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 />
hour multiple day exposures to "worst case" ambient<br />
concentrations (0.1-0.3 mg/m3 of ammonium sulfate with a<br />
MMAD of 0.3-0.6 µm and a relative humidity ranging between<br />
40 and 85% in the different experiments).<br />
Test condition: Both healthy, "sensitive" and asthmatic adult men were<br />
exposed to nominal (100 µg/m3) concentrations of ammonium<br />
sulfate, ammonium bisulfate, and sulfuric acid with a mass<br />
median aerodynamic diameter (MMAD) of 0.3 µm and a<br />
geometric standard deviation of approximately 3.<br />
"Sensitive" subjects had been studied previously and had<br />
shown unusually definite reactions in controlled exposures<br />
to ozone. Exposure concentrations and particle size<br />
distributions of the sulfate salts were based on the<br />
highest reported 2-h filter sample of particulate sulfate<br />
in the Los Angeles Basin. Groups of 6 subjects were<br />
typically exposed, 3 at a time. Exposures were performed in<br />
a blind experimental fashion, i.e. subjects were unaware of<br />
their actual aerosol exposure day, with 1 or 2 days of a<br />
"control" exposure to purified air followed by 2 to 3<br />
consecutive days of sulfate aerosol exposure.<br />
To initiate the 2-h protocol, subjects performed baseline<br />
pulmonary function tests on entering the chamber. Subjects<br />
then exercised for the first 15 minutes of each 0.5 h for 2<br />
h, on bicycle ergometers to double, approximately, the<br />
subject´s minute volume of ventilation (comparable to light<br />
outdoor activity). Chamber temperature and relative<br />
humidity were maintained at 31 deg C and 40 per cent<br />
relative humidity which simulated a typical Los Angeles<br />
summer day. Additional exposures to ammonium sulfate were<br />
performed at 85 per cent relative humidity. Lung function<br />
tests were performed before and after exposures and<br />
included FVC, FEV 1.0, maximal mid expiratory flow rate,<br />
total lung capacity, residual volume, single-breath<br />
nitrogen, and total respiratory resistance. Analysis of<br />
subject performance after the exposures to ammonium sulfate<br />
revealed no important differences in response between<br />
normal and sensitive subjects. The measured ammonium<br />
sulfate concentrations were between 0.104 and 0.337 mg/m3,<br />
the MMAD ranged from 0.28 to 0.6 µm.<br />
Reliability:<br />
(2) valid with restrictions<br />
valid with restrictions; no information on purity<br />
Flag:<br />
Critical study for SIDS endpoint<br />
12-APR-<strong>20</strong>06 (175)<br />
Remark:<br />
A cluster of ten cases of Hodgkin`s disease was identified<br />
within the active workforce of a large chemical<br />
manufacturing firm over a 23-year period. In the total<br />
workforce of 6<strong>20</strong>00 person-years, an expected number of 2.01<br />
cases was calculated, giving a standardized incidence ratio<br />
of 497 (95 % CI 238-915). A nested case-control study was<br />
undertaken with <strong>20</strong>0 controls. For 11 chemicals (incl.<br />
ammonium sulfate) exposure odds ratios were calculated. No<br />
substance emerged as a likely candidate for explaining the<br />
observed Hodgkin`s disease cluster.<br />
Reliability:<br />
(1) valid without restriction<br />
Flag:<br />
Critical study for SIDS endpoint<br />
<strong>20</strong>-MAY-<strong>20</strong>03 (176)<br />
UNEP PUBLICATIONS 213