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 />
5. TOXICITY ID: <strong>7783</strong>-<strong>20</strong>-2<br />
DATE: 18.04.<strong>20</strong>06<br />
necessary, during preliminary experiments, to prevent<br />
changes resulting from pneumonia (and subsequent mortality).<br />
EXPOSURE TO TEST SUBSTANCE:<br />
One-half of the elastase-treated animals and one-half of the<br />
saline-treated animals were exposed to ammonium sulfate, and<br />
the remainder were exposed to air only. Animals were exposed<br />
and housed in Hazelton Systems Model 100 stainless-steel<br />
exposure chambers. The chamber air flow of 0.30 m3/min<br />
provided seven changes of filtered air per hour.<br />
Aerosols were introduced into and thoroughly mixed with the<br />
filtered air stream before entering the chambers. Several<br />
Retec nebulizer generators supplied with special reservoirs<br />
provided a constant ammonium sulfate solution concentration<br />
and liquid level for stable aerosol generation.<br />
Time-weighted average concentrations of aerosol were<br />
determined from four 90-mm filter samples taken over the<br />
daily 6-hr exposure periods. These filter samples were<br />
analysed, chemically and gravimetrically, and corrected by<br />
correlating the amount of particles recovered by spiked<br />
filters with each set of samples. Daily<br />
time-weighted-average concentrations for ammonium sulfate<br />
were 1.03 mg/m3 +/- 0.11 SD (gravimetric) and 0.97 mg/m3 +/-<br />
0.11 SD (chemical). Aerosol particle size was measured by a<br />
cascade impactor (Mercer design) on samples collected over 15<br />
hours of exposure time during a 5-day week. The MMAD was 0.42<br />
+/- 0.05 um SD, geometric standard deviation (GSD) was 2.25<br />
+/- 0.22.<br />
Animals were exposed for 6 hours/day, 5 days/week, for a<br />
total of <strong>20</strong> exposures. Control (air only) animals were<br />
maintained in identical chambers under similar conditions of<br />
air flow, temperature, humidity, cage changes, etc. All<br />
animals were housed in similar chambers during nonexposure<br />
periods.<br />
At the end of the exposure period (4 weeks after<br />
intratracheal instillations), animals were deeply<br />
anesthetized, and the lungs perfused with 2% glutaraldehyde<br />
solution. The lungs were removed for examination after<br />
observation of macroscopic features in situ. Fixed lung<br />
volume was determined by weight of displaced fluid.<br />
Slices of approximately 1 mm were taken from both the right<br />
diaphragmatic and left lobes of each animal and examined<br />
under a dissecting microscope for the degree of emphysema. A<br />
subjective rating of 0 (none observed) to 5 (total<br />
involvement) was given to each tissue slice. The rating<br />
(score) was determined by estimating the proportion of the<br />
slice affected by disruptive alveolar changes and the<br />
severity of alveolar disruption within involved areas. The<br />
area affected was determined.<br />
From each animal, the slice most closely approximating the<br />
mean degree of involvement was prepared for examination by<br />
scanning electron microscopy (SEM).<br />
Morphometry: Chord lengths were measured across alveoli,<br />
alveolar sacs, and alveolar ducts from photographs taken<br />
during SEM. The median, mean, and SD were calculated for<br />
these chord length measurements, and histograms were<br />
developed. To ensure consistency in measurements between<br />
photographs the criteria as developed by Busch et al.,1984<br />
(Env. Res. 33, 497-513) were followed. In addition, alveolar<br />
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