Philip Morris
Measurement of Asbestos Retention in the Human Respiratory System Related to Health Effects
Fields
- Author
- Bignon, J.
- Gaudichet, A.
- Sebastien, P.
- Gaudichet, A.
- Type
- SCRT, REPORT, SCIENTIFIC
- ABST, ABSTRACT
- BIBL, BIBLIOGRAPHY
- CHAR, CHART, GRAPH, TABLE, MAPS
- DRAW, DRAWING
- PHOT, PHOTOGRAPH
- ABST, ABSTRACT
- Area
- SOLANA,RICHARD/CENTRAL FILES
- Litigation
- Fali/Produced
- Characteristic
- EXTR, EXTRA
- Site
- R545
- Named Organization
- Ministere De La Qualite De La Vie
- Natl Bureau of Standards
- Univ College of Cardiff
- Workshop on Asbestos
- Icrp Task Group
- Ilo Uc Intl
- Institut Natl De La Sante Et De La Reche
- Laboratoire De Biophysique Medicale
- Laboratoire Des Particules Inhalees
- Natl Bureau of Standards
- Author (Organization)
- Centre Hospitalier Intercommunal
- Direction Departmentale De Laction Sanit
- Institut De Recherche Sur Lenvironnement
- Laboratoire Des Particules Inhalees
- Universite Paris Val De Marne
- Direction Departmentale De Laction Sanit
- Named Person
- Berry, J.P.
- Bignon, J.
- Evans
- Fisher, R.
- Galle, P.
- Morgan, A.
- Pooley, F.D.
- Schneiderman, M.
- Sebastien, P.
- Stanton
- Suzuki
- Timbrell
- Wagner
- Wright, G.
- Bignon, J.
- Master ID
- 2063104795/5283
Related Documents:- 2063104795-5283 Proceedings of Workshop on Asbestos: Definitions and Measurement Methods Proceedings of A Workshop on Asbestos Held at the National Bureau of Standards, Gaithersburg, Maryland, 770718 - 770720
- 2063104803-4820 History of Asbestos - Related Mineralogical Terminology
- 2063104821-4835 Fibrous and Asbestiform Minerals
- 2063104836-4849 the Crystal Structures of Amphibole and Serpentine Minerals
- 2063104850-4864 the 'asbestos' Minerals: Definitions, Description, Modes of Formation, Physical and Chemical Properties, and Health Risk to the Mining Community
- 2063104865-4870 General Discussion of Mineralogical Aspects
- 2063104871-4893 Epidemiological Evidence on Asbestos
- 2063104919-4930 Epidemiologic Evidence of the Effect of Type of Asbestos and Fiber Dimensions on the Production of Disease in Man
- 2063104931-4940 Pathophysiology in Relation to the Chemical and Physical Properties of Fibers
- 2063104941-4949 the Carcinogenicity of Fibrous Minerals
- 2063104950-4958 Niehs Oral Asbestos Studies
- 2063104959-4973 Epa Study of Biological Effects of Asbestos - Like Mineral Fibers
- 2063104974-4985 A Study of Airborne Asbestos Fibers in Connecticut
- 2063104986-4995 General Discussion of Relationship Between Chemical and Physical Properties and Health Effects
- 2063104996-5015 Identification of Selected Silicate Minerals and Their Asbestiform Varieties
- 2063105016-5029 An Overview of Electron Microscopy Methods
- 2063105030-5043 Identification of Asbestos by Polarized Light Microscopy
- 2063105044-5064 Mineral Fiber Identification Using the Analytical Transmission Electron Microscope
- 2063105065-5074 Transmission Electron Microscopical Methods for the Determination of Asbestos
- 2063105075-5088 Statistics and the Significance of Asbestos Fiber Analyses
- 2063105089-5106 Selection and Characterization of Fibrous and Nonfibrous Amphiboles for Analytical Methods Development
- 2063105107-5117 Asbestiform Minerals in Industrial Talcs: Commercial Definitions Versus Industrial Hygiene Reality
- 2063105118-5131 the Detection and Identification of Asbestos and Asbestiform Minerals in Talc
- 2063105132-5146 Misidentification of Asbestos in Talc
- 2063105147-5155 Ambient Air Monitoring for Chrysotile in the United States
- 2063105156-5167 Environmental Protection Agency Interim Method for Determining Asbestos in Water
- 2063105168-5171 Inter-Laboratory Measurements of Amphibole and Chrysotile Fiber Concentration in Water
- 2063105172-5177 the Standard for Occupational Exposure to Asbestos Being Considered by Astm Committee E-34
- 2063105178-5193 Identification and Counting of Mineral Fragments
- 2063105194-5202 Practical Aspects of Talc and Asbestos
- 2063105203-5210 General Discussion of Analytical Methods
- 2063105211 Introduction
- 2063105212-5219 the Mining Enforcement and Safety Administration - Regulations and Methods
- 2063105220-5229 Occupational Safety and Health Administration Methods
- 2063105230-5236 FDA Projects and Methods
- 2063105237-5238 Cosmetic Talc Powder
- 2063105239-5248 Cpsc Regulation of Non-Occupational Exposure to Asbestos in Consumer Products
- 2063105249-5255 Impact of Asbestos Regulations on the Mining Industry
- 2063105256-5265 General Discussion of Regulatory Aspects
- Date Loaded
- 20 Sep 1999
- UCSF Legacy ID
- mbp52d00
Document Images
(CS
Figure 3. Electron micrographs showing chrysotile type fibers isolated from
sputum in people resident inside asbestos sprayed buildings.
E. Respiratory Tissues.
1. Lung Parenchyma
Lung parenchyma samples from 27 autopsic cases diversely exposed to asbestos and with
different malignancies have been studied by TEM. Four blocks of parenchyma were sampled
in different sites of the same lung: central upper lobe, peripheral upper lobe, central
lower lobe, and peripheral lower lobe, as described elsewhere [25]. The geometric mean of
fiber count in the 4 sites has been calculated and then the cases have been classified in
groups according to the asbestos lung burden (Table 7). The proportion of cases having
more than 106 fibers/cc of lung parenchyma was 8 out of 10 for the asbestosis +
respiratory cancer group, 5 out of 11 for the mesothelioma group, 0 out of 2 for the lung
cancer (without associated lung fibrosis) group, and 2 out of 4 for the other malignancies
group.
105
2063104904

