Document JN4ypwy6GaqpzKkM74ORBxYnK

m ASBESTOS INFORMATION ASSOCIATION NORTH AMERICA 1835 K Street, N.W., Washington, D C. 20006 (202) 223-4885 22 July 1976 Memorandum For: Subject: John Marsh John Riopelle Erich Feierabend Edward R. Zacharias y Advance of Mt. Sinai School of Medicine Article on Brake Lining Maintenance and Repair Attached galley proof of article prepared by Mt. Sinai School of Medicine (N.Y.) staff and scheduled to appear in the August issue Environmental Research and Gynecologic Oncology is forwarded as a matter of interest. This study was cited as the primary reference for the NIOSH "alert" issued August 1975 (distributed to members) calling attention to potential health hazards to workers exposed to asbestos dust during servicing of brake and clutch assemblies. The "alert" received nation-wide publicity. Ed Drislane, executive director. Friction Materials Standards Institute, was advised by Dr. Selikoff that the brake lining repair aspect of the asbestos-health question "is going to become a major project." We are seeing increasing evidence to substantiate that remark. Mr. Drislane1s memo randum on subject to FMSIT asbestos study committee is also attached. Attention is invited to the AIA/NA leaflet, "Asbestos and Brake Linings" and the apparent need to review this publi cation in the interests of current and positive addressal to subject. Your comments will be appreciated. R. H. Mereness Executive Director cc: ' es Armstrong, Stan Christian, Bendix Corp. W. Drislane, FMSI Enclosures FMSI 06786 .FRICTION MATERIALS STANDARDS INSTITUTE, INC., E-210 ROUTE 4, PARAMUS, N. J. 07652 July 15, 1976 To: Asbestos Study Committee Subject: Mount Sinai (Dr. A. N. Rohl) Paper: "Asbestos Exposure during Brake Lining Maintenance and Repair" On February 6, 1976, I advised the Asbestos Study Committee that I had received a paper entitled "Asbestos exposure during brake lining main tenance and repair" from Dr. A. N. Rohl of Mount Sinai. You may refer to my February 6, 1976 covering letter, I have now received from Dr. Rohl copies of page proofs of that article as it will appear. Dr. Rohl believes, in the August 1976 issue of Environmental Research. This is essentially the same paper presented by Dr. Rohl at the May 1974 meeting of the American Conference of Governmental Industrial Hygienists (AGGIH). It has been up-dated and expanded to include papers in 1974-75 for reference. In reviewing this, I do not believe his figures include fiber counts of asbestos longer than 5 microns on an 8 hour time weighted average (TWA) basis. The emphasis continues to be turning to asbestos fibers shorter than 5 microns and their measurement by other than optical microscopy. ELD/ere Enc: E. IV. Drislane Executive Director FMSI 06787 t -S Item ; Asbestos Exposure during Brake Lining Maintenance and Repair1 : Arthur N. Rohl, Arthur M. Lancer, MaryS. Wolff, and . Irving Weisman Environmental Sciences Laboratory, Mount Sinai School of Medicine of the City University of New York, New York, New York 10029 Received December 10, 1975 . i Data obtained on asbestos exposure of garage mechanics during brake lining maintenance , and repair work show that fiber concentrations frequently in excess of regulated limits are i ' common. The presence of chrysolite, ranging from 2 to 15%, in brake drum dusts, was i demonstrated by X-ray diffraction, transmission electron microscopy, selected area electron t diffraction, and electron microprobe analyses. Unaltered chrysotilc was found, both in Tiber t and fibril form, in air and brake drum dust samples. The chrysolite asbestos content of i personal air samples, taken during automobile brake repair work, was measured both by optical and electron microscopic techniques. While a positive correlation exists between the lypes of measurements, the present technique oT optically counting asbestos fibers may considerably underestimate the levels of total asbestos exposure. ENVIRONMENTAL RESEARCH and GYNECOLOGIC ONCOLOGY ; INTRODUCTION During the past decade, significant disease risk has been found associated with the inhalation of asbestos fibers in a number of occupational and environmental circumstances other than in asbeslos mining, milling and manufacturing, where serious hazard was already known (Wagner el til., I960: Ncwhouse and Thompson, 1965; Selikoff et al., 1964, 1965; Harries, 1968). Such exposures were found in the construction industry and in shipbuilding, as well as in other industrial settings where asbestos products were used. More recently, asbeslos exposure has been suggested to occur during automotive brake lining repair and installation work, and measurable concentrations of asbestos fiber were observed in the work environment of workmen involved in these opera tions (Hickish and Knight, 1970; Hatch, 1970; Boillat and Lob, 1973). With limited data available, however, uncertainty remained regarding the type and