Document zQmyg81YGdO3ew99ZokEJaV86

jlltnn log. r. y sclero , h. Pallnd. s I. Spou- Coronary m pigeon. perimental .ry athero- tjchol. 68, (1968). udy. Exp. EXI'UHIMtMAI. \M) MOI l-< VI Ut P VI HOI (H.V 19. o>cl->5o (_I973) PLAINTIFF'S EXHIBIT SA-547 Experimental Studies on the Effects of Heated Chrysotile Asbestos and Automobile Brake Lining Dust Injected into the Body Cavities of Mice1 J. M. G. Davis akd S. W. Coniam Institute nf Occupational Medicine, Roxburgh Place, Edinburgh F.IIS OSU, Scotland Received February 20, 1978 A series of experiments with mice involving the intrapleural injection of chrysotile asbestos dust heated to varying temperatures up to 1000C suggests that the physical shape of the dust particles is more important than the altered chemistry of the dust. Chrysotile heated to no more than 400C produced dust samples containing many long fibers, and these samples resulted in large pleural granulomas. Chrysotile heated to more than 400C produced dust containing mainly particles of low aspect ratio, and these produced very small granulomas. The initial size of the granulomas was very closely related to the final degree of fibrosis found in the animals and, therefore, chrysotile heated to 400C or less was much more fibrogenic than when it was heated to higher temperatures. A sample of automobile brake lining dust was found to con tain very little recognizable chrysotile, and consisted mainly of particles with a low aspect ratio. When this dust was injected into the pleural cavities of mice it produced very small granulomas and little fibrosis. The discovery by Wagner et al. (1960) that exposure to asbestos dust was often associated with the production of mesothelial tumors caused concern about the possible pollution of the normal urban atmosphere by asbestos dust. Wagner had shown that very small doses were apparently sufficient to produce tumors in some cases and it was suggested that the use of asbestos products from ironing boards to brake linings might be liberating sufficient dust into the atmosphere to cause a health hazard. Since automobile brake linings arc constantly being abraded in use and since many tons of asbestos arc consumed in this manner each year, the possibility of atmosphere pollution from brake lining dust has received particular attention. In order to test the level of atmospheric pollution by asbestos a number of studies have been undertaken. The lungs from unselected autopsy cases from different parts of the world have been examined and initially, since uncoated asbestos dust is difficult to find in tissues, the presence of asbestos bodies was used as a likely index of the presence of asbestos. The figures obtained showed an increase in the percentage of cases containing bodies with the increasing sophisti cation of the techniques used. The first of these studies was that undertaken by : The dust samples used in this study were prepared in the laboratories of T.B.A. Industrial Products Lid. of Itochdale, England. Tin, work was' undcrl:ik< n as part of the research programe. organised by the British Wla-st-is-s IV -r orb Council. r :ialit > ! <7* t.y A-ui. -:ic I' >-- I-.-. All of repno'jetion in any fur;:, r^erved. `i 1 :;-iu DAVIS AND COXIAM Thomson ct al. ( 1963' in Capetown and these workers reported bodies in m<> t!ia:i 30', of cases. Later. Thomson and Graves (19661 found a similar prevalent, n Miami: Cauna. Totten, and Gross (1965 * found bodies in 40M of a series <u longs from Pittsburg and Anjilvel and Thurlbeck ( 1966) found them in 45'ol their cases in Montreal. Meurman (1966' reported finding bodies in 70'i of a group of lungs from Finland and finally. Utidjian, Gross, and De Treville (1968 > using a new technique, reported that the lungs of 97 out of 100 consecutive autopsies from Pittsburg contained bodies. However. Davis, Gross, and De Treville r 1970) showed that the production of ferruginous bodies was not spe cific for asbestos as had been previously believed and it therefore became neces sary to undertake new studies by which asbestos could be identified by precise methods. This is still a very difficult problem, although Danger et ai (1970 I and Pooley et al. (1970) base shown that chrysotile asbestos can be positively identi fied in a large proportion of the lungs of town dwellers. The initial concern over generalized atmospheric pollution by asbestos involve1'! the possibility of tumor production but the problem was given a new dimension by the work of Jagatic (1967). Jagatic reported that chrysotile heated to high temperatures was acutely toxic to mice and found that after the injection of heated chrysotile into the peritoneal cavity, 60'<" of mice died within 48 hr. Since chryso tile is the type