Document zQLzKDYKaexdNenJbnj7Ean0B

11/13/02 WED 18:43 FAX 212 592 7215 NYPL EXPRESS , DEFENDANT'S a exhibit s Am. tnd. Hyg. Assoc. J. 48(5);W-50-t (1987) Exposure to Asbestos During Brake Maintenance of Automotive Vehicles by Different Methods TIMO KAUPPINEN** and KARI KORHONENh '^Institute oi Occupational Health. Topeliuksenkatu 4laA, SK-00250 Helsinki. Finland; BRcgional Institute of Occupational Health. PL 175, SF-5310I Luppeenranla, Finland Asbestos concentrations were measured during the different operations of brake maintenance of passenger ears, trucks and buses in 24 Finnish workplaces. The estimated average asbestos exposure during the workday (8-hr time-weighted average) was 0.1-9.2 fibers/cm3 during brake repair of trucks or buses, and under 0.05 f/cm'1 during repair of passenger car brakes when the background concentration was not included in the calculations. The background concentration was estimated to be less than 0.1 f/cm*. During brake maintenance ofbuses and trucks, heavy exposure, 0.3-125 (mean 56) f/cm', was observed during machine grinding of new brake linings if local exhaust was not in use. Other short-term operations during which the concentration exceeded 1 f/cm1 were the cleaning of brakes with a brush, wet cloth or compressed air jet. During brake servicing of passenger cars, the concentration of asbestos exceeded 1 f/cm1 only during compressed air blowing without local exhaust. The different methods of decreasing the exposure and the risk of asbestos-related diseases among car mechanics are discussed. Introduction Friction Materials and Brake Maintenance Procedures Brake maintenance and repair is carried out in most garages and service stations in Finland. Although substitute mate rials not containing asbestos are used increasingly, the brake and clutch linings of many cars, as well as the brake drum dust, still contain chrysotile asbestos. Therefore, car me chanics and other garage workers potentially arc exposed to asbestos fibers emitted during brake servicing. According to the Finnish Register of Employees Occupa tionally Exposed to Carcinogens,11* about 1400 car mechan ics are exposed to asbestos in Finland, most of them during brake maintenance of trucks and buses. The registration, however, is based on the notifications made by the employ ers. and this value does not include every worker who main tains or repairs brakes. If those persons who deal with pas senger car brakes or who service brakes infrequently are included also, the number of exposed workers approaches the total number of car mechanics, which is about 20 000 (nearly 1% of the employed population). During 1977-1983, the concentrations of asbestos fibers were measured by the occupational hygienists of the Finnish Institute of Occupational Health in 24 workplaces to study the exposure of car mechanics to asbestos during different operations and brake maintenance procedures. This article is a summary of these measurements. 'Correspondence to: Timo Kauppinen, Ph.D.. Institute of Occupa tional Health, Department ot Epidemiology and Biometry, Tcpcliuksenkatu 41aA, SF-00250 Helsinki, Finland. Drum brake linings usually contain 30-70%(by wt.) and disc brake pads 10-30% of chrysotile asbestos. In addition to asbestos, the brake linings contain phenolic type resins, lubricants and metal oxides.13'7* The typical composition of asbestos-free, "semi-metallic," drum brake linings or disc brake pads is as follows: metals (Fe) 60-70%; graphite 1525%; filling agents 7-10%; and binders 0-5%.