extent of asbestos exposure during this work. Some investigators have questioned whether free asbestos fibers survive the high temperatures produced during braking action (Lynch, 1968; Hickish and Knight, 1970; Hatch, 1970) contending that asbestos decomposes as a result of the high point contact temperatures produced at the interface of the brake drum or disc and brake lining. ' We have sought to obtain information concerning asbestos exposure of work men engaged in brake lining maintenance and brake shoe installation, by analysis of residual dusts recovered from brake linings and by direct measurement of the !'1 I*I Thisresearch wassupported by Center Grant ES 009E8 of the National Imtiatte of Environmental ! Health Sciences of ihc U.S. Department of Health. Education and Welfare. Assistance was also j provided in part b> the Health Research Council of the City of New York HRC U 2}2\) and by the i Ford MotorCompany. ! Cop.Ti^ht p- l9J6b> Aui lean-: Prcv Itw Al! of repfi-luction ir. jny form revcrvtrJ no ! i;iF0W*T0N ASSOCIATION/ f.'a'fri Amsfica 1S35 Nb-L'ri, i!. XI. Suits *t02 Wa3::inaicn, 0. C. 2G0CS FMSI 06788 4IEAD . in free asbestos fiber content of workroom air in areas where these operations take place. In the United States, an estimated work force of at least 900,000 auto mechanics and garage workers is potentially exposed to asbestos in the servicing of both brake and clutch linings. Furthermore, much brake dust enters the general environment during automobile use (Jacko and DuCharme, 1973). to add more to the burden of asbestos air pollution (Selikoff, Nicholson, and Langer, 1972). Asbestos in Friction Materials In the United States, an estimated 118 million pounds of asbestos is used annu ally for the production of brake friction materials (Jacko and DuCharme, 1973). After processing (cutting, grinding, punching), the asbestos in the material sold is approximately 103 million pounds per year. In addition, asbestos contained in automotive dutch friction materials amounts to 4.5 million pounds annually. . Major Constituents of Brake Linings ' A number of materials is commonly used in the manufacture of the three major automotive brake lining components (binder, fiber reinforcer, and property mod ifier). These are listed in Table 1. . Binder. The binders used in the automotive industry today axe primarily phenolic-type resins, which are noted for high binding efficiency and ability to withstand pyrolytic breakdown. Other materials have been used, in varying pro portions and in addition to resins, for binder improvement (Table _1-L TABLE I Common Components of Automotive Brakf. Linings'* Binder and organic Friction modifiers Fiber reinforcer . Properly modifier Phenotic-type resin Rubber Tire scrap Pilch Corl> Gilsonile Cashew nutshell resin and particles Drying oils Chrysolite asbestos* (grades 4-7) Unaltered Calcined Mixed fiber Lead compounds Zinc compounds Antimony oxide Iron oxide Copper metal Brass chips Clay minerals Barite (BaSO.) Wollastonite (CaSi03) Quartz (SiOj) Cryolite {Na,.-MF,t Rottenstone (SiO.) Coke(C) Coal tC) Gikonite (C) Graphite (C) Carbon black iCl Mol>bJemini st.IRde (MoS.) Fluorspar (CaFd . " See Carroll. 1962; Anderson. 196'); Anderson. 1973; Jacko and DuCharme. Bark, ct of.. 19.5. ChryMuik* fiber constitutes about 50'-7 b> weight of most nutomotisc brakes currently manufac tured in the United States. iCOf i RIGHT GYNEC FMSI 06789 Fiber. For fiber reinforcement of the friction product, chrysotile asbestos is " : used almost exclusively. The mineral typically comprises from 40 to 50% of the j - brake product. Fiber grades 4 through 7 are used, and occasionally, several sizes; are admixed or even calcined to improve performance characteristics, j Modifiers. Perhaps the widest range of materials used in friction products are I the property modifiers. Nineteen representative compounds are listed in Table I. Modifiers are used for a number of purposes; they are included to increase brake 1 shoe "density," making the brake surface able to withstand high pressures (e.g., ^ | barite); they are included as "lubricants" to reduce the coefficient of friction ; along the brake surface, and thereby prevent "grabbing" (e.g., lead compounds); | they act as "friction agents" increasing the coefficient of friction and enhancing j the braking action of the shoe (e.g.. brass chips); they act as internal "abrasives," I which help to "recondition" the braking surface and remove deposited decomposj ition products (e.g., rottenstone, quartz); they act as "heat sinks," reducing bin- der pyrolysis and fiber decomposition thereby extending the useful life of the lining (e.g., brass chips, metals, etc.). It is important to note that one major purpose of the reconditioning agents is to retard the formation of forsterite (a mineral not originally present in the brake material, but created by dehydroxylation and recrystallization