of asbestos usually used in brake linings and since, during braking, the linings are heated to very high temperatures, it became necessary to consider the possible acute hazards of the inhalation of brake lining dust. In order to study the biological effects of heated chrysotile and brake lining dust in more detail it was decided to undertake a series of experiments in which samples of these dusts were injected into the pleural and peritoneal cavities of mice. In later studies it is hoped to undertake inhalation experiments with these minerals to see whether they should be considered as dangerous atmosphereie pollutants. MATERIALS AX'D METHODS The mineral samples used in these studies were prepared as follows: Samples of high grade Cassiar chrysotile asbestos were heated in an electric tube furnace for 4 hr at temperatures of e'thor 400"C, 60CFC, 8000G. or l.OOO'C. After cooling, the chrysotile was ground in a mechanical mortar and pestle and half of each sample was sieved through a 250-mesh copper sieve. With normal chrysotile and chrysotile heated to no more than 400`G many long fibers remained m the dust after grinding and since most of these were removed by sieving it was possible to produce samples both with and without long fibers. With chrysotile heated to more than S'OO C. however, the dust fibers became' extremely brittle and gr ading was found to break most ol these into relatively short lengths. With these sample's, therefore', sieving maele little' diffe'rencc to the1 size' distribution al die elust particle's although experiments were1 conelucteel with both sieve*el anel uns-'e've'el samples to test the'ir effe'ets on tissue's. The thermal ele'compeisitiem e>f ehrysotile lollows <i twei-stage sespiemce of ele!i\ elm\\ l.etiou .me! breakdeiwn. anel the me'chanism has been studies] by sewen al eithors 'uclneling Ball anel Tayleir 1963 anel Brinelley anel Hayami ( 1965'. The' !eh\drei\\ lation eif chrysotile- take's place in the1 temperature1 range' 600-780 G anel i 1 :k c of of of a 1965, cutive d Do I \polecex- 'ioo\o and Imrli eatcd irysoiking, isider Silling vhich os of these icreie ctric IOC. and irina! lined was a i tile and With n u! tml de era 'he and C.'ilHV.SOTILK ASBESTOS AND AUTOMOBILE BRAKE LINIXC DUST 541 at SOO-SoO C the dehydroxylalcd noncrystallinc residue is said to recrystallize (u give lorslcrile and silica. The total decomposition corresponds to Mg,, Si, 01U fOH.U 3Mg, SiO, Si02 + 4H, O The forsterite persists together with silica up to 1000"C but above this temper ature some enstatite is formed 3Mgs SiO, SiO. = 2Mgo SiO, 4- Mg. Si. 0,; Since the highest temperature used in these experiments was 1000:C it was the decomposition of chrysotiie to forsterite and silica that formed the basis of the present study. Throughout this paper the dust samples are referred to as heated chrysotiie lor simplicity. Readers interested in the exact chemistry of any partic ular sample are referred to the information in this paragraph. The sample of brake lining dust used in these experiments was supplied by a commercial producer of brake linings and had been taken from the rear brake drums of two of their test vehicles. These cars had been put through a test routine designed to simulate a long period of normal usage. The original brake lining composit.on was similar to that described by Lynch in 1963 and in addition to chrysotiie asbestos and binding resins the linings had contained both chromium oxide and metallic aluminium granules. It would normally be expected that brake lining dust would contain metallic iron from the brake drum, but an X-ray analysis of the dust sample performed by A. L. Rickards failed to detect crystalline iron on this occasion. With these samples of heated chrysotiie and brake lining dusts the following experiments were undertaken. In the first series, in order to confirm the results of Jagatic et al. (1967), doses of 250 mg of chrysotiie heated to 1000 C were injected into the peritoneal cavities of 25 Balb/C mice. In the second series of experiments single 10 mg doses of normal chrysotiie and chrysotiie heated to either 400C, 600 C, 5003C, or 1000C were injected into the pleural cavities of similar mice. Batches of 25 mice were used for each dust sample and both sieved and unsieved dust specimens were used in each case. In the final series of experiments single doses of 10 mg of automobile brake lining dust were injected into the pleural cavities of another batch of 25 Balb/C mice. In all cases the dust samples were suspended in 1. ml of sterile distilled water before injection. Animals from all these studies were killed at intervals from 7 days to 1 yr alter injection and samples of tissue from each were fixed in either