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 />
difference between air- and ammonium sulfate exposed animals<br />
was both in spontaneously breathing and paralyzed animals. The<br />
residual volume / twice total lung capacity (RV/TLC), measured<br />
in paralyzed animals, was also significantly higher in<br />
ammonium sulfate exposed rats than in air-exposed rats. Carbon<br />
monoxide diffusion capacity and quasistatic compliance were<br />
not affected by aerosol exposure. Compared with air-exposed<br />
animals, ammonium sulfate exposed rats showed a decreased<br />
slope of single-breath N2 washout curves.<br />
Test condition:<br />
There were no consistent differences observed between 5- and<br />
<strong>20</strong>-day exposed animals.<br />
The test animals (from Charles River Breeding Labs, Portage,<br />
Mich.) were isolated for 3 weeks after delivery. Following<br />
isolation, animals were assigned to exposure groups such that<br />
preexposure body weight distributions were the same for all<br />
experimental groups exposed at the same time.<br />
Anesthetized animals were instilled intratracheally with<br />
either sterile saline or porcine pancreatic elastase (EO127,<br />
Sigma Chemical Co.; 75 units/100 g bw). Elastase activity was<br />
determined immediately before daily instillations by the<br />
method of Sachar et al. (1955, Proc. Soc. Exp. Biol. Med. 90,<br />
323-326), using elastin-orcein as substrate.<br />
The doses of elastase were selected as the<br />
maximum doses tolerated that produced less than 10% acute<br />
mortality, based on results of previous studies (Busch et<br />
al., 1984, Environ. Res. 33, 473-496).<br />
Following instillation rats were given prophylactic<br />
tetracycline (60 mg/L) in their drinking water<br />
for 2 weeks to prevent pulmonary infections, occasionally<br />
observed in preliminary studies, following the instillations.<br />
Three weeks following intratracheal instillations, the then<br />
approximately 14 week old rats were exposed in Hazleton<br />
Systems Model 1000 stainless steel chambers for 5 or <strong>20</strong> days<br />
to filtered room air or 1 mg/m3 ammonium aerosol.<br />
Chamber aerosol concentration was monitored continuously and<br />
the variations throughout the chamber were less than 5% of the<br />
mean concentration. Aerosol concentrations were<br />
determined from four daily, 90-min, filter-pad samples;<br />
ammonium sulfate concentrations were determined by an<br />
automated methyl-thymol blue method. Particle-size<br />
distribution was measured from combined Mercer cascade<br />
impactor samples, collected over 15 hours of exposure during a<br />
5-day week. Daily impactor samples were collected at a<br />
constant flowrate of 2 liters/min on glass coverslips.Mass<br />
median aerodynamic diameter (MMAD) and geometric standard<br />
deviation (GSD) of the aerosol were calculated using a program<br />
which compared the impactor data with a log-normal<br />
distribution (Hill et al., 1979; PNL-2405. Pacific Northwest<br />
Laboratory. Richland. WA. Available from NTIS,<br />
Springfield.Va.).<br />
For the evaluation of pulmonary function, animals were<br />
anesthetized by intraperitoneal injection with ethyl<br />
carbamate and then intubated with an esophageal catheter and<br />
placed prone in a flow-type plethysmograph. Transpulmonary<br />
pressure (airway pressure minus esophageal pressure) was<br />
determined by electronic subtraction of the two signals.<br />
Before making any measurements, the lungs were inflated<br />
twice to total lung capacity to establish a constant volume<br />
UNEP PUBLICATIONS 171