of chrysotile asbes- ' tos at high temperatures) which may accumulate on the surface of the brake lining. The hardness of the forsterite (Mohs, 6.5-7.0) is such that it tends to score and gouge brake drums and discs (hardness 3-3.5), degrading them prematurely, j Therefore, recrystallization of chrysotile to forsterite is an unwanted effect, hin| dered insofar as possible by the modifiers present in the matrix. j Materials of Biological Interest Asbestos, quartz, and heavy metals are constituents of automotive brake lin ings, each warranting special consideration from the viewpoint of biological activ ity. The focus of this report is limited to the problem of chrysotile asbestos exposure. Mechanisms of Degradation of Brake Linings during Use Brake wear is dependent upon many factors, such as the temperature generated at the surface of the brake shoe during braking operations. At any one time, only a small percentage of the rubbing area is in contact with the wheel, with "hot spots" generated, ranging up to 800 to I000C (Carroll, 1962; Anderson. 1969). It is not uncommon during moderate braking action, to attain temperatures as high as 500'C (Carroll, 1962). Some investigators have suggested that, in addition to bin der pyrolysis, chrysotile completely dehydroxylates under these conditions and j"reduces to powder" where it is swept off the brake facing (Carroll, 1962). Howjever, this hypothesis is oversimplified, in that other important processes, besides .thermal wear, contribute to shoe breakdown, and brake shoe degradation. (BurIwell. 1957). For example, the effects of abrasive wear and macroshear have been investigated. When monitored by X-ray diffraction, chrysotile in brake materials displays structural strain and substructure fragmentation, caused by shear during braking processes (Mizutani et a!.. 1973). This shear strain produces material fatigue which, with binder pyrolysis, can cause brake lining disintegration at corYiuom FMSI 06790 ENVIRONMENTAL RESEARCH a n d GYNECOLOGIC O N C O lOGY .{n^0. . ! 113 temperatures far below those requiredfor chrysolite dehydroxylation. Therefore, brake lining disintegration may liberate partially altered, or unaltered, chrysotile - fibers. Thermal Decomposition of Chrysotile Differential thermal analysis indicates that chrysotile undergoes dehydroxyla tion at 650 to 680'C and recrystallizes (anhydrous magnesium silicate to Torsterite) (Mg.SiO.,) at about 810 to 820C (e.g., Martinez, 1966; Daykin. 1971; Berry, 1971; Monkman, 1971; Harris, 1971). These temperature ranges are subject to great variation as a function of the chemistry of the fiber, particle size, instrumental variations, sample packing, etc. Also, forsterite has been noted to form, during prolonged static heating, at considerably lower temperatures (Bates and Comer, 1957; Martinez. 1966; Brindley and Hayami. 1965; Naumannand Dresher, 1966). In general, temperatures in excess of 570SC are required for dehydroxylation and incipient forsterite formation in chrysotile. Extensive study of both the thermal behavior of chrysotile and brake lining composition and design indicates that chrysotile fiber may survive in the decomposed lining dust. ' METHODS * Analysis of Brake Drum Dust (Decomposed Lining) Ten samples of automobile brake drum dusts were collected and examined by optical microscopy. X-ray diffraction, transmission electron microscopy and scanning electron microscopy with microchemical capability, for the purpose of determining the presence or absence of chrysotile.2 Optical microscopy, employing polarized light, was generally not useful for detecting asbestos in brake drum dust. A number of factors are considered re sponsible for this phenomenon including the low relief and birefringence of chrysotile and the nature of the matrix, consisting largely of road dust, resin binder, and pyrolyzed residue, which, in optical microscopic preparations, readily obscures the smaller asbestos fibers. X-ray diffractometry. in the continuous and step-scan mode, was performed on all dusts. Chrysotile reflections (hkl = 002; 020; 004) were observed in all ten samples. Quantitative determination of chrysotile content was made by compari son of unknowns with calibrations of chrysotile dilution standards. The weight occurrence ranged from about 2-15%, with an average ranging from 3-6%. Lead compounds, quartz, calcite, mica, clays, barite, graphite, and alpha-iron particles were identified as well. In several samples, weak, diffuse reflections suggested the presence of forsterite, but positive identification could not be made using this technique. Identification of Chrysotile by Electron Microscopy Transmission electron microscopy, selected area electron diffraction, and elec- We acknowledge the cooperation of the United Automobile Workeis. Local Union No. 259 and the Automobile Dealer', lmluttti.il Relations Association in helping us obtain