formol saline lor light microscopy esummation or buffered osmium tetroxide for electron microscopy. For light m croscopy, sections were stained with either hematoxylin and eosin. E.P.S., or Peris' stain for iron. For electron microscopy, the tissues were embedded in uraldilc and after sectioning were stained with lead citrate. OBSERVATIONS In the first series ol experiments those animals '.liven an intraabdominal injec t on ol 250 mg of chrysotiie heated to 1000'C showed sisins ol toxic effects within 2t hr and by 45 hr seven had died. The remainder showed continuing signs ol disability for several days but all eventually recovered and none died within 6 mo of dust injection. When those mice that had died within 45 hr ol injection were :: 1-2 DVVLS VXD COXIAM ovaimned it was found tliat little or no cellular response had developed around the dust which remained scattered and loose in the peritoneal cavity. A histo logical examination of the viscera of those animals showed no signs of damage with the exception of some patchy hydropic change in the kidney tubules. When mice from tin's series were killed 7 days after dust injection it was found that the dust in the peritoneal cavity had by now become compacted into large gran ulomas. Most of these remained free in the peritoneal cavity, supported by strands of connective tissues, but some became attached to the surface of the omentum. It was only occasionally however that adhesions were formed between the loops of the intestine. Within the granulomas the cellular reaction to the dust consisted largely of macrophages with a few giant cells, fibroblasts, lymphocytes, and plasma cells and with the smaller lesions cells were able to penetrate throughout the dust mass. With a dose of 250 mg, however, some of the dust lesions were so large that complete penetration did not occur and the central regions of these granulomas remained completely acellular. By 2 wk after dust injection most of the granulomas were surrounded by a thin but clearly defined capsule of fibrous tissue and some collagen had been produced among the colls of the granuloma itself. A gradual increase in collagen was seen within the lesions between 7 days and I yr after injection but within this period the granulomas still contained many cells. In the experiments using 10 mg doses of either heated chrysotile or brake lining dust no animals died within the first 2 wk after injection and none showed any toxic effects. Granulomas were produced in response to all the injected samples but cellular reaction to the dust was found to vary according to the dust type, the temperature to which it had been heated, and its method of preparation. Animals injected with either normal chrysotile or chrysotile heated to 400C were found after 2 wk to have cellular granulomas with complete cellular penetration throughout the dust masses. In these lesions cells masked the dust to such an extent that it was extremely difficult to see with the light microscope. In the animals injected with chrysotile ground and sieved the granulomas were relatively small and formed few adhesions, but in those animals injected with unsieved dust the granulomas were much larger for the same dust dose and frequently formed adhesions between the contents of the chest cavity. In animals injected with dust heated to 600~C cellular granulomas were still produced but there appeared to be less dilference between the sieved and the unxieved dust groups, and both produced only small granulomas without adhesions, fn the groups of animals injected with chrysotile heated to either $00 or lOOO'C the resulting granulomas were always small compared with the dust dose used and no adhesions were found in either the sieved or the unsieved group. In these experiments, however, it was lound that the chrysotile dust was now clearly visible in the tissues and in the light microscope appeared to consist o| cylindrical or rectangular particles which ranged irom 1 to Khun in diameter and which could be up to 50/un in length. Normally cells were still able to penetrate throughout the dust masses but fewer cells were present than in granulomas produced h\ normal chrysotile. By 2 wk alter dust injection a thin capsule of fibrous tissue was usually formed around those granulomas remaining free in the pleural cavity. Those that formed adhesions, however, did not develop ans specific laser ol fibrous tissue between the main granuloma and the organ to which tin s sw-io attached. By 2 wk, also around To- lailiage When hat the granstrands cntuin. loops usisted s, am1 IghfllV . ore s these lost ol fibrous uilonia 7 days many lining d any unples . type, ration. ' "'ere on tcii an la the itively d dust orined h dust ! to be both ninials ilomas found it was in the whicli ength. fewer irmed irmetl tween \ also CHRYSOTILE ASBESTOS AMD AUTOMOBILE BRAKE LIXI.VG DUST 34b' tW'. $4 .