28.01.2014 Views

AMMONIUM SULFATE CAS N°: 7783-20-2

AMMONIUM SULFATE CAS N°: 7783-20-2

AMMONIUM SULFATE CAS N°: 7783-20-2

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

OECD SIDS<br />

<strong>AMMONIUM</strong> <strong>SULFATE</strong><br />

3. ENVIRONMENTAL FATE AND PATHWAYS ID: <strong>7783</strong>-<strong>20</strong>-2<br />

DATE: 18.04.<strong>20</strong>06<br />

pelletized 15N labelled ammonium sulfate fertiliser to the<br />

West Bear Brook catchment, from June 1991 until December 1992<br />

(1991: 21 kg N/ha, 1992: 42 kg/ha). This was part of an<br />

experiment involving otherwise unlabelled ammonium sulfate<br />

fertiliser application at the same level, which has run from<br />

1989 to 1996. The nearby East Bear Brook catchment, with no<br />

fertiliser application, was used as a control.<br />

Remark:<br />

Further information on soil characterisation may be<br />

available in Norton et al (1999), in Environmental<br />

Monitoring and Assessment 55 (page not given).<br />

Result:<br />

Analysis of stream water established that the 1.5 year<br />

(1991-1993) cumulative exports of fertiliser-derived<br />

ammonium represented less than 1% of the labelled fertiliser<br />

added to the catchment. Nitrate plus ammonium exports<br />

contained ca. 2 kg N/ha of the 42 N kg/ha<br />

deposited.<br />

Test substance: Commercial pelletised ammonium sulfate fertiliser, enriched<br />

in 15N at the Tenessee Valley Authority laboratory by<br />

dissolution of the pellets in water, addition of (15NH4)2SO4<br />

into the fertiliser solution, and repelletizing the<br />

precipitated, labelled fertiliser.<br />

Reliability: (1) valid without restriction<br />

study well documented and assignable<br />

28-MAY-<strong>20</strong>04 (41)<br />

Type of measurement: other<br />

Media:<br />

soil<br />

Result: In two soils treated with ammonium sulfate at rates of 0,<br />

25, 50, 100 and 150 mg N/kg ammonium was rapidly converted<br />

to nitrate. In Tifton soil (fine loamy, siliceous, thermic<br />

Plinthic Paleudults) practically all ammonium had<br />

disappeared by day 22, whilst nitrification in Dothan soil,<br />

a fine loamy, siliceous, thermic Typic Hapludults, was much<br />

slower, and almost stopped by day 30. This difference<br />

between soils was probably due to differences in soil pH and<br />

buffer capacity. Tifton soil had an initial pH of 6.8,<br />

wihich is considered to be close to the optimum for<br />

nitrification. In contrast, Dothan soil had an initial pH of<br />

5.5, providing a much less favorable environment for<br />

nitrification. Nitrification in Dothan soil stopped when thepH<br />

approximated a value of 4.5.<br />

Test condition: temperature: 30 °C<br />

test duration: 40 d in quadruplicate<br />

air change: each 2. day<br />

Reliability: (1) valid without restriction<br />

study well documented and assignable<br />

28-MAY-<strong>20</strong>04 (42)<br />

Type of measurement: other: laboratory study<br />

Media:<br />

soil-air<br />

Remark:<br />

1) This is a static test, so less ammonia will be removed<br />

than in a flow through test.<br />

2) This reference also cites other papers which give ammonia<br />

losses from fertilisers and liquid sludges applied to soils<br />

of up to 60%. The ammonia volatilisation is dependent upon<br />

the pH of the soil and mode of application, with subsurface<br />

application having greatly reduced ammonia loss from soil.<br />

UNEP PUBLICATIONS 71

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!