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A recent interpretation of the pathogenetic role of asbestos fiber size in the development of mesothelioma and in the possibility of mesothelioma prevention needs clarification. This point of view is based on a biased interpretation of the literature. Epidemiologic, experimental, and molecular evidence suggests that the arguments for the role of fiber size relative to dose, dose–response effect, and genetic susceptibility are sci-entifically unsound. Their proponent also states that means available in the past for the implementation of dust-control measures and/or personal protective equipment would not have contributed to reducing the frequency of mesothelioma among exposed subjects, an argument again based on invalid assumptions. Key words: asbestos; mesothelioma; prevention.

I N T J O C C U P E N V I R O N H E A LT H 2 0 0 7 ; 1 3 : 6 4 – 6 9

A

n unsound hypothesis, positing a role for fiber size in the pathogenesis of mesothelioma and debunking the potential effectiveness of dust-control measures that were available by the mid 1980s for its prevention, has recently surfaced in the medical literature. Its author, Chiappino,1 has arrived at

erro-neous conclusions based on arbitrary interpretations of selected earlier reports. A danger is that his conclu-sions, which are not scientifically valid, could be used to support unjustified acquittals of negligent defendants in the courts.

Chiappino’s published interpretations need to be corrected or clarified with respect to:

1. the role of fiber dimensions (length and diameter); 2. the alleged predictability, but not preventability, of mesotheliomas until the 1980s, and role of exposure dose and the dose–response effect;

3. the alleged role of genetic susceptibility in deter-mining the risk of developing mesothelioma; and

4. the alleged uselessness of dust control measures and ineffectiveness of personal respiratory protection equipment for reducing exposures.

The Role of Fiber Dimensions

Chiappino states as a given fact that only “ultrashort” and “ultrathin” asbestos fibers are able to reach the parietal pleura and lead to the development of malig-nant pleural mesothelioma. His statement is based mainly on three publications 2–4 that allow him to assert

that ultrathin fibers are “the only dimensional size class that can get past the lung–pleura barrier.”

A thorough reading of the papers he quotes reveals that:

According to Paoletti et al.,2“about 80% (48/60) of

the fibers found were under 5 µm in length, and 68% were under 0.3 µm in diameter,” while according to Boutin et al.,3“a total of 22.5% of fibers were 5 µm in

length in black spots” (the small dot-like spots of the parietal pleura near the lymphatic stomata). In these areas fibers 8 µm or more in length accounted for 8% of all fibers, those 15 µm or longer, 2.1%;, and the max-imum length recorded was 29 µm; the geometric mean of the diameter was 0.13 µm, greater than that of the fibers found in the lung, which was of 0.10 µm. The conclusions were that “long amphibole fibers concen-trate in the same structures of the parietal pleura that trap other particles such as coal dust.”

According to Suzuki and Yuen,4 “the majority of

asbestos fibers detected in the lung and mesothelial tis-sues were shorter than 5 µm”; in the study published in 2002, the fibers longer than 5 µm represented 10.5%,

Special Contributions

The Role of Asbestos Fiber Dimensions

in the Prevention of Mesothelioma

LORENZO TOMATIS, MD, SUSANNA CANTONI, MD, FRANCESCO CARNEVALE, MD,

ENZO MERLER, MD, FRANCO MOLLO, MD, PAOLO RICCI, MD, STEFANO SILVESTRI, OH,

PAOLO VINEIS, MD, BENEDETTO TERRACINI, MD

Received from the International Society of Doctors for the Envi-ronment (LT); the Occupational Health Unit, National Health Ser-vice, Milan, Italy (SC); the Occupational Health Unit, NHS, Flo-rence, Italy (FC); the Venetian Mesothelioma Registry, Occupational Health Unit, NHS, Padua, Italy (EM); the University of Turin, Italy, Professor emeritus (FM); the Occupational Health Unit, NHS, Mantua, Italy (PR); the Tuscany Mesothelioma Registry, Center for Study and Cancer Prevention, Florence, Italy (SS); Environmental Epidemiology, Imperial College, London, U.K. (PV); and the Center for Oncological Prevention, CPO, Turin, Italy (BT).