-<o\ '<W >v;#. r* * 'fib-'t' "v -fejjT u*S. Fit:. 1. A .section of a macrophage from a mouse granuloma 2 wk after an injection of chry sotile asbestos heated to 600'C. Croups of chrysotile crystals' are seen in two phagosomes <P/ within the cell, and the structure of these crystals appears normal. In both cases, the dust appears loosely ananged in the phagosomes and the phagosome membrane has not at this stage contracted closely around the dust. X 65,000. some collagen was usually present among the plagocytic cells that made up the main part of the lesions. During the first lew weeks after injection collagen pro duction was more rapid in those granulomas induced by chrysotile dust heated to 300;C or more, than in granulomas resulting from cither unheated chrysotile or chrysotile heated to no more than 600'C. However, by 6 mo after injection this distinction was no longer apparent, and the long-term production of collagen in auv given area of granulation tissue did not appear to differ much between similarly prepared chrysotile samples that had been heated to different temper atures. The physical shape of the dust particles did, however, have considerable effect on fibrosis. The total amount of collusion produced in response to a 10-mg dose was closely related to the size ol the resulting granulomas and since unsieved samples heated to no more than 400 C produced large lesions these samples were more fibrogenic than sieved samples heated to 400 'C or to samples heated to higher temperatures. All these produced very small anmulonias. Electron microscope studies showed that almost all the injected dust from samples heated at 600 C or less was phagneyloscd In imu ropliages and occasional giant cells and lew estr.icellulai dint particles were louud. The process ol Oil DAVIS AND CONIAM im -fair-* m At Fit;. 2, A section of a mouse granulomas } \vk after the intrapleural injection of clirysotile dust lieated to 800'C A large bundle of fused clirysotile crystals has been pbagocytosed by a macrophage tM), and the phagosome membrane is in close contact with the dust (arrowed'. Although the clirysotile crystals are partialis fused with one another, tin1 original crystal outline is still discernible. X 65,000. phagocytosis and the subsequent behavior of the dust within cells appeared identical to that reported previously (Davis, 1968, 1970a). Dust particles were initially taken up into large vacuolated phagosomes (Fig. lb but the membranes of these eventually contracted and became closely opposed to the dust particles. Usually the dust remained on its own inside the phagosome membrane, but occasionally it was found mixed with ferruginous granules and membrane debrisin the dense structures that are known as phagosome residual bodies. Most of the dust remained in those structures, but occasionally an odd fiber was found that appeared to have escaped into the cell cytoplasm. The macrophages from these experimental groups showed no signs of damage even when they contained large amounts of dust. Xo differences could be detected in the structural appearance ol crystals of normal clirysotile and clirysotile crystals that had been heated to 400'C. With dust heated to 600 `C. however, it yva.s noticeable that the phagocytosed dust, yvhether sieved or unsieved. contained more indiiidual clirysotile crystals than crystal bundles, and many phagosomes yvere hnmd closely [lacked yvith inch vicinal crystals. Electron microscope examination of lesions produced by clirysotile heated to 800 C or 1000 C shoyved yvliy the dust yvas dearly visible in these lesions even yvith the light microscope. Durum the heating jinx ess the individual CHI chrysob' crystals the crystals large masse each. When original out detected (Iwas no Iondissolution by an irrtu masses wetno greater macrophag although d more ' = i macro; . m behay i*>r normal chi Suid and t .. I- ,}i ,, dust pa^ick ^ :ioindi & - 70,000. CHKVSOTILK ASBESTOS AND AUTOMOBII-K BKAKI' l AS ISC. OUST Tin clir\ so tile crystals lmd lost their normal tubular structure and fused with the other crystals in the- bundle ( Rickards. 