<71 Other types of asbestos-free friction materials also have been developed. During braking, most asbestos fibers lose their fibrous character, but the brake drum dust still contains some chrysotile asbestos. Several investigators have analyzed brake drum dust and found0.I-l wt-%13'8'11' or 1-15 wt-% of chrysotile fibers.1*'6'11,13' Besides drum dust, the brake repair workers may be exposed to unaltered asbestos fibers during grinding, beveling or riveting of new brake linings. The procedure of brake maintenance depends on the type of vehicle and brakes. Trucks and buses usually have drum brakes. After removing the wheel and brakedrum, the clean ing of the brakes may be carried out by blowing with a compressed air jet, by brushing, by wiping with a wet cloth, by sucking with a vacuum cleaner, or by washing with water. A vacuum funnel is commonly used during compressed air cleaning because of heavy dust emission, but it is less com mon during other procedures. If the brake linings are worn out. they are removed and new linings are riveted to the brake shoes, if needed, the new linings are ground to fit the shoes. Finally, the brake shoes, brake drum and the wheel are assembled. The brakes of passenger cars are either of disc or drum type. The disc brakes gather less debris than the drum brakes Copyright Arner-can Industrial Hygiertg Association 4m, lag. hyg. Xssoe. J (tg) May. 1587 (99 NOU-13-2002 17-54 212 592 7215 95*4 P.10 HWBUI0007490 11/13/02 WED 18:44 FAX 212 592 7215 NYPL EXPRESS @011 because of more open structure. The maintenance of disc brakes usually consists of the removal of old pads, cleaning of the brakes with compressed air, and attaching of new brake pads. The maintenance of drum brakes is basically similar to that of heavy vehicles. Methods The authors carried out measurements in 7 out of 24 work places under study. The other results were collected from the measurement reports that include a description of sampling and analytical methods used, remarks on the prevailing circumstances during the measurements, data on sampling sites and limes, and the results with pertinent comments. The sampling procedures and the analytical methods were the same in all measurements. Asbestos was measured in the breathing zones of car mechanics or within the working areas. Dust samples were collected on Millipore membrane filters. A sampling rate of 2 L/ min and a sampling time of 1-60 min (air volume 2-120 L) was used depending on the duration of the operation and the expected dust concentration to get a proper fiber density on the filter for microscopic counting. Asbestos fibers (length over 5 pm, diameter under 3 and the aspect ratio over 3:1) were counted by a phase contrast-optical microscope according to the standardized method (Finnish Standard SFS 3868).0,1 A similar method is used in many countries (e.g., Sweden, Norway, Denmark, 'Great Britain, the Federal Republic of Germany and the United States). This method has been tested in international quality control analyses.061 In addition, respirable dust containing asbestos was meas ured in some workplaces. Leitz tyndallometer(TM Digital) that measures dust with particle diameters up to 3 pm was used with xy-plottcr to monitor the dust concentration by time, and for the comparison of the relative dust concentra tions produced by different working procedures. Eight-hour time-weigh ted average (TWA) concentrations of asbestos were estimated for different work procedures. The estimates were calculated by using the measured mean and maximum concentrations, as well as the mean durations of the operations. It was assumed that the brake mainten ance of four wheels was carried out during the workday. Other less common operations -- such as grinding of brake linings, turning of brake drums and clutch repair -- were assumed to take 1 hr of the workday. The calculated concen trations do not include the background concentration of asbestos, because only very few data were available. Results The results are presented by operation and type of vehicle. As to buses and trucks, the results were similar; and they are combined in Table 1. The highest concentrations were meas ured during grinding of brake linings when local exhaust was not used. Other operations during which the mean