Address correspondence and reprint requests to: Benedetto Ter-racini, Center for Cancer Prevention, Region Piemonte, Torino, Italy (via Santena 7, 10126 Torino, Italy); e-mail: <benedetto.terracini@ fastwebnet.it>.

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while in a previous study5 they reached 18.6%. The

conclusions were that “such short, thin asbestos fibers should not be excluded from those contributing to the induction of human malignant mesothelioma,” which is very different from saying that they are the sole agent in mesothelioma induction.

Even based on a more recent pathology study,6the

principle of “contribution”—not of exclusiveness—of fibers that are equal to or shorter than 5 µm in length and equal to or smaller than 0.25 µm in diameter in the development of mesothelioma is confirmed. There is no evidence that only ultrathin and ultrashort fibers penetrate the pleura, since, although the smaller fibers are in the majority, larger fibers are also present in the parietal pleura, both in the material examined in the studies cited by Chiappino and in other studies by the same authors.

Furthermore, the common occurrence in the pari-etal pleura of “black spots” shows that the lung–pleura barrier is not at all impassable, even for particles much larger than “ultrathin” and “ultrashort” fibers. These parietal pleura agglomerates, which contain carbona-ceous pigments and mineral fibers, have been found in 92.7% of 150 consecutive autopsies of inhabitants of urban areas in Belgium.7

Chiappino states such findings as “not physiological,“ and “likely linked to transitory increases in the perme-ability of the lung–pleura barrier due to inflammatory events or other situations influencing the direction of the lymphatic flow.” The relevance of such an obvious statement, in respect to asbestos exposure and the con-sequent induction of mesothelioma, is not clear, since it refers to a phenomenon that certainly is not physio-logic. It is well known that benign effusions (precisely by pleural transudation and/or exudation) are the first reactive manifestations that might later lead to those features of diffuse pleural fibrosis considered among the indicators of previous exposure to asbestos.8,9

Moreover, Gibbs et al.10found long fibers of

commer-cial amphiboles in subjects with diffuse pleural fibrosis, while Dodson et al.11have shown the presence of similar

fibers in pleural (parietal) plaques of asbestos workers, as well as in the peritoneum and in the mesentery.12

Starting from the lung, asbestos fibers can reach other organs by direct or macrophage-mediated migra-tion, or by diffusion through the lymphatic and blood vessels.4,12–19 In addition, once they have reached the

lung, asbestos fibers can undergo transformation and degradation processes that might result in reducting length and diameter.20

Our concerns about Chiappino’s statements are also supported by other scientists conclusions:

Asbestos fibers of all lengths induce pathological responses and caution should be exerted when attempting to exclude any population of inhaled fibers, based on their length, from being

contribu-tors to the potential for development of asbestos-related diseases.21

Clearly, fibers of the type and size known to be asso-ciated with the greatest risk of mesothelioma do, in fact, migrate to pleural tissues.22

The large majority of fibers detected in the omen-tum and mesentery of 20 occupationally exposed work-ers suffering from mesothelioma, inclusive of three shipyard workers affected by peritoneal mesothelioma, were longer than 5 µm, so that Chiappino’s view is def-initely not valid for peritoneal mesotheliomas, repre-senting about 10% of all mesotheliomas.12

Alleged Predictability, but Not Preventability, of Mesothelioma until the 1980s, and the Role of Exposure Dose and Dose–Response Effect

The first scientific articles on the carcinogenic effect of asbestos on the mesothelium appeared in the 1960s, on the basis of clinical evidence in exposed workers.23 In

1964, the conference on the biological effects of asbestos organized by the New York Academy of Sci-ences ratified the general consensus of the scientific community on the carcinogenic effects of asbestos. In that conference the first cases of pleural mesothelioma in asbestos workers in Italy were described and pre-sented by Professor Vigliani,24who had been

Chiap-pino’s professor at the University of Milan. In 1977, the IARC classified all types of asbestos in the group of known human carcinogens.25 In the 1960s,

asbestos-exposed subjects were already under mandatory health surveillance by occupational physicians in many coun-tries, including Italy. No occupational physician, there-fore, from the mid 1960s onwards, could be unaware of the carcinogenic effect of asbestos on the mesothe-lium, and consequently of the need to give indications to those in charge within the companies of the rigorous measures of environmental prevention and individual protection that were needed.