these samples in auto maintenance shops in the Nesv York area. Each sample was taken from "a typical job" under way at the time. it r;.; .euxtil I I GYNECOLOGIC ONCOLOGY and ENVIRONMENTAL RESEARCH FMSI 06791 k f 114 0 I . ... | _! tron microprobe analysis of the brake dusts were carried out on each of the ten samples after preparation by a technique which disperses the dust particles in a - nitrocellulose Him without altering particle size distribution. Free chrysotile fiber- bundles and fibrils were observed in all ten samples (Fig. 1). Selected area elec tron diffraction analysis of representative fibers demonstrated the preservation of the chrysotile structure (Figs. 2A. B). Some patterns displayed arcuate reflections suggestive of interfibril rotation and inirafibril displacement (Figs. 2A, B). Occa sionally, fibers were observed without characteristic chrysotile morphology, with mottled surfaces and obliterated fibrils, indicating partial or complete recrystalli- ENVIRONMENTAL RESEARCH and GYNECOLOGIC ONCOLOGY FMSI 06792 GYNECOLOGIC ONCOLOGY ond e n v ir o n m e n t a l research Fic. 2. Selected area electi on diffraction patterns obtained on fibers of chrysolite obtained daring air sampling at brake repair shops. In A. the reciprocal a axis is marked a' as are the layer lines in the (OKI) series Indexing of upper right quadrant yielded 16 reflections corresponding to single crystal X-ray diffraction analysis of Whittaker and Ziissmun. 19.56. Pattern in (B) displays "smear ing" of reflections in a "clockwise" manner suegesting interplanar rotation. i " polycrystalline characteristics of multiple random reflections or Debye-Scherrer rings rather than the distinctive single fiber chrysotile pattern (Fig. 2B). Mic rochemical analysis with a probe technique on the unaltered fibers showed them to possess the usual Mg:Si ratio of chrysotile. In addition to free chrysotile f ber bundles and fibrils, chrysotile was also frequently observed projecting from the margins of binder fragments (Fig. 3). .- Free asbestos fibers present in the decomposed lining dusts were sized at 42.000x magnification. The results, seen in Table 2, show that most fibers are too small to be seen by optical microscopy; almost all of them are shorter than 0.4 pm in length; virtually all are of respirable size (-5 pm). Hatch (1970) in reporting on optical fiber counts obtained from brake cleaning operations with compressed air jet, found that 94% of the fibers fell in the 2-5 jam length category, while only 6% were longer than 5 pm. Jacko and DuCharme (1973) made size distribution meas urements of asbestos fibers in brake dusts generated during dynomometer tests, using both optical and electron microscopy. They found, at magnifications of 22.000x that 30% of the fibers were from 0.25 to 0.50 jtm in length and that 60% were longer than 0.5 yarn. Some discrepancies between our data and those of Jacko and DuCharme may be attributed to their use of the lower magnification (22,OOOx vs 42-OOOx), at which fibers shorter than 0.20 pm may not be easily seen or identified on the electron microscopic screen. Thus., both the optical fiber count data in other studies and the electron microscopic fiber si/e distribution data I ............. : iK...o..r....-.K...it...-.i.i.r......................................... I FMSI 06793 V I ENVIRONMENTAL RESEARCH and GYNECOLOGIC O N C O lO G Fic. 3. Electron photomicrographs of brake drum dusts. Chrysolite is present in both Tree fiber and fibril form. Opaque granular material is road dust or phenolic binder, a., x 10.800; b. x9300; c. x'O.OOO; d. x30,000. . ____ ... Indicate that the chrysotile fiber population generated by brake wear is a strongly skewed one, with almost all fibers concentrated in the smaller than 5 fim region. No attempt was made to size the asbestos-binder particulates. Personal Air Sampling during Drake Repair Work Personal air sampling for asbestos exposure during brake lining maintenance and repair was carried out at franchised auto dealer garages, taxi fleet repair shops, and a municipal truck repair shop, all located in New York City.5 Personal i; ,A>Nt>tance in pioviiling opportunity for sampling v.as given by the Department of Air Resources, ' New Yotk City. I. !...................................................... ! ! |f.t JK i i'll..111 j FMSI 06794 !H[' M.) 117 TABLE 2 LtNOTH DlSIKint'T ion oy CifRvsn i in Fireks in Brake Dac'i Di sr" Sample 750- 1300A N (%) 1500 - 2250A N (%) 2250 - 3000.A N 17r) 3000-3 750A N (95-) Total It*) 1 40 34 II II 96 2 32 23 32 -- 87 3 20 ' ' 25 25 --- ' ' ' 70 4- 26 37 26 7 96 5 57 17 4 -- 78 6 23 9 12 12 56 7 50 26 21 2 99 8 29 30 21 17 97 9 6 ' . 