1967). This fusion was complete enough to hold the crystals together during grinding so that the dust was broken up into relatively large masses rather than fine fibrous bundles often containing only a few crystals each. When the tissues were examined only a few weeks alter dust injection the original outline of the chrvsotile crystals within the fused masses could still be detected ( Fig. 2), but several months after dust injection this crystalline structure was no longer visible. It appeared that the dust had undergone some degree of dissolution within the tissues, and the neat crystal arrangement had been replaced by an irregular honeycomb structure (Fig. 3). Although the fused chrvsotile masses were much thicker than normal chrvsotile dust particles, most of them had no greater length, and the majority could still be phagoevtosed by single macrophages. Very large particles were occasionally seen inside giant cells although these cells are not common in mouse granulomas (Davis, 1970b), and more frequently the larger particles were closely surrounded by unfused macrophages. Inside the cells there were some notable differences between the behavior of the heated chrvsotile masses and normal chrvsotile. Particles of normal chrvsotile are taken up into large phagosomes which presumably contain fluid and the phagosome membrane is often well clear of the contained dust, at ehrysotile ' by .1 ed). tl outline ppeared es were nbranes 'articles, ne, but ' i debris t of the ;nd that n these tl large anee of <Kxrc. O^tosed Is l-'n.. 5. A section of a macrophage from a mouse granuloma 3 mo after `.lie injection of chrvs ole dust heated to SOU C. The macrophage is surrounded by collagen fibers ' Ft. but a large particle of fused chrvsotile O is piesent within the < yloplasm. In this ease, however, the norma! crvst.d on'ime has been lost .old has bee;, p-p!a<ed 1,,. ,,, uT'-guio' honevcomh pattern. 7(1 00(1. .SIC) DAVIS AND COXIAM nn granule; , by thin -a;., could be s. diameter. b from 2 to 2 were able t always eon quickly sur injection, a` within 2 wi lesions bee been bouugranuloma' to till' (lust Fig. 4. Particles of chrysotile dust within a macrophage from a mouse pleural granuloma, 3 mo after dust injection. The dust had been heated to 800C before injection, and by this stage the chrysotile crystal pattern has been replaced by an irregular honeycomb structure. The largest dust particle (P) is associated with masses of dense granules (F) that probably represent ferritin, or haemosiderin, and in some areas these have penetrated deeply into the dust. X 35,000. least in the early stages. With the masses of heated fused chrysotile however, al though they were taken up into membrane bounded vesicles the membrane was always seen in close contact with the dust. Many of the small dust masses could still be taken up by single macrophages which usually showed no signs of damage. In these granulomas, however, it was not uncommon to find dead macrophages containing dust although such dead macrophages have only rarely been found in lesions produced by normal chrysotile. In animals injected with either unsievcd normal chrysotile, or chrysotile heated to 400C some typical ferruginous bodies (Davis, 1970b) were found in the gran ulomas from about 2 wk after dust injection. Sieved samples of normal chrysotile and. chrysotile heated to 400 ~C did not, however, result in the production of any ferruginous bodies. This was also true of both sieved and unsieved samples oi chrysotile heated to 600C. In animals treated with chrysotile heated to either S00`C or 1000'C no due asbestos bodies were found in which the dust particles were surrounded by a distinct coating of ferruginous material. However, with some of the larger chrysotile fragments, especially those showing the greatest degree of dissolution, it appeared that dense granules similar to ferritin or haemosiderin had penetrated deep into the dust ( Fig. 4 '. Brake lining dust when injected into the pleural cavity of mice produced smaller granulomas than any of the asbestos types used in this study and these t ( ..A t' & 'v-1 v- CHRYSOTILE ASBESTOS AXD AUTOMOBILE BRAKE LINING OUST .147 granulomas never formed adhesions, being mainly suspended in the pleural cavity by tliin strands of connective tissue. In the light microscope the brake lining dust could bo seen to consist mainly of irregularly shaped particles 5-25 /xin in diameter, but a number of elongated particles were also present which ranged from 2 to 25 /on in diameter and which could be up to 50 jun in length. Cells were able to penetrate deep!}' into the dust masses but the number of cells was always comparatively few compared to the dust load. The granulomas were quickly surrounded by a thin capsule of fibrous tissue within a few days of injection, and some collagen had been produced among the dust containing cells within 2 vk. After this time collagen production increased quite rapidly and the lesions became less cellular so that 1 yr after injection the dust particles had been bound together bv a network of old acellular collagen. Since the initial granulomas were so small, however, the amount of collagen produced in response to the dust was never very great. tnuloma. by thisructurc. dil* , ft v'er, al oe was . could image, phages found heated granvsotile it me. lies a', eitln rticli with c.itest tin or inccd these Eu.. A. A particle of automobile brakt* lining dust within a macrophage* from a ni* pleural granuloma 2 wk after dust injettion. The dust i- separated from the cell cstoplasimi by a membrane but this is (losely opposed i the du-l it o point-; arrowed . The dust consists mainly of iIum- amorphous miti rial, and contain- no re< omu/.nlile rhrssotile i-hestos. There arc. how< >.