Chiappino states that the means for prevention that could have been applied before the 1980s to eliminate or reduce the risk related to exposure to dusts were efficient to prevent asbestosis, which is caused by inhaled fibers of all dimensions, but not mesothelioma, which is caused, he repeatedly emphasizes, exclusively by ultrathin fibers. The inconsistency of this argument is shown above.

It has been repeatedly claimed that mesotheliomas can be caused by light and/or brief exposures.26–30A

cut-off “in the region” of 5 fibers/mL of air/year was sug-gested for amphiboles.31However, in a later, ample

epi-demiologic survey carried out in France,32a significant

excess of mesotheliomas was observed for levels of cumulative exposure as low as 5 f/mL/year or lower, below the limits of acceptable exposure adopted in many industrial countries in the 1980s. The IARC stated, as early as 1977,25that there is no proof of a cut-off level of

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exposure to asbestos below which there is no risk,1 a

statement that was repeated by Doll and Peto in 198533

and, more recently, citing Selikoff,34by Motley et al.35

Some authors have declared themselves in favor of recognizing a cut-off level on the basis of the assumed levels of exposure of asbestos-related mesothelioma cases,36 but according to Hodgson and Darnton37the

direct confirmation of a threshold based on human data is virtually impossible, and case–control studies with measurement of pulmonary asbestos content38–40

do not suggest any threshold, or any tendency of the steepness of the dose–response curve to decrease at the lower ends of their scales of exposure.

At the end of the 1960s, it was already evident that increased risks of mesothelioma correlate with increases in both intensity and duration of exposures to asbestos, and thus with the overall dose of inhaled fibers,41–43 and that lower cumulative doses lead to

longer latency periods for the onset of mesothelioma. This observation has led to the consideration that a reduction in dose, i.e., applied prevention, will at least postpone the appearance of mesothelioma.43–46

Later, the HSE’s asbestos workers’ mortality survey in England and Wales demonstrated that workers first exposed to asbestos before the implementation of the 1969 Regulation, and thus exposed to higher intensities than thereafter, had a higher frequency of mesothe-lioma than those first exposed only after 1970, showing that “prevention,” intended as a reduction of intensity of exposure, reduces the occurrence of mesotheliomas.42

These observations then found authoritative confir-mation, and finally a computation of risk according to dose and latency.48,49 The doubts raised by some

authors50 about the existence of a dose–response

rela-tion for mesothelioma refer to particular case studies, often characterized by very high exposures, whereas Peto’s formulas answer the majority of observations and are almost unanimously supported by the scientific com-munity. More recently, other authors51observed a

signif-icant dose–response correlation for pleural mesothe-lioma in a cohort of 5,000 Londoners exposed to asbestos between 1933 and 1980. Various authors have verified a significant increase in the risk of mesothelioma correlated with the increase in pulmonary asbestos con-tent detectable by electron microscopy.52–55

The epidemiologic findings are also confirmed by experimental studies showing that a reduction in dose lengthens the period of latency of mesotheliomas, and in this way reduces their incidence, since the duration of latency exceeds that of the life of rats.56,57 In-vitro

studies58of the damaging effect of asbestos corpuscles

on DNA, which is strongly inhibited by the chelating action of the leukocytes, also supports the relevance of continuous inhalation of “fresh” fibers for the onset of mesothelioma.