41 18 10 75 10 It 6 31 31 79 Fibers counted and sized at 42,(XX)x; all fibers have diameters from 250 to 500.A. air samples were taken during and after brake repair work and at varying distances from the work sites in other areas of the garages and shops. The latter samples were intended to provide information concerning levels of asbestos exposure which garage employees other than those doing brake work might experience. Asbestos Exposure during Automobile Brake Repair Work Air samples were first taken in the breathing zone of mechanics doing brake repair work. These peak exposure measurements were taken over periods of 3-8 minutes during which the workers were blowing dust from brake drums. The air samples, taken on membrane filters, were processed, and fiber counts made in accordance with the procedures which have been adopted by the Occupational Safety and Health Administration (OSHA) of the U.S. Department of Labor (Baver, Brown, and Zumwalde, 1975). Essentially, the analysis consists of count ing fibers 5 to 100 ftm, in a fixed area of a Porton graticule, using phase contrast microscopy at a magnification of 400x. This microscopic method enhances image contrast and allows large asbestos fibers to be readily seen and counted. When a vehicle is brought into a repair shop for brake lining inspection or replacement, the wheel is removed and loose dust is removed from the drums and back plates, generally by means of a compressed air jet. A recent survey of brake repair establishments in Baltimore and Washington revealed that this is the stand ard method in those cities (Castleman et al,, 1975). A similar situation exists in New York City. The cloud of dust that is produced is visible for several minutes afterwards (Fig. 4). Table 3 shows that fiber concentrations are high in the operator's area under these conditions (an average concentration of 16 fibers/ml), and that there are significant concentrations at least 30 ft away. Background or area sampling during the same operation shows that, at least 14 minutes after jet air blowing and up to 75 ft away, asbestos concentrations are still measurable even by optical microscopy. The data in Table 3 indicate that an asbestos concentration gradient, dependent on distance and time, is associated with this operation. It is evident that any person 65-75 ft away can be exposed. Current (interim) regula tions of OSHA prohibit concentrations of 5 fibcrs/ml or more, longer than 5 ;tm, as c or'it; i'.t:t ! 1 i I j j I j i GYNECOLOGIC ONCOLOGY a n d ENVIRONMENTAL RESEARCH FMSI 06795 i l" i I ENVIRONMENTAL RESEARCH and GYNECOLOGIC ONCOLOGY Fic. }. Removal of dust from brake drum and back plate by pneumatic air blowing at automobile garage. a time-weighted average for workers, and concentrations above 2 fibersml will be illegal after 1976. Regulations set a peak concentration (maximum excursion) of 10 fibers/ml of air. Newly proposed standards are designed to set a limit of 0.5 fibers/ml (500.000 Ftbers/m3), with a maximum excursion of 5 fibers/ml. " It was generally found that there was minimal, if any. effort to control dust in most garages. Workmen do not use respiratory protection. There was little aware ness of the potential hazard of brake dust. In a single instance, brake drum cleaning was not done with a compressed air jet, but with a dry hand brush. Fiber concentrations were somewhat less (2.5 fibers/ml) at the operator level, but background levels 12 ft away were the same as with air jet cleaning. Asbestos Exposure during Truck Broke Repair am! Installation Work Personal air sampling was also conducted at the New York Department of Sanitation truck repair shop, where various kinds of brake application and repair work are performed. Used truck brake linings are salvaged by grinding the surface to remove grease and dirt, and new linings are ground to expedite break-in. The edges of new linings are beveled on a grinding w heel or arcing machine to avoid noise problems. (Fig. 5). Holes aic drilled or punched into the brake lining, which ;i t.orvrusin I FMSI 06796 jl i' -M H9 TABLE 3 Ashf.mds Covuvri.uiONs pckinc. AurnMOmi.v. Bkak 5mvicr.*A Fiber concentration Operation Blowing dust out of brake drums with compressed air jet Distance (ft) 3-5 5-10 10-20 Number of samples 4 3 2 (fibers/mll Mean Range 16.0 6.6-29.8 3.3 2.0-4.2 2.6 0.4-4.8 Background samples taken at varying distance and lapsed times, after brake drum blowing Distance from operation <fo 10 20 12 50 65 75 Time lapse (min) 0 0 5 5 7 14 Concentration (fibers/ml) 0.3 - 0.8 0.2 O.t 0.1 O.t Distance Number of Fiber concentration (SJaers/ml) Cleaning brake drums with dry brush Background samples taken 3 minutes after cleaning brake drums with dry brush (ft) samples Mean Range 1-3 . 2 2.5 1.3-3.6 12 3 0.1 0-0.2 * Fibers 5-100 jim in length, counted by optical microscopy. 1 The new proposed Asbestos Standard of the U. S. Department of Labor records asbestos exposure in fibers/m1. noting that a workman might respire approximately 8 m' of air per working day, retain ing an unstudied proportion of inhaled fibers. The above table omits reference to air content of fibers < 5 /am in length. 