concentration exceeded I fiber/cm3 (f/ cm3) were the brushing of brakes, the cleaning of brakes with a wet cloth, compressed air blowing, and grinding of brake linings, even though a vacuum funnel or local exhaust was in use. During all other operations, the mean concentration was under I f/cm3. The results on passenger cars are presented in Table 11. The mean concentration of asbestos exceeded 1 f/cm3 only during compressed air blowing without exhaust. The estimated asbestos concentrations during different hypothetical 8-hr workdays are shown in Figure 1. According to these calculations, the average exposure to asbestos dur ing the workday was usually 0.1 -0.2 f/cm3 during brake re pair of trucks or buses, and underO.05 f/cm3 during repair of passenger car brakes. The heaviest exposure, about 7 f/cm3, was due to grinding of brake linings for 1 hr without exhaust. Three examples of the variation of the dust concentration by time as measured by Leitz tyndallometer are shown in Figure 2. The concentration remained at a low level during washing of the brakes, but during brushing and compressed air blowing, the concentration of dust -- and probably also that of asbestos -- was characterized by high peaks. The concentration, however,.decreased to the background level rapidly, usually in 1-2 min. Also the interday variation in the concentration is worth noting because the frequency of brake maintenance jobs varies with workplace. According to the data of the Finnish Register of Employees Occupationally Exposed to Carcino gens, a car mechanic maintains on average the brakes of 12 trucks or buses in a year (range 1-45, sample of 53 work places). The corresponding figure for workplaces maintaining mainly passenger car brakes is 41 (range 3-150,23 workplaces). Therefore, it is likely that the annual mean exposure is even less than that shown in Figure I. In addition, the difference in exposure between the heavy vehicles and passenger cars is diminished to some extent. When the daily exposure during brake repair of heavy vehicles is on average 10-15 times higher than during brake repair of passenger cars, the annual mean exposure is only 3-5 times higher. Discussion The occupational exposure limit for asbestos is 0.5-2 f/cm3 (8-hr TWA) in most countries. The Threshold Limit Values (TLVs) adopted by the American Conference of Govern mental Industrial Hygienists (ACGIH) are 2 f/cm3 for chrysotile, 0.5 f/cm3 for amosite, 0.2 f/cm3 for crocidolite, and 2 f/cm3 for other forms of asbestos fibers.^";, in brake maintenance of trucks and buses, the ACGIH TLV for chrysotile asbestos was exceeded only when new brake lin ings were ground without local exhaust (Figure I). With all other proced ures, the estimated mean concentration was less than 10% of the TLV. The unestimaied background concen tration of asbestos in the brake maintenance workplaces, however, gives rise to the possibility of underestimation of the TWA concentrations. The background concentration of asbestos measured in this study was, at its highest, the same as the detection limit of the method (0.1 f/cm3). Similar or slightly higher short-term background concentrations have been found also in other studies.0'5,11,181 It is not possible to infer exactly the magnitude of the 8-hr TWA background 500 Am. Ind. Hfg. Assoc. J. (48) 1S87 Nni i-i l-'W 17:54 P12 592 7215 95'4 P-U HWBUI0007491 11/13/02 WED 18:45 FAX 212 592 7215 NYPL EXPRESS @012 TABLE I Asbestos Fiber Concentrations by Operation In Brake Maintenance of Trucks and Buses Operation Atbeitot Fiber Con centration (f/ero3) Range Median Mean Sample* Workplace* Range ol Sampling Time (min) Opening ot brakes Opening and brushing of brakes Cleaning of brakes by brushing Cleaning of brakes with compressed air jet, enclosure and exhaust in use Cleaning of brakes with damp cloth Opening of brakes and clean ing of brakes by washing Cleaning of brakes by washing