Chiappino emphasizes the role of the “trigger dose” as a short-lasting and irreversible phenomenon in

pleu-ral carcinogenesis caused by asbestos. Indeed, what is known about induction and growth of tumors strongly suggests that the progressive and irreversible develop-ment of the tumor cannot take place at the beginning of exposure or shortly thereafter. In fact, if models of time of reduplication of tumor cells—developed on the basis of studies carried out on this topic59–63—are

applied, for instance, to the period elapsing between the beginning of the exposure and the clinical mani-festation of a case of mesothelioma with a latency of >10 years, the tumor mass would reach paradoxical dimensions. Therefore, “self-sufficiency” of the neo-plastic process of the mesothelioma at the beginning of such a period of latency is hardly tenable. If asbestos, as is generally recognized, is a complete carcinogen, i.e., it can both induce and promote cancer, its promoting effect must be considered effective up to complete induction, and therefore for a prolonged period of exposure. Therefore, contrary to Chiappino’s thought, the persistence of exposure after an initial first expo-sure can never be considered irrelevant.

The Relevance of Genetic Susceptibility in Determining the Risk of Developing Mesothelioma

The argument used by Chiappino is that individual sus-ceptibility must play an important role, since only 10% of the people exposed to asbestos develop mesothe-lioma.1This proportion, however, does not differ much

from those associated with other environmentally induced carcinogenic events in humans. In addition, the argument is faulty because it does not consider the very long latency period before mesothelioma arises, sometimes more than 40 years, and that exposure does not start at birth and that to observe a 100% incidence exposed individuals should be followed for time peri-ods longer than their lifespans.

While the development of mesothelioma in individ-uals who have had only months of low-level exposures to asbestos64 may suggest that individual susceptibility

could play a role, other studies actually suggesting familial mesothelioma clusters65 contain serious

falla-cies66and provide poor evidence for such a role. Genes

that have been implicated in other studies are NAT2, GSTM1, and DNA repair genes. The evidence is con-tradictory (e.g., both NAT2 rapid acetylators and slow acetylators have been suggested as being at high risk) and associations are weak., making its biological plausi-bility highly questionable.

The Alleged Uselessness of Dust-control Measures and Ineffectiveness of Personal Respiratory Protection Equipment for Reducing Exposures

Chiappino states that “mesothelioma in the ’60s,’70s, and ’80s had the requisite of predictability, but it could not be prevented with the technology of dust control

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available at that time in occupational settings.” He pos-tulates that a systematic error was introduced in the field of industrial hygiene when it was decided to con-sider only fibers ”subject to regulation,” neglecting all those under 0.5 µm in diameter, which, instead, are in his view the ones solely responsible for biological reac-tions. He also claims, paradoxically, that air extractors with filters unable to stop the ultrathin fibers were responsible for disaggregating the large asbestos fibers, thus increasing the risk proportionally to their power. This is meant to give credit to the statement that mesothelioma is caused only by ultrathin fibers that could not have been controlled with the air-treatment technology available in 1960–1980. With these state-ments, Chiappino seems to be unaware of what the real situation was like in work environments in those years, and introduces misleading elements concerning the characteristics of the air extractors.

Inside the workshops that had large amounts of dust, wall-mounted air extractors were installed to expel polluted air directly outside, with no filtering system at all. Some of these air extractors were still visi-ble a few years ago in old dismantled industrial sheds (e.g., Eternit in Casale Monferrato, Breda in Pistoia, Italy). These systems were based on dilution ventila-tion. The introduction of filtering systems, usually fabric dust collectors, needed outdoor installation.67

There was neither need nor convenience in recycling exhausted air in workshops without heating or air con-ditioning.

