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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

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