e
Table. 7. Asbestos fibers burden in lung parenchyma according to
pathological features.
Pathological Fiber concentration in the lung, Nb cm 3
features ~ <106 106 - 107 >107 Total
Asbestosis t
Respiratory
2
5
3
10
Cancer
Mesothelioma
6
3
2
11
Lung Cancer 2 0 0 2
Others
Malignancies
2
2
0
4
Total 12 10 5 27
The mineralogical type of fibers encountered in lung parenchyma has been assessed by
TEM and the results are expressed in Table 8 by the percentage of amphibole/all asbestos
fibers. The parenchyma retention of amphibole type fibers has been found important in
most cases, the amphibole proportion increasing with fiber concentration in all
pathological groups. Moreover, whatever the fiber concentration in lung parenchyma, the
highest mean proportion of amphibole type fibers was observed in the mesothelioma group.
Table 8. Mineralogical type of fibers in lung parenchyma:
ratio amphiboles/(amphiboles + chrysotile) x 100.
Pathological Fiber concentration in the lung, Nb an 3
features <106 106 - 107 >107 Average
Asbestosis t
Respiratory
38
59
69
58
Cancer
Mesothelioma
53
70
89
64
Lung Cancer 4 4
Others
Maligancies
12
41
26
Several size parameters have been assessed: mean length, mean diameter, and
proportion of fibers longer than 8 pa. The results are shown in Tables 9, 10, and 11
respectively. The main figures are: 1) the size of fibers increases when the
concentration increases; 2) the mean diameter never exceeds 0.16 Nm; 3) the mean
percentage of fibers longer than 8 pm does not exceed 20.8 percent.
106

.T,
Table 9. Size of fibers in lung parenchyma: mean length (um).
Pathological Fiber concentration in the lung, Nb cm 3
features <106 106 - 107 >107 Average
Asbestosis ±
Respiratory
3.7
5.4
5.5
5.1
Cancer
Mesothelioma
4.8
5.7
4.1
4.9
Lung Cancer 1 1
Others
Maiignancies
2.8
2.3
2.6
Table 10. Size of fibers in lung parenchyma: mean diameter (pm).
Pathological Fiber concentration in the lung, Nb cm 3
features <106 106 - 107 >107 Average
Asbestosis t
Respiratory
0.11
0.13
0.16
0.13
Cancer
Mesothelioma
0.09
0.13
0.12
0.11
Lung Cancer 0.05 0.05
Others
Malignancies
0.09
0.13
0.11
Table 11. Size of fibers in lung parenchyma:
than 8 pm (%). proportion of fibers longer
Pathological Fiber concentration in the 1ung, Nb cm 3
features
Asbestosis t <106 106 - 107 >107 Average
Respiratory
Cancer 11.6 20.1 20.8 18.6
Mesothelioma 13.1 20.5 11.4 15
Lung Cancer
Others 0.7 0.7
Malignancies 1.6 6.3 4.1
107