The 1970 edition of the manual Industrial Ventilation

states, with regard to the recirculation of exhaust air:

Air recycling is not recommended in the cases where the extractor systems treat substances that have an effect on the worker’s health. Recirculation is accepted if the contaminants that are filtered are simply bothersome and do not pose a real health threat, and in any case only during the winter period in order to save on the cost of heating.68

Contrary to what Chiappino asserts, HEPA ( high-efficiency particulate arrestance) filters, which were developed in the 1940s by the U.S. Atomic Energy Commission to respond to the need for an efficient fil-tering of radioactive particulate contaminants, were commercially available in Italy at the beginning of the 1950s. In addition, their use was the filtering the air that was released into the environment. They would not have had any role, therefore, in protecting the workers in the working environment. Air extraction at the source, physical confinement of the polluting source for limiting the air dispersion of pollutants, the so-called “close-cycle,” if at all reasonably possible, has always represented the criterion of choice for selecting dust-control measures in workplaces. Consequently, prevention has always been based on extraction and expulsion of polluted air, and not on its filtration.

Furthermore Chiappino asserts, without citing any supporting reference, that personal protective equip-ment was ineffective for respiratory protection. Indeed, filters do not work as “sieves,” but they are able to stop particles and fibers of much smaller sizes than those indicated by the manufacturer as filtering capacity. This happens because very small fibers and particles tend to deposit around the openings between the threads of the filtering fabric for diffusional and electrostatic reasons, giving more protection than that which could be expected from a simple “sieve” effect.69–72

In conclusion, Chiappino’s argument basically rests on two points. 1) pleural mesothelioma is induced by the ultrathin and ultrashort fibers only; and 2) asbestos persistence in human tissues is extremely long com-pared with other known carcinogens.

With regard to the former, several studies provide evi-dence that fibers of all lengths and diameters play a role in the induction of mesothelioma. With regard to biop-ersistence, the recognition of this property is used by Chi-appino to exclude the need of repeated and prolonged exposures to initiate and promote the carcinogenesis that will lead to the development of mesothelioma. All epi-demiologic, experimental (in vivo and in vitro) and molecular evidences, however, reject this pathogenetic hypothesis, as well as the negative impact its acceptance would have in terms of actual prevention and regulations worldwide. It would actually mean the total acquittal of anyone who, being in a position to do so, omits to take care to prevent asbestos exposure, or at least reduce its intensity, leaning on “fatalistic principles” that are not substantiated in the international scientific literature.

References

1. Chiappino G. Mesotelioma: il ruolo delle fibre ultrafini e con-seguenti riflessi in campo preventivo e mediclo legale. Med Lav. 2005;96:3-23. [In Italian]

2. Paoletti L, Falchi M, Batisti D, Zappa M, Chellini E, Biancalani M. Characterization of asbestos fibers in pleural tissue from 21 cases of mesothelioma. Med Lav. 1993;84:373-8. [In Italian] 3. Boutin C, Dumortier P, Rey F, Vialat JR, De Vuyst P. Black spots

concentrate oncogenic asbestos fibers in the parietal pleura. Thoracoscopic and mineralogic study. Am J Respir Crit Care. 1996;153:444-9.

4. Suzuki Y, Yuen SR. Asbestos fibers contributing to the induction of human malignant mesothelioma. Ann NY Acad Sci. 2002; 982:160-76.

5. Suzuki Y, Yuen SR. Asbestos tissue burden study on human malignant mesothelioma. Ind Health. 2001;39:150-60. 6. Suzuki Y, Yuen SR, Ashley R. Short, thin asbestos fibers

con-tribute to the development of human malignant mesothelioma: pathological evidence. Int J Hyg Environ Health. 2005;208:201-10.

7. Mitchev K, Dumortier P, De Vuyst P. “Black spots” and hyaline pleural plaques on the parietal pleura of 150 urban necropsy cases. Am J Surg Pathol. 2002;26:1198-206.

8. Levin SM, Kann PE, Lax MB. Medical examination for asbestos-related disease. Am J Ind Med. 2000;37:6-22

9. Peacock C, Copley SJ, Hansell DM. Asbestos-related benign pleural disease. Clin Radiol. 2000;55:422-32.

10. Gibbs AR, Stephens M, Griffiths DM, Blight BJN, Pooley D. Fiber distribution in the lungs and pleura of subjects with asbestos related diffuse pleural fibrosis. Br J Ind Med. 1991; 48:762-70.