< r. within *h du-t - iuc i< - .!>-' dim-- ii.ir'u !< - *h o prohahk :> p:< -cut metallic dummoni \ . OtJ.OOtl. :;is DAVIS AN'D CONIAM Electron microscope studies showed that the brake lining dust consisted main of dark masses showing no internal structure and containing no recogniza!-.'. chrysotile. In most cases the only contaminants within the dust masses wen smooth crystalline particles usually about 0.05 of a micron in diameter (Figs. 5 and 6). Since metallic iron was not present in the original dust sample these were probably particles of metallic aluminum added to the original brake lining mivture as an abrasive. Very occasionally dust particles were found that consisted of a lighter and more homogenous material which contained in addition to the crystalline particles already mentioned elongated crystals of apparently normal chrysotile (Fig. 7b This type of dust, however, made up much less than lb of the total. Small dust particles were phagoeytosccl in large numbers by single macrophages but as with chrysotile heated to high temperatures normal phago some vacuoles were not seen even in specimens examined only a few days alter dust injection. The phagosome membrane contracted quickly around these smaller dust particles to form phagosome residual bodies, and these often contained sour ferruginous granules and membrane debris as well as dust (Fig. 6b The larg, dust fragments were sometimes found within small giant cells, but as with heated Fie. T of this <!are emlir parlieles chr\ -of extr.a-e'' granule; graniil: The | of asbel m ('ssir and We to luagt to bet i sa-'ples fit Hu h- u.d usi.sled niainlv recognizable musses were sieter ( Fitts. 5 )le those wore m` lining iui\it consisted n! hlition to III. reiitly norm d s tluin 1'- ers by sine ,ormal pliaa w days alb ; these smaller mtained some :. The. larger s with heated CHRYSOTILE ASBESTOS AX'D AUTOMOBILE BRAKE LIXIXU IX'ST 549 'MU tit IlJto 4J i?* '<tu ;l i-oii.- - Fio. 7. A particle of brake lining dust within a mouse macrophage 2 wk after the injection of tin's dust. In this instance the dust consists of low density amorphous material within which are embedded recognizable crystals of chrysotile asbestos- < C} and larger nonfibrous crystalline paitides that probably represent metallic aluminum (. A. a 63.000. chrysotile many of the larger particles although surrounded by cells, remained extracellular. Dead macrophages containing brake lining dust were found in the granulomas at all stages of the experiment, but they were less frequent than in granulomas produced by chrysotile heated to either SOCPC or lOOCFC. . DISCUSSION The present studs' has confirmed previous suggestions that the physical shape asbestos particles is important in determining the degree of fibrosis produced u t ssuos. Ses'eral workers ineluding King cl al. ; 1946'. Yorwald et al. (19511. and Webster 1965 > have' suggested that long fiber asbestos is more fibrogenie ( hmg (issue than short fiber dust and Davis in 1972 showed that this also applied to dust injected into the pleural cavity. It was found in this work that long fiber samples ot a number ot mineral dusts produced much more fibrosis than short fiber dust. In the studies using heated chrysotile it was found that if the dust was heated to no more than 400 C mechanical grinding still produced dust contain ing a large proportion o! long fibers. When normal ohrvsolile is finely ground `die original crvstal bundles tend to split longitudinally rather than transversely and then !or< very long thin libers are produced. Sieving tins dust removes most 350 DAVIS A\:D CO XIAN I of these long fibers and it was therefore possible by using both sieved and unsieved dust samples to gain some idea of the effect of fiber length on the tissues. It was found that the long fiber samples produced larger granulomas than the short fiber dust and since the amount of fibrous tissues produced depended on the initial size of the lesions (Davis 1972) long fiber dust was more fibrogenic than short. When dust was heated to 600C the structure of the chrysotile crystals appeared unchanged in the electron microscope but the ground dust samples contained few long