with water Loosening rivets from brake linings Cleaning of brake shoes Punching rivets into brake linin s Grinding of brake linings with machine, no exhaust Grinding of brake linings with machine, exhaust in use Bevelling edges of brake linings with file Cleaning of brake drums by brushing Grinding of brake drums Assembling of brakes Sweeping floor of garage Other, rare operations Background to brake maintenance <01-1.9 <0.1-1.0 0.1-4.5 0.2-3.0 0.1 0.3 0.9 0.7 0.4 03 1.3 1.2 1.1-3.3 <0.1-0.3 <0.1-0.2 1.3 0.2 0.2 1.9 0.2 0.1 <0 1-1.6 0.3-0.4 02 - 0.1-3.5 0.4 0.3-125 67 0.1-5.9 0.6 0.1-09 0.5-0.7 0.1-0.3 <0.1-04 <0.1-1.7 <0.1-0.6 0.3 0.2 0.1 0.3 <0.1 <0.1-01 0.1 03 - 0.7 56 1.5 04 * 0.2 0.2 0.6 0.2 <0.1 25 6 8 9 3 6 6 12 2 28 S 30 7 2 6 9 4 5 3 13 2-25 4 1-12 3 2-12 5 1-14 2 2-5 4 2-10 5 4-18 9 S-29 1 3-5 9 3-60 2 4-27 4 4-33 3 2-5 1 5-6 4 3-26 6 6-41 3 2-4 2 2-30 3 3-68 concentration based on these data, but it is likely to be less than 0.1 f/cm3 in the present Finnish garages. Even though this concentration is low when compared with the occupa tional exposure limits, it is considerably more than in the urban atmosphere. According to electron microscopic stu dies, 1 ng of asbestos corresponds approximately to 400 libers of asbestos as counted by a phase contrast micro scope .",J ifthis conversion factor is applied to the concentra tions measured by electron microscopic methods, the mean concentration of asbestos fibers in urban air has been reported to be below 0.001-0.003 f/cm3 in Great Britain'301 and about 0.002 f/cm3 in46 cities in the U.S.l2l,Theconcen trations measured near busy road junctions in New York City were 0.004-0.02 f,- cm3.'2'2' Reports on asbestos exposure during brake maintenance have been published earlier by R chief a/..'1' Lorimerei a/.,'51 An l<Kl. Hfi toot J (481 Mjy. 1987 Hickish & Knight16'17' and Rodelsperger el al.iZS> The expo sure estimates of this study (8-hr TWA: below 0.01-0.5 f/cm3; annual mean: below0.0l-0.03 f/cm3) are compatible with the results of the recent German study.1231 Hickish and Knight,'61 however, reported the 8-hr TWA of 1.8 f/cm3 for a truck brake service worker and of 0.7 f/cm3 for a worker who maintained the brakes of eleven passenger cars during the workday. These values are higher than those reported in this study. The difference may be due to the different work procedures used during the measurements. The data of Hickish and Knight161 were published in 1970 and the proce dure used was the compressed air blowing without exhaust, whereas the authors'data are mainly from the 1980s when a vacuum funnel is nearly always used during blowing of truck brakes in Finland. Furthermore, in the servicing of pas senger cars, the air jet blowing without exhaust is nowadays SOI l mi r_ i T.nnm -i n? 71 7 771 S f,z P.12 HWBUI0007492 11/13/02 WED 18:45 FAX 212 592 7215 NYPL EXPRESS 013 TABLE II Aabealoa Fiber Concentrations by Operation In Brake Maintenance of Passenger Cars Operation Asbestos Fiber Con centration (f/cm3) Rang* Median Mean Samples Workplacea Range of Sampling Time (min) Opening and brushing of drum brakes Cleaning of drum brakes with compressed air jet, no exhaust Cleaning of drum brakes with compressed air jet, exhaust In use Cleaning ot brake drum by brushing Grinding ot brake drums Cleaning of disc brakes and changing of brake pads Changing of brake discs Grinding of brake discs Changing of clutch linings Background to brake maintenance 0.3-0.6 <0.1-8.2 0.4 0.4 0.4 1.5 <0.1-02 0.1 0.1 0.1 0.5 - <01-0,2 <0.1 <0.1-02 <0.1-0.1 <0.1 - <0.1 0.1 - - <0.1 - <0.1 - 4 9 5 1 1 8 2 2 3 1 2 2-13 3 1-10 2 2-15 11 13 1 7-38 1 23-23 1 10-10 2 8-12 1 44 used only during cleaning of disc brakes that are not as dusty as drum brakes. The TWA estimates in the present study, and those in the study by Htckish and Knight, are thus actually based on different work procedures. Measurable concentrations of asbestos