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11. Dodson RF, Williams MG, Corn CJ, Brollo A, Bianchi C. Asbestos content of lung tissue, lymph nodes, and pleural plaques from former shipyard workers. Am Rev Respir Dis.1990;142:843-7.

12. Dodson RF, O’Sullivan MF, Huang J, Holiday DB, Hammar SP. Asbestos in extrapulmonary sites—omentum and mesentery. Chest 2000;117:486-93.

13. Godwin NMC, Jagatic J. Asbestos and mesothelioma. Environ Res. 1970;3:391-416.

14. Cunningham HM, Pontefract RD. Placental transfer of asbestos. Nature. 1974; 249:177-8.

15. Lawerrys JM, Baret JH. Alveolar clearance and the role of the pulmonary lymphatics. Am Rev Respir. Dis. 1977:625-83. 16. Brody AR, Hill LH. Interstitial accumulation of inhaled

chrysotile asbestos fibers and consequent formation of micro-calcification. Am J Pathol. 1982;109:107-14.

17. Viallat JR, Raybuad F, Passarel M, et al. Pleural migration of chrysotile fibers after intratracheal injection in rats. Arch Envi-ron Health. 1986;41:282-6.

18. Dodson RF, Williams MG, Corn CJ. A comparison of asbestos burden in lung parenchyma, lymphnodes and plaques. Ann NY Acad Sci. 1991;643:53-60.

19. Haque AK, Vrazel DM, Burau KD. Is there transplacental trans-fer of asbestos? A study of 40 stillborn infants. Pediatr Pathol. 1996;877-92.

20. Lippman M. Effects of fiber characteristics on lung deposition, retention, and disease. Environ Health Perspect. 1990;88:311-7. 21. Dodson RF, Atkinson MA, Levin JL. Asbestos fiber lenght as related to potential pathogenicity: a critical revue. Am J Ind Med. 2003;44:291-7

22. Roggli VL, Sharma A. Analysis of tissue mineral fiber content. In: Roggli VL, Oury TD, Sporn TA (eds). Pathology of Asbestos-associated Diseases. New York: Springer, 2004:309-54.

23. Wagner JC, Sleggs CA, Marchand P. Diffuse pleural mesothe-lioma and asbestos exposure in the North Western Cape Province. Br J Ind Med. 1960;17:260-71.

24. Vigliani EC, Mottura G-, Maranzana P. Association of pul-monary tumors with asbestosis in Piedmont and Lombardy. Ann NY Acad Sci. 1965;132:558-74.

25. International Agency for Research on Cancer (IARC). IARC monographs on the evaluation of the carcinogenic risks of chemicals to humans. Volume 14. Asbestos. Lyon, France: IARC, 1977.

26. Bertazzi PA, Piolatto G. Epidemiologia mondiale e italiana. In: Mesotelioma Maligno.Torino, Italy: Regione Piemonte Editore, 1985:18-31. [In Italian]

27. Scansetti G, Piolatto G, Pira E. Il rischio da amianto oggi. Torino, Italy: Regione Piemonte Editore, 1985. [In Italian] 28. Gardner MJ, Saracci R. Effects on health of non-occupational

exposure to airborne mineral fibers. In: Mignon J, Peto J, Saracci R (eds). Non-occupational Exposure to Mineral Fibers. IARC Scientific Publication No. 90, Lyon, France: IARC, 1989: 375-97.

29. De Vos Irvine H, Lamont DW, Hole DJ, Gillis CR. Asbestos and lung cancer in Glasgow and the West of Scotland. Br J Med. 1993; 306:1503-6.

30. Hillerdal G. Mesothelioma: cases associated with non-occupa-tional and low dose exposures. Occup Environ Med. 1999;56:505-13.

31. Browne K. Asbestos related malignancy and the Cairns hypoth-esis. Br J Ind Med. 1991;48:73-6.

32. Iwatsubo Y, Pairon JC, Boutin C et al. Pleural mesothelioma: dose–response relation at low levels of asbestos exposure in a French population-based case–control study. Am J Epidemiol. 1998;148:133-42.