fibers. It appeared that the crystals were more brittle than normal chrysotile and that in most cases the bonding between the crystals had been weakened. This was probably associated with the gradual dehydration that occurs when crysotile is heated from between 100'C and 600CC. Grinding this type of dust tended to break it into individual short crystals and there was little differ ence between sieved and unsieved dusts. Since few long fibers were present both samples resulted in the production of small granulomas and little fibrous tissue was produced compared to the size of the dust dose. When chrysotile was heated to 8003C or 1000C the individual crystals fused with one another and the fused bundles remained brittle. When these samples were ground the original large bundles of chrysotile crystals fractured transversely as one unit and the resulting dust consisted of thick, but short particles- Sieving this dust did not change the particle size distribution and both samples produced very small granulomas resulting in relatively little fibrosis. With the brake lining dust the particle size distribution was very similar to chrysotile heated to S00C or more. Some, enlongated particles were present but these always had a very low aspect ratio. Since very little of this dust could be recognized as chrysotile even with the elec tron microscope, the results are not directly comparable with heated chrysotile but very small granulomas were produced in response to brake lining dust and little fibrosis resulted from its injection. The first group of experiments in this study confirmed the suggestions of Jagatie ct al. (1967) that chrysotile asbestos heated to high temperatures is far more' toxic than normal chysotile. It would appear, however, that very high doses are needed to produce a lethal effect and after a 10 mg dose none of the mice showed any signs of disability. This 10 mg dose for mice corresponds to one of approximately 30 g for a 12 stone man and this is an impossible figure for anyone to take in by inhalation over a short period even under the worst industrial conditions. It is very unlikely, therefore, that this toxic effect of heated chrysotile need be considered seriously when dealing with the problems of general atmos phere pollution by this type of asbestos. From the experimental point of view, however, the reasons for this toxicity are of considerable interest. It has been suggested that when chrysotile is heated to more than SOO'G free silica is liberated in the amorphous state, and several workers hav e shown that this can be lethal. Gye and Purdy (1922' demonstrated that colloidal silica was rapidly fatal to experimental animals when injected intravenously and Dale and Kiwi 1953" produced similar results. These workers found that colloidal silica waten times more toxic than crystalline quartz in these conditions. Klosterkotter and Totten '19531 also showed that molecularly dispersed silica, whether administered 'ufr.icheally or intraperitoneally was lethal to rats, ft therefore seems possible that the (' acute Reg.u heated f toxicity using th 1970a1 1 With he quite ("is percent distinct otile. V for soon tore c`i (Dapha>_ macro p; granhio' and brai membra it would sible In: residual to the r. Mark cst deg) to maei cause t' able t< red) e T- o normal 1964 fii from si! in the-.c rosultin. initial^ length.! nlomast dust c>* the total l'lie I is uico| h ike f , . -sotM lining { iespo4 .ppeare.d mtaincd normal ad been it occur type <. e differ ait both is tissue v heated he fused ial large 'csulting tnge the milomas icle sizi' e. Some ct ratio, the elec- otile lust and f Jagatic id King 'ica was tter and nistered ble that CHRYSOTILE ASBESTOS AND AUTOMOBILE BRAKE LINING DUST 351 the deaths of animals given large injections of heated chrysotile were due to acute silica poisoning. Regardless of general systemic toxicity, however, it was found that chrysotile heated to 800:C or more and brake lining dust both showed much more cyto toxicity for individual macrophages than normal chrysotile. In a previous study using the intrapleural injection of chrysotile in experimental animals (Davis, 1970a 1 it was noted that it was very rare to find dead macrophages in the lesions. With heated chrysotile or brake lining dust, however, macrophage death was quite frequent although dead macrophages never made up more than a few percent of the total. Even the fix ing macrophages from these granulomas showed distinct differences from those in lesions produced in response to normal chrys otile. When normal chrysotile is phagocytosed by macrophages it is retained for some time in a large phagosome vacuole before the membrane of this struc ture contracts around the dust particle. It was shown in organ culture experiments i Davis. 