2. Asbestos Fiber Parameters A~_ccordin to ~Samp~lin_q Sites in Respiratory Tissues:
ar~ enhymaar et~TP leura, ~iastinaT Lymp~i Nes.
Besides lung parenchyma samples parietal pleura samples were available in 13 cases
and mediastinal lymph node.samples in 4 of these cases.
The comparison of fiber concentration in lung parenchyma and parietal pleura is
indicated on figure 4. The absenceoF-correlation between asbestos fiber content in
parenchymal and pleural tissue is emphasized. It is noteworthy that in some mesothelioma
cases, even with high concentration inside lung parenchyma, the fiber concentration in the
parietal pleura was very low. By contrast, a correlation seemed to appear between the
fiber concentration in parietal pleura and in lymph nodes (figure 5).
107
108
10 106 10 f
LUNG PARENCHYMA
M
A
AM M
M
A
A
105
104
M
M M M M
FIBERS IN LUNG AND
PLEURA (Nb.cw3)
M. Masetheliom.
A. Asbsstesis ± Luny
Cancer
Figure 4. Correlation between asbestos fiber concentration in lung and in parietal
pleura (see text for comments).
108

CS
A
A
y
W
PARIETAL PLEURA
105 106 10 7
A I I I
FIBERS IN PLEURA AND
LYMPH NODES (Nb.cm3)
Figure 5. Correlation between asbestos fiber concentration in parietal pleura and
mediastinal lymph nodes.
The comparison of mineralogical types has been carried out in the same way. The most
striking features were:
a) Most of TEM fibers encountered in parietal pleura were of chrysotile type even
when the proportion of amphibole/amphibole + chrysotile type fibers was higher than 0.5 in
the lung parenchyma (figure 6).
b) By contrast, so far in the few cases studied, most of the fibers encountered in
lymph nodes were of amphibole type (figure 6).
The fiber size has been compared in the different sampling sites (Table 12). The
longest ftT ers were found in the lung and the thinnest in the parietal pleura. Mean fiber
length was of 4.9 pm for lung parenchyma, 2.3 pm for parietal pleura, and 2.5 pm for lymph
nodes.
N
~
109 W
f+
~
~
00

COS
Ratio (AmPhiielas/Amp hib olms + ChrYsotilo) x 100
100
E-50
A
50 1g0
1~ _ AA A
LUNG PARENCHYMA
100
Dp
0
F-5
50 100
PARIETAL
PLEURA
LYMPH
NODES
Figure 6. Ratio of amphiboles count/total asbestos fibers count in lung parenchyma coopared
to the ratio in parietal pleura (top) and to the ratio in lyvph nodes (bottom).
110

CS
Table 12. Fiber size in lung parenchyma, parietal pleura,
and lymph nodes.
Lung
parenchyma Parietal
pleura Lymph
nodes
Mean Length
um 4.9 2.3 2.5
Mean Diameter
um
Proportion of Fibers 0.13 0.06 0.16
Longer than 8 um
percent 15 2 3
Discussion
{
The contribution of this metrologic study of asbestos dusts in the human PT is
relevant to three major points relating to the pathophysiology of fibrous particles:
- It allowed a check of the reliability of monitoring asbestos in sputum and lung
washing fluid for the assessment of asbestos exposure.
- It provided a better understanding of the partition of fibers in the different
compartments of the respiratory system, which allows hypothesis about the translocation of
fibers in the PT.
- It yielded quantitative data concerning the actual fiber dimensions in humans in
different diseases, including pleural mesotheliomata, which have to be discussed in view
of recent experiments concerning the mesothelial response in relation to fiber dimension.
A. External Indicators of Asbestos Lung Burden.
The present work demonstrated that the study of sputum and LWF by LM and TEM was very
reliable for the assessment of asbestos exposure in heavily exposed people. The advantage
of LWF over sputum is that it yields a greater amount of fibers which are most
representative of the alveolarly deposited fraction. This technique, which requires that
the patient accept a fiberoptic bronchoscopy, might help to diagnose asbestos-related
diseases. However, this possibility has some limitation. Indeed, the information
provided by BAL carried out in moderately exposed people was much less reliable than the
study of lung parenchyma. This can be easily understood since we will discuss later on
that the percentage of intraalveolar fibers is very low compared to the fibers retained in
lung parenchyma.
However, it seems that LM and TEM study of sputum is an excellent tool for detecting
and following exposed people [9,11]. A cytological control of the sputum looking for, AM
is needed to be sure that it represents the mineral content of the deep lung. It is
possible that the measurement of asbestos fibers in other biological samples could be
better indicators of asbestos body-burden, as discussed elsewhere [50]. Thus the search
for asbestos fibers in feces appeared to be a very sensitive method, allowing detection of
low intake of asbestos fibers [12].
B. Translocation of Asbestos Fibers in the Respiratory System.
The figure 7 summarizes all the mean data concerning number, length, and diameter of
fibers in four sites of the respiratory system: alveoli, LP, PP and LN. Moreover, the
figure 8 gives the distribution of length fibers in these four sites.
111
2063104910