33. Doll R., Peto J. Asbestos: Effects on Health of Exposure to Asbestos. London, U.K.: Health and Safety Commission, HMSO, 1985.

34. Selikoff IJ. Asbestos-associated disease. In: Rosenau M (ed). Public Health and Preventive Medicine. 11th ed. New York: Appleton-Century-Crofts, 1986: 568-98.

35. Motley RL, Patrick CW Jr, McGuiness Kearse A. Medico-legal aspects of asbestos-related diseases: a plaintiff’s attorney’s per-spective. In: Roggli VL, Oury TD, Sporn TA. Pathology of Asbestos-associated Diseases, New York: Springer, 2004: 355-401.

36. Illgren EB, Browne K. Asbestos related mesothelioma: evidence for a threshold in animals and human. Regul Toxicol Pharma-col. 1991;13:116-32.

37. Hodgson JT, Darnton A. The quantitative risk of mesothelioma and lung cancer in relation to asbestos exposure. Ann Occup Hyg. 2000;565-601.

38. McDonald JC, Armstrong B, Case B, et al. Mesothelioma and asbestos fiber type: evidence from lung tissue. Cancer. 1989; 63:1544-7.

39. Rödelsperger K, Woitowitz HJ, Brückel B, Arhelger R, Pohla-beln H, Jöckel KH. Dose–response relationship between amphi-bole fiber lung burden and mesothelioma. Cancer Detect Prev. 1999;23:183-93.

40. Rogers A, Leigh J, Berry G, Fergusond A, Mulder HB, Ackad M. Relationship between lung asbestos fiber type and concentra-tion and relative risk of mesothelioma. Cancer. 1991;67:1912-20.

41. Newhouse ML. A study of the mortality of workers in an asbestos factory. Br J Ind Med. 1969;26: 294-301.

42. Newhouse ML, Berry G. Predictions of mortality from mesothe-lial tumors in asbestos factory workers. Br J Ind Med. 1976;33:147-51.

43. Seidman H, Selikoff IJ, Hammond EC. Short-term asbestos work exposure and long term observation. Ann NY Acad Sci.1979;330:61-89.

44. Leigh J, Davidson P, Hendri L, Berry D. Malignant mesothe-liona in Australia, 1945–2000. Am J Ind Med. 2000;41:188-201. 45. Neumann V, Gunthe S, Mulle KM, Fisher M. Malignant

mesotheliona—German mesothelioma register 1987–1999. Arch Occup Environ Health. 2001;74:393-5.

46. Bianchi C, Girelli L, Grandi G, Brillo A, Ramani L, Zuch C. Eur J Cancer Prev. 1997;6:162-6.

47. Hutchings S, Jones J, Hodgson J. Asbestos related disease. In: Driver F(ed). Occupational Health. Decennal Supplement. The Registar General’s decennal supplement for England and Wales. London, U.K.: HMSO, 1995:127-48

48. Peto J, Seidman H, Selikoff IJ. Mesothelioma mortality in asbestos workers: implications for model of carcinogenesis and risk assessment. Br J Cancer. 1982;45:124-35

49. Goldberg M. Amiante et risque de cancer: relations exposi-tions–effets pour les popolations professionnellment exposees. Arch Mal Prof. 1999;60:278-85. [In French]

50. Browne K. Asbestos-related disorders. In: Parkes WR (ed). Occupational Lung Disorders. 3rd ed. 1995 revised reprint. Oxford, U.K.: Butterworth–Heinemann,1995: 411-504 51. Berry G, Newhouse ML, Wagner JC. Mortality from all cancers

of asbestos factory workers in east London 1933–80. Occup Env-iron Med. 2000;57:782-5.

52. Mowe’ G, Gylseth B, Hartveit F, Skaug V. Fiber concentration in lung tissue of patients with malignant mesothelioma. A case– control study. Cancer. 1985;56:1989-2093.

