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Reprinted from the$ Archives of Environmental Health August 1969, Volume 19
Copyright 1969. American Medical Association <
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Pulmonary Ferruginous Bodies in City Dwellers
PLAINTIFF'S EXHIBIT USX-1083
A Study of Their Central Fiber
Paul Gross, MD; Robert T. P. deTreuille, MD, D Sc; and Martin N. Haller, Pittsburgh
Chrysolite, which comprises more than 90% o( the asbestos used in this country, has a character istic electron {Attraction pattern because ot Its unique, hollow, tubular, crystalline structure, as seen under the electron microscope.
On the basis of the electron diffraction pattern, chrysolite was decisively excluded as a constituent ot the cores of all 28 ferruginous bodies isolated from lungs of urban dwellers not occupationally exposed to asbestos.
This exclusion Is considered highly significant because if the ferruginous bodies In the above city dwellers had been caused by the inhalation of asbestos dusts, then some of the cores should logically be composed of chrysolite.
It has recently been suggested that the
prevalence of ferruginous ("asbestos")
bodies in the lungs of city dwellers not occu
pationally exposed to asbestos was largely
dependent upon the method and diligence
employed in searching for the ferruginous
bodies.1
The reported prevalence of the positive
cases was represented to range from 30% to
70% of the hospital deaths investigated;
whereas, by digesting some of the lung tissue,
a 97% prevalence of lungs positive for ferrugi
nous bodies was found among randomly
selected autopsied hospital patients in Pitts
burgh-1'
--
Ferruginous bodies, which are indistin
guishable from those produced by asbestos
dust, were recently demonstrated in lungs
of hamsters injected intratracheally with
----
d
Submitted for publication Feb 29, 1963; accepted March 17.
From the Industrial Hygiene Foundation of Amer ica, Inc (Drs. Gross and deTreville), and the Mellon Institute (Mr. Haller), Pittsburgh.
Reprint requests to Industrial Hygiene Fouadatiwii of America, Inc., 5231 Centre Ave, Pittsburgh 15232 (Dr. deTreviUe).
Arch Environ Health--Vol 19, Aug 1969
187
fibrous dusts other than those of asbestos.3 In view of this demonstration, it would seem proper to ask whether the "asbestos" bodies found in city dwellers have been evoked by the inhalation of asbestos dust or the inhalation of fibrous dust of other compositions.3
Based on the assumption that there is a substantial contamination of urban air by asbestos dust, it has been suggested that the source of such dust is from the brake lining of automobiles, the weathering of asbestoG cement products (shingles and tiles), as well as from insulation used in the building construction industry.4 Inasmuch as 90% or more of the asbestos used in the United States is chrysotile,5 and since very little of other types of asbestos is used in the above-named products, the major compo nent of the asbestos dust that is assumed to contaminate urban air would logically be chrysotile. Since there are no grounds for believing that asbestos bodies develop with greater difficulty around chrysotile fibers than around the fibers of other types of asbestos that may be inhaled, it would be reasonable to expect the vast majority of ferruginous bodies in the lungs of nonoccupationally exposed city people to have a central core of chrysotile--if the ferrugi nous bodies are indeed asbestos bodies.
Inasmuch as chrysotile fibers appear to be hollow in the electron microscope,* these may sometimes be identified by inspection. Furthermore, because of its hollow struc ture, chrysotile has a unique and readily identifiable diffraction pattern.7 Because chrysotile lends itself so readily to positive identification by electron microscopy, we undertook a study of the central cores of ferruginous bodies derived from lungs of
people of Pittsburgh not occupationally ex posed to asbestos. We are here reporting the results of our study.
Methods and Materials-
Ferruginous bodies isolated from the lungs of 28 people* were placed upon electron micro scope grids by means of a micromanipulator. In the electron microscope, it became necessary to find a suitable fiber area on the ferruginous body that was free of electron-opaque encrusta tion (possibly ferritin) which would have inter fered with the study of the core. Work with "standard" samples of chrysotile, amosite, and croddolite showed that useful diffraction pat terns could be obtained from fiber areas as small as 500 X 500 Angstrom, and as large as 5,000 x 5.000 A. All bodies examined had fiber areas suitable for such study. The bodies had to be manipulated in such a way as to yield their characteristic electron diffraction patterns, so that measurements of interplanar crystal lattice spacings could be made. Typical "layer line" diffraction patterns are obtained if the fiber axis is perpendicular to the electron beam. Ferruginous bodies isolated from the lungs of hamsters killed 12 months after an intratra cheal injection of 25 mg of brake-drum dust (iron-free) were similarly-placed upon electron microscope grids, and electron diffraction pat terns were obtained of the central filaments.
