| RCFC |
Refractory Ceramic Fibers Coalition |
|
2300 N Street, N.W. n Room 2110 n Washington, DC 20037 Tel: 202-663-9188 n Fax: 202-354-5230 n http://www.rcfc.net |
|
Issues
Related to Refractory Ceramic Fiber
¨
It is important when comparing
the effects of different fibers to explore how these effects relate to
dimension and durability, rather than simply to exposure concentrations.
In this regard, when such data are available, attention should also be
paid to the differences between exposure concentrations and lung tissue
burden.
¨
The RCF samples, to which the
animals were exposed, were significantly different both to the aerosols to
which humans may be exposed and to the other, non-RCF MMVF samples tested at
the Research and Consulting Company (RCC). These differences are important for risk assessment purposes
and to any comparisons made among man-made mineral fibers (MMVFs).
¨
Contrary to early reports,
pulmonary clearance was overwhelmed by the high RCF particulate levels and the
maximum tolerated dose (MTD) was therefore exceeded in the RCC experiments
with both rats and hamsters. In a
continuation of these experiments, as in most modern inhalation studies,
overload was monitored much more carefully before selecting test doses.
(See, for example, Ref. 3.)
¨
Pulmonary overload by even
innocuous particulate has been shown to produce inflammation, fibrosis and
tumors in the rat, thus confounding the results of the RCC rat studies.
(See Ref. 2.) In addition, particle exposures promote the production of
mesothelioma when mixed with fibers. (See
Ref. 2.)
¨
Most regulatory guidelines require effects occurring at pulmonary overload
concentrations to be discounted, as these would only occur at very high doses
that are not seen in humans.
¨
There is strong evidence that
had the RCF samples been prepared by the same method used for the other
“MMVF” samples neither overload nor tumors would have occurred. (See
Ref. 1.)
¨
The quantity of fibers remaining
in lung tissue depends upon the fibers’ ability to persist and accumulate;
these characteristics are determined by the fibers’ biopersistence, which is
heavily dependent on the chemical composition of the fiber.
The biological activity of fibers, on the other hand, is largely
determined by their size and shape. For
man-made wools, this depends upon how long fibers in the wool are broken,
which in turn depends upon how the fibers are manufactured. Therefore,
it is only meaningful to measure the biological activity of a fiber in a
laboratory setting if the samples tested are in a way that resembles the
aerosols produced during normal handling and use.
¨ The chart below provides a summary of the animal tests in which RCF was involved.
Summary
of Animal Inhalation Tests Related to RCF
|
Fiber Type |
Animals at Risk |
Exposure
duration (h/d;
d/w; wks) |
Concentration WHO f/cc (SD) mg/m3 (SD) |
Tumor Incidence (%) |
Reference |
|
|
|
Lung |
Mesothelial |
|
|||
|
Syrian Hamster Experiments |
|
|
|
|||
|
Air Control |
58 |
6: 5; 104 |
0 |
2 |
0 |
Smith
1987 |
|
Kaolin |
70 |
6; 5; 104 |
200 |
0 |
1 |
|
|
Air control |
119 |
6; 5; 104 |
0 |
0 |
0 |
McConnell 1995 |
|
Kaolin |
112 |
6; 5; 104 |
256
(58) 29.2
(7.7) |
0 |
38 |
|
|
SPF Wistar Rats (AF/HAN)
Experiment |
||||||
|
Unspecified |
48 |
7; 5; 52 |
95 |
17 |
0 |
Davis 1984 |
|
Fischer Rat (344/N)
Experiments |
||||||
|
Air Control |
130 |
6; 5; 104 |
0 |
1.5 |
0 |
Mast 1995a |
|
Kaolin |
121 |
6; 5; 104 |
234
(35) 29.1
(5.2) |
14.0 |
1.7 |
|
|
Mock after
service Kaolin |
118 |
6; 5; 104 |
206
(48) 30.1
(7.8) |
4.2 |
0.8 |
|
|
High purity |
121 |
6; 5; 104 |
213
(44) 29.2
(7.0) |
14.0 |
1.7 |
|
|
Zirconia containing |
121 |
6; 5; 104 |
268
(45) 28.9
(4.5) |
8.3 |
2.5 |
|
|
Air control |
132 |
6; 5; 104 |
0 |
0.8 |
0 |
Mast 1995b |
|
Kaolin |
126 |
6; 5; 104 |
162
(37) 16.5
(1.1) |
1.6 |
0 |
|
|
Kaolin |
128 |
6; 5; 104 |
91
(34) 8.8
(0.7) |
3.9 |
0.8 |
|
|
Kaolin |
125 |
6; 5; 104 |
36
(17) 3.0
(0.4) |
1.6 |
0 |
|
References
1.
Brown RC, Bellmann B, Muhle H, Davis JMG and Maxim LD.
(2005). Survey of the Biological Effects of Refractory Ceramic Fibres: Overload
and Its Possible Consequences. Ann. Occup. Hyg., pp. 1–13.
2.
Davis JMG, Addison J, Bolton RE, Donaldson K, Jones AD and Wright A.
1984. The pathogenic effects of fibrous ceramic aluminium silicate glass
administered to rats by inhalation or peritoneal injection.
Biological effects of man-made mineral fibres. Proceedings of a WHO/IARC
Conference) Vol. 2, Copenhagen.
3.
Hesterberg
TW, Axten C, McConnell EE, Hart GA, Miller W, Chevalier J, Everitt J, Thevenaz
P, Oberdorster G. Studies
on the inhalation toxicology of two fiberglasses and amosite asbestos in the
Syrian golden hamster. 1999. Part I. Results of a subchronic study and dose
selection for a chronic study. Inhal Toxicol 11(9):747-8.
4.
Mast RW, McConnell EE, Anderson R, Chevalier J, Kotin P, Thevanaz P,
Bernstein DM, Glass LR, Miiller, WC, and Hesterberg TW. 1995a. Studies on the
chronic toxicity (inhalation) of four types of refractory ceramic fiber in male
Fischer 344 rats.
Inhal. Toxicol. 7:425-467.
5.
Mast RW, McConnell EE, Hesterberg TW Chevalier J, Kotin P, Thevanaz P,
Bernstein DM, Glass LR, Miiller, WC, Anderson R. 1995b. A multiple dose chronic
inhalation toxicity study of size-separated kaolin refractory ceramic fiber (RCF)
in male Fischer 344 rats. Inhal.
Toxicol. 7:1141-1172.
6.
McConnell EE, Mast RW, Hesterberg TW, Chevalier J., Kotin P, Bernstein
DM, Thevenaz P, Glass LR, Anderson R. 1995. Chronic inhalation toxicity of a
kaolin-based refractory ceramic fiber in syrian golden hamsters. Inhal.
Toxicol. 7(4):503-32.
7. Smith
DM, Ortiz LW, Archuleta RF, Johnson NF. Long-term health effects in
hamsters and rats exposed chronically to man-made vitreous fibres. 1987. Ann.
of Occ. Hyg. 48, 731-754.