53. Tuomi T, Huuskonen MS, Virtamo M, et al. Relative risk of mesothelioma associated with different levels of exposure. Scand J Work Environ Health. 1991;17:404-8.

54. Berry G. Models for mesothelioma incidence following expo-sure to fibers in terms of timing and duration of expoexpo-sure and the biopersistence of these fibers. Inhal Toxicol. 1999;11:111-30. 55. Rogers AJ, Leigh MB, Berry G, Ferguson A, Mulder HB, Ackad M. Relationship between lung asbestos fiber type and concen-tration and relative risk of mesothelioma. A case–control study. Cancer. 1991;67:1912-20.

56. Davis JMG, McDonald JC. Low level exposure to asbestos: is there a risk? Br J Ind Med. 1988;45:505-8.

57. Pott F, Roller M, Ziem, et al. Carcinogenicity studies on natural and man-made fibers with intraperitoneal test in rats. In: Bignon J, Peto J, Saracci R (eds). Non-occupational Esposure to Mineral Fibers. Lyon, France: IARC Scientific Publication No. 90, 1989: 173-9.

58. Governa M, Amati M, Fontana S, et al. Role of the iron in asbestos-body-induced oxidant radical generation. J Toxicol Environ Health. Part A. 1999;58: 279-87.

59. Collins VP, Loeffler RK, Tivey H. Observations on growth rates of human tumours. Am J Roentgenol Radiol Ther. 1956;76: 988 60. Tannock IF. Biology and the tumor growth. Hosp Pract. 1983;

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61. Flora S, Vannucci A. La prevenzione primaria dei tumori. Pro-fessione: Sanità Pubblica e Medicina Pratica. 1996;4:46-53. [In Italian]

62. Cotran RS, Kumar V, Collins T. Neoplasia. In: Cotran RS, Kumar V, Robbins SL (eds). Robbins Pathologic Basis of Disease. Philadelphia, PA: W. B. Saunders, 1999:300-1.

63. Bregni M, Siena S, Bonadonna G. Principi di proliferazione cel-lulare. In: Bonadonna G, Robustelli G, della Cuna M (eds). Medicina Oncologica. Milano, Italy: Masson, 2000: 73-115. [In Italian]

64. Hansen J, de Klerk NH, Musk AW, Hobbs MST. Environmental exposure to crocidolite and mesothelioma: exposure–response relationships. Am J Respir Crit Care Med. 1998;57:9-75. 65. Roushdy-Hammady I, Siegel J, Emri S, et al. Genetic

susceptibil-ity factor and malignant mesothelioma in the Cappadocia region of Turkey. Lancet. 2001;357:444-5.

66. Saracci R, Simonato L. Familial malignant mesothelioma. Lancet. 2001;358:1813-4.

67. Thieme B. I sistemi di aspirazione localizzata per la bonifica degli ambienti di lavoro. Milano, Italy: Clinica del Lavoro Devoto, 1980. [In Italian]

68. Committee on Industrial Ventilation. Industrial Ventilation: A Manual of Recommended Practice. 11th ed. Michigan, Ameri-can Conference of Governmental Industrial Hygienists, 1970. 69. Plebani C, Di Luigi M, Caponi M. Efficienza di filtrazione di

filtri antipolvere utilizzati nei respiratori in funzione della gran-ulometrica dell’aerosol. Giornale degli Igienisti Industriali 2005;30:253-9. [In Italian]

70. Spurny Kvetoslav R (ed). Advances in Aerosol Filtration. Boca Raton, FL: CRC Press, 1998.

71. Chen CC, Lettimaki M, Willike K. Aerosol penetration through filtering facepieces and respirator cartridges. Am Ind Hyg Assoc J. 1992;53:566-74.

72. Chen CC, Lettimaki M, Willike K. Loading and filtration char-acteristics of filtering facepieces. Am Ind Hyg Assoc J. 1993; 54:51-60.

References

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