1968) that this process could be completed in as little as 12 hr after phagocytosis but this must be rare and after intrapleural injection of chrysotile macrophages with vacuolated dust containing phagosomes could be found in the granluomas for several weeks. With chrysotile heated to S00C or more, however, and brake fining dust, vacuolated phagosomes were never seen and the phagosome membrane was always closely opposed to the dust particle. From these findings it would appear that chemical differences between the dust samples are respon sible for quicker contraction of the phagosome membrane and the formation of residual bodies, and it is interesting to consider whether this property was related to the raised content of amorphus silica in the heated samples. Marks et al. (19561 showed that whereas amorphous silica produces the great est degree of systemic toxicity, the crystalline varieties are more rapidly cytotoxic to macrophages. It may be. however, that while noncrystallinc silica is unable to cause the rupture of phagosome membranes (Allison et ah, 1965) it is nonetheless able to increase the permeability of most phagosome membranes enough to reduce phagosome contraction time. The finding that chrysotile heated to more than 600C is more cytotoxic than normal chrysotile yet results in less fibrosis appears to contradict Heppleston's 1964 finding that macrophage death is an essential precursor to fibrosis resulting from silica dust. In fact, however, two conflicting factors are probably involved in these findings. It has been found (Davis, 19721 that the amount of fibrosis resulting from the injection of mineral dusts closely corresponds to the size of the initial cellular response to the dust and this in turn depends largely on the fiber length. Since the heated chrysotile contained no long fibers the resulting gran ulomas were very small and although macrophage death resulting from increased dust v> totoxieity probably accelerated the production of collagen in these lesions the total collagen production was never very large. The finding that automobile brake fining dust has a very low fihrogenicity is encouraging, but the initial concern oxer the pollution of the atmosphere by brake lining dust concerned its possible association xxdth the production of mesotheliomas, and the present study has not settled this point xvith certainty. Xo tumors xx'ore found in animals injected xvith either heated chrysotile or brake lining dust but the experiments xxerc mainly concerned xvith the initial tissue response to the dust and were terminated alter 1 \r. It noxv knoxvn. howex-er. 352 DAVIS AND CON'IAM that whereas intrapleural injection of asbestos in rats produces large numl mesotheliomas (Wagner, I960) few arc produced by similar injection in - Davis, unpublished) and so no significant results would have been produced I rom prolonged experiments of this type using brake lining dust. It is planned to undertake new series of experiments that will test the long-term effects of brake lining dust in conditions where normal ehrysotile is known to produce tumors. At this point, however, it may be pointed out that electron microscope studies of lesions produced in response to brake lining dust have shown that this dust contains extremely little recognizable ehrysotile and what there is is mostly embedded in the plastic bonding material. No computation of urban atmospheric pollution by ehrysotile from this source can therefore be made by calculating brake drum wear. REFERENCES Allison, A. C., Harincton, J. S. Birueck, M., and Nash, T. 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The effects of ehrysotile asbestos dust on lung macrophages main tained in organ culture. Brit. J. Exp. Pathol. 48, 379-385. Davis, J. M. G. (1970a). The long term fibrogenic effects of ehrysotile and crocidolite asbestos dust injected into the pleural cavity of experimental animals. Brit. J. Exp. Pathol. 51, 617-627. ' Davis, J. M. G. (1970b). Further observations on the ultrastructure and chemistry of the formation of asbestos bodies. Exp. Mol. Pathol. 13, 346-358. Davis, J. M. G. ( 1972). The fibrogenic effects of mineral dusts injected into the pleural cavity of mice. Brit. J. Exp. Pathol. 53. 190-201. Davis, J. M. C., Gross, P., and De Treville, R. T. P. (1970). Ferruginous bodies in guinea pigs. Arch. Pathol. 89, 364-373, Ericsson. J. L. E., and Trump, B. F. (1964). Electron microscopic studies of the epithelium of the proximal tubule of the rat kidney. Lab. Invest. 18. 1427-1456. Gye, VV. E., and Purdy. W. J. - 19241. Poisonous properties of colloidal silica. Brit. J. Exp. 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