.g. Al) released from soil at acid pH may contribute<br />
to the effect. Soil pH can be increased by liming.<br />
Biological nitrogen-fixing activity was reduced<br />
(nitrogen-fixing legume bacteria) or eliminated<br />
(nitrogen-fixing blue green algae) in soil fertilised with<br />
ammonium sulfate.<br />
exposure period: more than 30 years; 80 kg N/ha applied<br />
annually.<br />
The test site is located 60 degrees N, 17degrees E, near<br />
Uppsala in Central Sweden. The soil is post glacial clay<br />
(35% clay, 35% silt, 21% fine sand). Several organic and<br />
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