Results
None of the cores of the 28 ferruginous Bodies showed the hollow, tubular structure characteristic of chrysotile. Measurements of the diffraction patterns obtained (to an accuracy of 1%) on each of the cores of these bodies from human lungs showed that none of the fibers examined were identifiable as one of the three forms of asbestos cited above. In particular, chrysotile could be excluded as being involved in the formation
Arch Environ Health--Vol 19. Aug 1969
r \
188 PULMONARY FERRUGINOUS BODIES--GROSS ET AL
of the ferruginous bodies. On the other hand, the central filament of the ferruginous bodies isolated from hamster lungs injected with brake-drum dust yielded electron dif fraction patterns characteristic of chrysotile.
Comment
Although we have failed to identify the fibers that caused the population of ferrugi nous bodies in people not occupationally exposed to asbestos, we have decisively ex-cluded chrysotQe. This exclusion is highly significant in view of the fact that if asbes tos dust were the contaminant in urban air responsible for the formation of these bodies, chrysotile would be the most promi nent constituent of the cores and should be identifiable in some of the ferruginous bodies recovered from the lungs of these people, particularly since we have demon strated that the cores of ferruginous bodies resulting from intratracheal injections of brake-drum dust were composed of chryso tile.
From the fact that the central fibers of the ferruginous bodies examined demon strate an electron diffraction pattern, it
must be concluded that the fiber is crystal line, but identification must await further electron diffraction information and possi bly electron microprobe measurements. Its crystalline diffraction pattern effectively rules out fibrous glass, glass wool, and other vitreous materials in this sample which have been shown experimentally to be capa ble of producing ferruginous bodies.*
A recent analysis, utilizing an electron microscope, of tije central fiber of asbestos bodies removed from lungs of people who had worked in a Flushing (Netherlands) shipyard, led to the conclusion that these cores were composed of amphibole asbestos.* This might have been expected since croddolite and amosite have long been the predominant types of asbestos used in the shipbuilding industry. However, the relevance, if any, of this finding to the ferruginous bodies found in the lungs of urban dwellers, not occupationally exposed to asbestos, would appear to be doubtful.
This investigation was supported in part by Public Health Servioc research (rant PH96-66-156, National Center for Urban and Industrial Health, and rrant FR 05580 from the National Institute of Health.
Michael D. Utidjian, MD, Department of Epide miology, University of Pittsburgh Graduate School of
Public Health, isolated the ferruginous bodies and transferred them to electron microscope grids.
References
1. Utidjian, M.D.; Gross, P.; and deTreville, R.T.P.: Ferruginous Bodies in Human Lungs: Prev alence at Random Autopsies, Arch Environ Health
17:327-333 (Sept) 196a
2. Gross, P,, et al: Pulmonary Ferruginous Bodies: Development in Responae to Filamentous Dusts and a Method of Isolation and Concentration, Arch Path 35:539-546 (May) 196&
3. Cralley, LX, et al: Source and Identification of Respirable. Fibers, A/HA J 29:129-135 (May-April) 196a
4. Thomson, XG-, et al: Asbestos as Modern Urban Hazards, S A/r Med J *7:77-31. 1963.
a Rosato, D.V.: Atbeetoe: Ite Industrial Applica
tions, New York: Reinhold Publishing Corp,, 1959,
P<a Rice. R.V.; Maser. M.; and Klug, H.P.: Chryso
lite Morphology, Amer Min 45&80-688, 1960.
7. Zussman, X, and Brindley, G.Wu Electron Diffraction Studies of Serpentine Minerals, Amer Min 42:133-153,1957.
a Gaensler, EA, and Addington. W.W.: Current Concepts: Asbestos or Ferruginous Bodies, Nets Eng J Med 287:433492 (Feb 27) 1969.
9. Stumphius, J, and Mayer. PJB_: Asbestos Bodies and Mesothelioma, Ann Oecup Hyt 11:283293 (Oct) 1968.
Arch Environ Health--Vol 19, Aug 1969
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