'i i -. is then riveted onto a steel plate. Some of these operations are similar to those done during the manufacture of brake shoes. Table 4 summarizes the results of personal air sampling in the course of this work. During light grinding of truck brake shoes (Fig. 6), an average peak concentration of about 4 fibers/ml was found in the breathing zone of the operator. The data show that measurable fiber con centrations are found 25 ft or more away. At a distance of 25 ft, for example, a concentration of 1 fiber/ml (1,000.000 fTbers/ml3) was found. Much larger numbers of shorter fibers would simultaneously be inhaled. During the beveling of truck brake shoes on a grinding machine, very high concentrations of fibers were found in the vicinity of the operator. The average of five air samples was about 37 fibers/ml. Area samples, taken up to 30 ft away from this operation, demonstrated the presence of airborne fibers. It was of interest to note that, at the time of this sampling, from eight to 15 other garage mechanics were working within this I'.onrihnt ' i ^ i GYNECOLOGIC ONCOLOGY and ENVIRONMENTAL RESEARCH FMSI 06797 ENVIRONMENTAL RESEARCH and .GYNECOLOGIC ONCOLOGY * Fic. 5. Beveling of truck brake linings ai municipal garage. Arrow indicates accumulation of asbestos i 1 ;.... i perimeter and were exposed to asbestos. Fiber levels for other kinds of operations at the truck garage are given in Table 4. Boitlat and Lob (1973) have reported fiber concentrations measured during drilling holes for rivets and grinding. They found values ranging from 0.3 to 29.2 fibers/ml: four of the nine values exceeded 5 fibers/mi. A Comparison of Fiber Leeds Visible by Light Microscopy and Electron Micros copy In the ten brake drum dust samples examined, it was found that asbestos Fibers shorter than 0.4 /im predominated (Table 2). The OSHA Asbestos Standard does not require that short Fibers (< 5 pm in length) be counted or controlled. This oversight may have considerable biological significance in that small chrysotile Fibers readily produce asbestos disease (Moll. Mills, and V oung. 19f>4. 1965; Davis, J963; Fott, Huth, and Friedrichs. 1972; Wagner, Berry and limbreli, 1973: i cot FMSI 06798 | > 1-21- I GYNECOLOGIC ONCOLOGY ond ENVIRONMENTAL RESEARCH l Fig. 6. Renewing of municipal truck brake linings by light grinding to remove grease and dirt. ___ ! ; "'7 Hilscher et al., 1970). Attention has recently been again called to the potential importance of this question (Bouhuys, 1975). There is little published information on the numbers of, and sizes of, submicro- scopic asbestos fibers in occupational exposures. The present study afforded an opportunity to collect data on the relationship between submicroscopically- and optically-visible fibers for this specific industrial exposure. Eight air samples were selected for both light and electron microscopic examination. Six of these were taken during brake drum dust removal operations with optical fiber counts re corded from 0.1 to 3.6 fibers.'ml. The other two samples were taken during light grinding of automobile brake shoes. Preparation ami Analysis of Air Samples One square centimeter sections of the eight membrane filters were mounted, dust side down, on microscopic slides and ashed in low temperature activated .! ! ! I'lOi Yf-l till ' j| FMSI 06799 0 1 ENVIRONMENTAL RESEARCH ond GYNECOLOGIC ONCOLOGY 122 1 i -' TAH1.E 4 Asi b n>N COMCLN t RATION Dl'KINC Tltt'CK Brakf Skhvic.f. n Distance Number of Fiber concentration (fibers/ml) ' ' 1 Operation (fo samples Mean Range 1 1 Renewing used linings by I1 grinding Background lo grinding 3-5 10 10 3.8 "> 1.5 1.2--1.7 j 11 1 used linings b 1 25 ? 0.8 60 1 0.2 -- . j Beveling new linings 3-5 5 37.3 23.7-72.0 Background lo beveling 8 1 0.6 -- new linings 12 2 0.4 0.3-0.5 30 1 0.3 . -- Punching rivets into brake linings 3-5 2 1.5 1.9-2.0 Chipping rust off used brake linings 3-5 1 2.4 -- Sweeping floor around grinder 3-5 1 3.6 --- ' Background lo sweeping floor around grimier 15 1 3.1 ' -- " Fibers 5-100 >tm in length, counted by optical microscoDV, i oxygen to remove organic materials. The ashed residue was dispersed in a drop of nitrocellulose solution. The dispersal was accomplished by a "rubouf' technique 1 using the edge of a watch glass (Nicholson, Rohl and Ferrand, 1971). By this I method large asbestos fiber bundles are broken into their constituent smaller j fibrils and large agglomerates of inorganic materials, which normally obscure the presence of asbestos fibers, are broken into particles small enough to allow virtu ally all asbestos to be seen. By placing a second slide over the ground residue and nitrocellulose solution and then gliding the two slides apart, a thin film is pro duced. The dried film is cut into segments which are then floated off in water. The film is mounted onto Formvar-coated electron microscopic grids. Typically, four