Figure 7. Diagram comparing the mean number (Nb), mean length (L) and mean diameter
(d) of asbestos fibers in 4 sites of the respiratory system. Numbers have
been estimated for the whole lung for parenchyma (Par) and alveoli (Alv),
while they are given per cc of tissue for pleura and lymph nodes (LN).
112

percent
30
20
t0
30
20
10
30
20
10
30
20
10
LUNG PARENCHYMA
1 2 4 6 8 16 32 µm
PARIETAL PLEURA
LYMPH NODES
ALVEOLUS
Figure 8. Distribution of fibers length in parenchyma, parietal pleura, lymph nodes
and alveoli. Note that long fibers, more than 4{rm in length, are less
frequent in pleura, lymph nodes and alveoli than in parenchyma.
113
1

,--
For LP and alveoli, the fiber counts have been integrated for the whole lung,
distinguishing intra-alveolar fibers assessed by the BAL and intra-parenchymal fibers
assessed by destroying LP. Thus, the fraction corresponding to LP totalizes fibers
entrapped in the pulmonary interstitial tissue (plus fibers inside blood vessels?) and
fibers within the alveolar compartment. For that estimation, the volume of total lung has
been assumed to be 5000 mL and the fraction of alveolar spaces washed by the BAL to be
1/20 of the whole lung volume. Thus, the figure 7 shows that the intra-alveolar fraction
of all intra-parenchymal fibers would only represent about 1 percent of all the fibers
retained in lung tissue, when assumed that BAL recovered all intra-alveolarly deposited
fibers.
The mineralogical type of alveolar and interstitial asbestos dusts did not differ
significantly, as indicated on one hand by the electron diffraction pattern and on the
other hand by the measurement of fiber diameters, identical in both sites (0.13 pm in mean
diameter).
Elsewhere, it is noteworthy that the intra-alveolar fibers were significantly shorter
(3.3 pm in mean length) than the interstitial fibers (4.9 pm in mean length for LP
fibers). This difference must even be more important, because the mean length of
interstitial fibers is probably reduced by adding the 1 percent of short alveolar fibers
to the interstitial fibers when LP is studied; on the other hand, it is possible that the
mean length of intra-alveolar fibers is increased by the addition of longer fibers
deposited at the surface of the peripheral airways and washed out during the BAL. Indeed,
the mean length of fibers in sputum was found to be 5 pm (Table 5). These results clearly
indicate a shorter length of fibers inside alveoli compared to pulmonary interstitial
tissue. This can be related to two mechanisms, more or less associated (figure 9); either
long fibers might penetrate more easily across the alveolar membrane or small fibers are
more easily cleared from the interstitial tissue toward the alveolar spaces? As will be
discussed, sizing of fibers in pleura and in lymph nodes brings a clue in the favor of the
last hypothesis.
Indeed, in these two sides (PP and LN), the asbestos fibers were significantly
shorter than in lung parenchyma (2.3 pm in PP; 2.5 pm in LN compared to 4.9 pm in LP).
These findings are additional clues to the greatest translocation effectiveness of short
fibers. The migration of fibers was found even more selective in this study, since mostly
chrysotile fibers were found inside the PP, with a mean diameter of 0.06 pm, whereas
mostly amphibole type fibers with a mean diameter of 0.16 pm were found in mediatinal LN.
This selective migration of fibers might be mostly related to their dimension, as if only
short and very thin fibers could be entrapped in the PP tissue (figure 9).
C. Fibers Dimension Related to Carcinogenicity.
The aforementioned recent animal experiments after implantation of fibers in the
pleura [3,5] reinforced the idea that the carcinogenicity of fibers depends only on
dimension of fibers, whatever the chemical composition is, in such a way that the
probability to induce pleural cancer reaches 100 percent when all the fibers are less than
0.25 Nm in diameter and more than 8 Nm in length (see Stanton et al. , this meeting).
In humans, as demonstrated by this work and by others [24,26,57], all the asbestos
fibers encountered in different sites of the respiratory system were found to have a
diameter less than 0.25 pt. By contrast, the present study has clearly demonstrated that
the mean length of fibers was always less than 8 pm in all sites (figure 7). However, a
certain percentage of fibers was longer than 8 pm, especially in lung parenchyma (15
percent) (see Table 12 and figure 8). The point is to understand how such few fibers,
distant from the parietal pleura, might induce the carcinogenetic transformation of
mesothelial cells, or if other mechanisms specific to humans are to be considered.
114