fibers have been reported to exist up to a distance of 25-30 m from a repair man blowing dust from the brakes with compressed air. According to these results, it takes 15-20 min until the back ground level of about 0.1 f/cm3 is reached again.'51 The present study indicates a more rapid decrease in concentra tion, but the lower initial concentration and indirect meas uring method (tyndallometry) probably explain the differ ence. During the grinding of new linings the asbestos concentra tion has been reported to be24-72 f/cm3 near the workplace and 0.3 f/cm3 at a distance of 10 m.1 These concentrations are compatible with the results of the present study. The results demonstrate that the grinding of new linings is an operation that may cause heavy exposure unless the enclo sure and the local ventilation are efficient. The vacuum brush method has been preferred to com pressed air blowing with a vacuum funnel, in the servicing of truck brakes."7' The authors' results indicate that the most preferable method of cleaning brakes is by washing with water. The concentration of asbestos during washing was considerably lower than during brushing, vacuum funnel blowing or wiping with a damp cloth. The concentration during vacuum brush cleaning was not measured because it was not used in any of the 24 workplaces under study. The likelihood of contracting asbestos-related disease because of brake repair cannot be inferred accurately from the exposure data of this study. Six verified cases of asbestosis among car repair workers, however, have been reported to the Finnish Register of Occupational Diseases during 19641984. Four of them were car mechanics, one was a turner, and one a garage supervisor. In addition, two car mechanics in the garage of an asbestos quarry have been affected with asbestosis, but their exposure mainly may have originated from contaminated mine vehicles. It is noteworthy, how ever, that the past exposures during brake maintenance probably have been heavier that the concentrations reported in this study. Thus the present exposure may indicate a lowered risk of asbestosis in the future. it is well-established that exposure to asbestos may cause cancer -- especially mesothelioma and lung cancer.1'' There are only few epidemiological data on the cancer morbidity or mortality among car mechanics. Nicholson5' has referred to the data of McDonald and McDonald, according to which at least eleven cases of mesothelioma were diagnosed among automobile maintenance workers in Canada during 19601972 and in the U.S. in 1972. Jn the Federal Republic of Germany, four cases of mesothelioma have been observed among car mechanics.3' One case of mesothelioma in a brake repair worker has been reported in detail.1261 Based on exposure and x-ray data, Nicholson has estimated that the probability of contracting asbestos-related cancer among automobile maintenance workers is over tenfold less than among insulators and manufacturing workers exposed to asbestos.5' Additional epidemiological studies are never theless required to obtain more accurate information on the cancer risks among car mechanics, and to evaluate thepossible contribution of smoking and other chemical exposures to the risks in car repair work. so? 4m. Ind. Hyg. 4ssac. 1. (4S) Mar. 1987 NOU-13-2002 1?:54 212 592 7215 S5'4 P. 13 HWBUI0007493 11/13/02 WED 18:46 FAX 212 592 7215 NYPL EXPRESS @014 ESTIMATED EXPOSURE TO ASBESTOS (8-hour TWA), fiber* over S 0.001 O.OI 0.1 BRAKE MAINTENANCE OF TRUCKS AND BUSES (FOUR WHEELS/PAY) Cleaning of brake* by bruablno Cleaning of brake* erllft em*riMd air, vacuum tunnel In uae Cleaning of brake* with wat cloth Cleaning of brakes by washing wlih water OTHER OPERATIONS Grinding of brake linings, no exhaust (one hour) Grinding of brake linings, erfteusi in use (one (tour) Grinding of brake drums (one hour) BRAKE MAINTENANCE OF PASSENGER CARS (FOUR WHCEL5/0AY) Cleaning of