grids are prepared from each sample and one square on each grid is scanned in the electron microscope at 42.000X magnification to determine the quantity of chrysotile present. By estimating the length and diameter of each fiber, and as- . suming a cylindrical fiber geometry, the mass of chrysotile per grid square is determined. Representative electron photomicrographs of chrysotile fibers and fibrils are shown in Figs. 7 and 8. RESULTS A comparison of the optical microscopic fiber counts and the electron micro scopic total asbestos mass calculations obtained from the eight samples is shown in Table 5. Figure 9, showing the same data, is plotted on logarithmic paper, and visual inspection indicates that a positive correlation exists between the optical and electron microscopic results, although the data are limited and the amount of. "" ! roriRi'.vtii FMSI 06800 GYNECOLOGIC ONCOLOGY and ENVIRONMENTAL RESEARCH Fic. 7. Electron photomicrograph of air sample taken during brake drum blowing (sue sample No. A. Table 5). Large numbers (70-100) of chrysotilc. some of which are masked by granular particulates. presumably road dust (65.000 total magnification). scattering precludes a regression analysis. For example, from these data it may be possible to predict that, during the grinding of new brake linings (Sample No. 8, Table 5). a worker could be exposed to about 0.5 mg of asbestos daily in cir cumstances in which the time-weighted TLV of 5 fibers/ml would not have been exceeded. Similarly, Fig. 9 shows that, since a microgram of asbestos represents on the order of 1 million fibers per cubic meter of air (of greatly varying diameters and lengths), extremely high concentrations of submicroscopic fibers are present up to 65 ft away from brake repair work (e.g., Sample No. 5. Table 5). even though Fiber levels in such a case are barely detected, if at all, by the standard optical counting technique. These limited data indicate that the standard (OSHA) optical fiber counting method may be only a fractional indicator of total asbestos expo sure. at least in the case of automobile repair work. They also indicate that the total exposure is much higher than the OSHA technique records, in terms of COi'f' r. lll I Ij FMS1 06801 ' !` ENVIRONMENTAL RESEARCH and GYNECOLOGIC ONCOLOGY Fic. 8. Electronmicrograph of air sample of cluster of chrysotile fibrils in background sample (see ! sample No. 3, Table 5 (83.OOOx magnification). . - - --- t asbestos fiber number, mass, and surface area. Additional studies relevant to this and other kinds of asbestos exposure are needed to confirm and extend these findings. It is important to note that particles of asbestos-containing pulverized brake lining were not included in this mass determination. Their importance, in terms of biologic potential, is presently unknown. SUMMARY AND CONCLUSIONS (I) Chrysotile asbestos fiber is a major component of brake lining materials. Degradation of the lining is brought about by a combination of factors, which. ii I................................................ | icoi' r Fii> a i r 1 FMSI 06802 Hi: AH i| I' 1If i 125 \ TABLE 5 .i Operation Optical microscopy (fibers/ml) Electron microscopy (/ig/m') M 1. Blowing duel off drum with air jet (10 ft away) 2.0 (.27 2. Background to blowing out brake drum (10 ft away) 0.3 0.2 3. Blowing dust off drum with air jet (30 ft away) 0.4 LI 4. Background to blowing out brake drum (30 ft away) 0.8 0.1 I 5. Background to blowing out brake drum (63 ft away--7 minutes after blowing stopped) .1 0.2 6. Cleaning brake drum with hand brush 3.6 6.5 7. Light grindings of new linings before installation 4.7 53.0 8. Light grinding new linings before installation 2.7 66.0 j I i -T' .I . include thermal stress, material fatigue, and shearing. Modifying agents are in cluded in brake linings which lower the contact temperature between'the lining and wheel interface; this, in turn, prevents binder pyrolysis and chrysotile fiber dehydroxylation. The amount of chrysotile fiber which survives the braking oper ation is related to a number of additional factors, including some which are exter nal to the properties and quality of the lining itself. As a consequence, degradation may occur at temperatures signficantly lower than that required for the dehydrox ylation of chrysotile, with the persistence of fibers. (2) Ten samples of dust were taken from automobile brake drums in New York City, and analyzed. Optical microscopy was of limited usefulness. X-ray diffrac tion analysis, using both continuous and step-scan modes demonstrated the pres ence of chrysotile in all dust samples. The proportion of chrysotile ranged from about 2-15%, and averaged about 3-6%. This included both free .fibet'.s and chrysotile which survived in pulverized binder as particulates. Forsterite, the I .. i i *-rw_y* , . i GYNECOLOGIC ONCOLOGY and ENVIRONMENTAL RESEARCH _ja.