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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 />

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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