disc brakes and changing of brake pads 1 10 100 Cleaning of drum brakes by brushing Cleaning of drum brake* with compressed air. no exhaust Cleaning of drum brakes with compressed air, exhaust in use Clutch repair (one hour) 0.001 0.01 0.1 1 10 100 Figure 1 -- Estimated mean (bar) and maximal (T-length) exposures to asbestos during a hypothetical workday with different cleaning procedures of brakes; four wheels of a truck, bus or a passenger car are maintained. The back ground concentration of asbestos is not included in the calculations. Figure 2 -- Variations in respirable dust concentration as measured by Leitz tyndallomeler during different cleaning procedures of bus brakes; a) cleaning of brakes by brushing; b) cleaning of brakes with compressed air jet, vacuum funnel in use; and c) cleaning of brakes by washing with water. Acknowledgments Wc wish to thank our colleagues in the Regional I nstitutes of Occupational Health, especially Mr. Berndt Engstrom and Ms. Salme Rantanen have been extremely kind in providing information. The help of Ms. Marja Vasama and Dr. Maui Huuskonen in providing the data from the Register of Occu pational Diseases also is gratefully acknowledged. References 1. Herva, A. and T. Partanen: Computerizing Occupational Carcinogenic Data in Finland. Am. Ind. Hyg. Assoc. J. 42:529-533 (1981). 2. Institute of Occupational Health: ASA 1983. Data on Employees Occupationally Exposed to Carcinogens. Helsinki, Finland: Institute of Occupational Health. 1985. [In Finnish], 3. Heidermanns, G., G. Kuhnen, A. Schutz and R. Prochazha: Dust Concentrations During Production of Asbestos Con taining Friction Materials and Brake Repair in Truck Main tenance Workplaces. Slaub Reinhalt. Luft 35:433-436 (1975). [In German]. 4. Rohl, A.N., A.M. L-anger, M.S. Wolf and I. Weisman: Asbes tos Exposure During Brake Lining Maintenance and Repair. Environ. Res. 12:110-128 (1976). 5. lorimer, W.V., A.N. Rohl, A. Miller, W.J. Nicholson and I. Selikofl: Asbestos Exposure of Brake Repair Workers in the United States. Mount Sinai J. Med. 43:207-218 (1976). 6. Hickish, D.E. and K.L. Knight: Exposure to Asbestos During Brake Maintenance. Ann. Occup. Hyg. 13:17-21 (1970). 7. Lohrer, W, and M. Berlin: Substitution of Asbestos in Fric tion Linings - Problems and Trends Staub Reinhalt. Lult 43:78-65 (1983). [In German], 8. Lynch, J.Rj Brake Lining Decomposition Products. J. Air Poitut. Control Assoc, f8:824-826 (1968). 9. Hatch, 0.: Possible Alternatives to Asbestos as a Friction Materials. Ann. Occup. Hyg. 13:25-29 (1970). 10. Rowson, D.M.: The Chrysotile Content of the Wear Debris of Brake Linings. Wear 47:315-321 (1978). 11. Alste, J., D. Watson and J. Bsgg: Airborne Asbestos in the Vicinity of a Freeway. Atmos. Environ. 10:583-586 (1978). 12. Seshan, 1C.: On the Utility of Dark-Field Electron Micro scopy in the Determination of the Degree of Deformation in Chrysotile Asbestos: An Environmental Research Applica tion. Environ. Res. 16:383-392 (1978). 13. Bolllat, M.A. and M. Lob: Risk of Asbestosis in Workers Employed in Replacing Automobile Brake Linings. Schweiz. Med. Wochenschr. 103:1354-1359 (1973). [In German], 14. Finnish Federation of Standards: Air Control, Workplace Atmosphere, Counting Criteria lor Asbestos Fibers. A Fin nish Standard SFS 3B68. Helsinki. Finland: Finnish Federa tion of Standards, 1981. [In Finnish). Am ha. Hyg. Assoc J I4S) Mar. I9B? 103 N0U-13-2002 17:54 212 592 7215 95: P.34 HWBUI0007494 11/13/02 WED 18:47 FAX 212 592 7215 NYPL EXPRESS @015 15. Beeket, T., B, Gytseth, S. Krantz, I.M. Paris and T. Schneider: An Exchange of Membrane Filter Samples of Airborne Asbestos Between One U K. and Three Scandinavian Laboratories. Scand.J. Work Environ. Health 5:42-49 (1979). 16. American Conference of Governmental Industrial Hygien ists: TLVs* -- Threshold Limit Values and Biological Exposure Indices for 1985-86. Cincinnati, Ohio: ACGIH, 1985. 