________. ICO oco Fui. 9. Comparison of optical aru! electron micro>ev>pic fiber counts. COI* r'K'lGl 11 FNtS\ 06803 r i ii 126 <' . .} ! _' I ! thermal transformation product of chrysotilc could not be unequivocally identified by continuous scan X-ray diffraction. -- (3) The presence of chrysotile asbestos in the ten dust samples was further verified by transmission electron microscopy, selected area electron diffraction and electron microprobe analyses. Chrysotile was found, both in fiber and Hbril form, with unaltered structure and chemical composition. Its frequency of occur rence was consistent with, but lower than the quantitative determination made by X-ray diffraction analysis. However, it should be noted that X-ray diffraction analysis is based on both free fibers and fibers present in clumps; the latter would obscure the presence of discrete fibers on electron microscopic study. In addition to unaltered fiber, partially altered and completely recrystallized fibers were also seen. (4) Size distribution analysis at 42,000x magnification in the ten samples indi cate that about four-fifths of all chrysotile, in fiber form, is shorter than 0.4 in length. These fibers are too small to be seen by optical microscopic techniques. (5) Personal air sampling was conducted during brake repair work in automobile garages in New York City. Standard optical microscopic procedures for fiber counting were used. In samples taken in the vicinity of repairmen blowing dust from automobile brake drums with compressed air. an averagej:oncentration of 16 fibers/ml was measured. Background and time-lapse samples indicate that measurable concentrations exist at least 75 ft from the work site and for at least 14 minutes after jet air blow ing. (6) Personal air samples were taken at a municipal truck repair facility where various brake fabrication and application operations are performed. Grinding of truck brake shoes resulted in an average concentration of about 4 fibers/ml (4,000,(XXYmJ). During beveling, an average fiber count of 37 fibers/ml was meas ured. Exposure levels during drilling, punching rivets, and cleanup were also measured. Background measurements show that fiber concentration gradients are produced during truck brake repair and application work. During light grinding of truck brake shoes, measurable fiber concentrations were found 25 ft or more away, as well as up to 30 ft from brake beveling operations. The background measurements, during both automobile and truck brake work, indicate that many employees in garages other than brake lining workers are potentially exposed to asbestos, including other mechanics and shop management. (7) Eight air samples taken during automobile brake repair work were analyzed by other optical and electron microscopy. A positive correlation was found to exist between optical fiber counts (> 5 p.m) and the total chrysotile mass calcula tions based on sizing all fibers at 42,000x magnification. These data indicate that standard (OSHA) optical fiber counts may be a useful index of total free asbestos exposure during brake repair work. They also demonstrate that the total free asbestos exposure, in terms of fiber number, mass, and surface area is much greater than the optical counting techniques indicate. (8) Attention is called to the fact that in addition to asbestos, other biologically active substances, including free silica and lead compounds, have been identified in brake lining dusts. Their concentrations in brake work environments are not known, and warrant investigation. c;of' i r;i* m ! i ENVIRONMENTAL RESEARCH and GYNECOLOGIC ONCOLOGY FMSI 06804 (9) Potentially hazardous asbestos exposure exists during automotive brake servicing. It has been reported that approximately 900.000 persons are employed in such work in the United States. It is recommended that stringent industrial ,hygiene measures to control exposure be implemented as rapidly as pos.sib.le.. . ACKNOWLEDGMENT We thank Drs. A. E. Anderson. R. 1.. Gealer. and 1. Eichen of The Ford Motor Company for their valuable comments in reviewing the manuscript. REFERENCES Anderson, A. E. (1969). Wear in brake materials. In Proc. Amer. Sue. Metals Wear Conference. Anderson, A. E., Gealcr, R. L.. McCune. R. C.. and Sprys. J. W. 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Selikoff. I. J.. Hammond. E. C., and Churg. J. (1968). Asbestos exposure, smoking and neoplasia. JAMA 204,(2). 106-112. Selikoff. I. J.. Nicholson, W. J., and L.anger, A. M. (1972). Asbestos air pollution. Arch. Emir. Health. 25, 1-13. Wagner. J. C.. Berry, G.. and Timbrel!. V. (1973). Mesothcliomata in rats after inoculation with asbestos and other materials. Brit. J. Cancer 28. 173. Whittaker. F.. J. \V., and Zussman, J. 1956. The characterization of serpentine minerals by x-ray diffraction. Min. Mug. 31. 107. ENVIRONMENTAL RESEARCH and GYNECOLOGIC ONCOLOGY ; iIi !CQ`"t rr;iu I I I t j FMSI 06806