Subacute inhalation toxicity testing with iodoform vapor

1981 ◽  
Vol 8 (1-2) ◽  
pp. 59-70 ◽  
Author(s):  
Martin F. Tansy ◽  
Michael Werley ◽  
Wendell Landin ◽  
Richard Oberly ◽  
Frank M. Kendall ◽  
...  
1984 ◽  
Vol 2 (5) ◽  
pp. 328-347 ◽  
Author(s):  
Clayton Huggett

A number of procedures have been described in the literature for investigation of the inhalation toxicity of combustion products. There is need for agreement on test methods and test conditions to facilitate communication, allow the ex change of data, and provide a basis for control of hazards due to combustion products in fires. Combustion systems and animal exposure systems which have been employed are classified according to their basic attributes. Simple con siderations of limiting stoichiometry in the combustion module can guide the selection of conditions which simulate real fire environments. The dynamics of the exposure system will determine the procedural dose received by the test animal and can be related to real fire exposure. Many past investigations have failed to take adequate account of these fundamental principles.


2018 ◽  
Vol 295 ◽  
pp. S123
Author(s):  
P. Hayden ◽  
G.R. Jackson ◽  
J.L. Vinall ◽  
E. Storey ◽  
H. Simpson ◽  
...  

1996 ◽  
Vol 71 (1-2) ◽  
pp. 1-10 ◽  
Author(s):  
J. Pauluhn ◽  
D. Bury ◽  
U. Föst ◽  
A. Gamer ◽  
E. Hoernicke ◽  
...  

1986 ◽  
Vol 5 (2) ◽  
pp. 127-135
Author(s):  
M. F. Tansy ◽  
M. Werley ◽  
R. Oberly ◽  
F. M. Kendall ◽  
W. E. Landin ◽  
...  

Short-term exposures of adult male and female Sprague-Dawley rats to aerosolized aluminum chlorhydrate in a silicone-ethanol vehicle were conducted to assess the effects of such exposures upon body and tissue weights, various blood constituents, tissue aluminum concentrations, and appropriate histopathology. Rats were exposed 4 hours/day 5 days/week (excluding weekends) for 22 days to concentrations of 0.34 ± 0.22 μg/L and 2.50 ± 0.37 μg/L of solubilized aluminum chlorhydrate as determined by atomic absorption spectroscopy. The mass medium aerodynamic diameter (MMAD) for the low-dose group was 1.57 ± 0.45 μm. The mean MMAD for the high-dose exposure was 4.28 ± 0.93 μm. No mortality was experienced by any group. Final mean body and most tissue wet weights were not significantly different from sham control values. No remarkable changes were noted in SMA 12/60 blood values for either exposed group. Mean aluminum concentrations of lungs, liver, gastric mucosa, or parathyroids from the high-dose group were not significantly different than mean values for the same organs obtained from a sham exposed group of rats. There were no remarkable histopathological observations.


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