17. Knight, K.L. and D.E. Hicklsh: Investigations into Alterna tive Forms of Control for Dust Generated During the Clean ing of Brake Assemblies and Drums. Ann. Occup. Hyg. 13:37-39 (1970). 18. Wambugu, A.W., A.S. Mubfshi, W.O. Sakari, K. Kurppa, T. Kuusela and A. Zitting: A Study of Workers Exposed to Asbestos During Brake and Clutch Lining Maintenance in a Kenian Workshop. A Radiological Survey. In Proceedings of the Second Finnish-Kenian Symposium on Occupa tional Safety and Health, edited by L. Saarinen. K. Kurppa and H. Koivunen. Nairobi, Kenya and Tampere and Hel sinki, Finland: Institute of Occupational Health, 1983. 19. Dement, J.M., R.D. Zumwalde and K.M. Wattlnglord: Dis cussion Paper: Asbestos Fiber Exposures In a Hard Rock Gold Mine. Ann. N.Y. Acad. Sci. 27V.345-352 (1976). 20. Burden, G.J., J.N. Le Guen and A.P. Rood: Mass Concen trations ol Airborne Asbestos in the Non-occupational Environment -- A Preliminary Report of U.K. Measure ments. Ann. Occup. Hyg. 28:31-38 (1984). 21. National Institute lor Occupational Safety and Health: Revised Recommended Asbestos Standard (NIOSH Report No. 77-169). Washington D.C.: NIOSH 1976. 22. Selikoff, I.J., W.J. Nicholson and A.M. Langen Asbestos Air Pollution. Arch. Environ. Health 25:1-13 (1972). 23. Rddelsperger, K., H, Jahn, B. Bruckel, J. Manka, R. Paur and H.-J. Woitowllz: Asbestos Dust Exposure During Brake Repair. Am. J. Ind. Med. 10:63-72 (1986). 24. International Agency for Research on Cancer: Chemicals. Industrial Processes and Industries Associated with Cancer in Humans. In IARC Monographs Supplement 4. Lyon, France: IARC, 1982. 25. Nicholson, W.J.: Estimates of Occupational Mortality from Past and Projected Exposure to Asbestos. In Proceedings of the World Symposium on Asbestos May 25-27, 1982. pp. 136-149. Montreal, Canada: Canadian Asbestos Informa tion Centre, 1982. 26. Langer, A.M. and W.T. McCaughey: Mesothelioma in 8 Brake Repair Worker. Lancet i: 1101-1103 (1982). 16 June 1986; Revised 3 January 1987 PETITION FOR CONTRACT AGREEMENT FOR THE GENERATION OF REFERENCE SAMPLES TO SUPPORT THE AIHA PROFICIENCY ANALYTICAL TESTING (PAT) PROGRAM The Proficiency Analytical Testing (PAT) Program is an inter-laboratory, round-robin testing program where industrial hygiene reference samples are sent quarterly to participating laboratories. The program currently provides reference samples of lead, cadmium, zinc, silica, asbestos and organic solvents (benzene, carbon tetrachloride, cellosolve acetate, 1,2-dichloroelhane, hexane, methylene chloride, methyl chloroform, methyl ethyl ketone, methyl isobuty! ketone, octane, chloroform, p-dioxane. toluene, trichloroethylene and O-xylcne) to over 670 public and private laboratories on a quarterly basis. The American Industrial Hygiene Association is accepting proposals for the Proficiency Analytical Testing Program until June 30. 1987. Companies which feel they are capable of preparing reference materials on various air sampling media by aerosol generation and filtration means should request a proposal which states the specifics of such work. The awardee of this contract will prepare variable quantities of PAT reference samples in accordance with A! HA specifications including shipping samples to participating laboratories on a quarterly basts. The quantities ofeach contaminant sample self metals, silica, asbestos and organic solvents), in addition to the quantity of sample kits to be delivered lo the participants arc variable to match sample production as closely as possible with participant analytical needs and the number of laboratories participating in the program. Requests for proposals should be directed to: American Industrial Hygiene Association c/o Rebecca S. Boyes, Manager Member Services 475 Wolf Ledges Parkway Akron, OH 44311-1087 (216) 762-7294 104 NOU-13-?002 17=54 212 592 7215 Am ind Hn. Assoc. J. (AS) May, 1987 9b4 P. 15 HWBUI0007495