Document 8R9BYkN7dzExw92EpvznrX4ka

FILE NAME: Kaiser Gypsum (KG) DATE: 1973 Nov 19 DOC#: KG 101 DOCUMENT DESCRIPTION: Report - Evaluation of Exposure to Asbestos During Mixing and Sanding of Joint Compounds GEORGE D. CLAYTON & ASSOCIATES ENVIRONMENTAL CONTROL SPECIALISTS SOUTHFIELD. MICHIGAN 48075 EVALUATION OF EXPOSURE TO ASBESTOS DURING MIXING AND SANDING OF JOINT COMPOUNDS GYPSUM ASSOCIATION Denver, Colorado November 19, 1973 *-s 961 l ZfOcI EVALUATION OF EXPOSURE TO AS3EST0S DURING MIXING AND SANDING OF JOINT COMPOUNDS GYPSUM ASSOCIATION Denver, Colorado INTRODUCTION The Gypsum Association retained George D. Clayton and Associates to conduct an industrial hygiene survey at a test site located in Den ver, Colorado. The purpose of the survey was to determine the con centrations of airborne asbestos to which workers were exposed dur ing mixing and sanding of joint cement compounds and to interpret the results in terms of potential health hazards with particular refer ence to regulations promulgated under authority of the Occupational Safety and Health Act of 1970. This study was conducted on November 19, 1973 by Mr. Robert D. Soule of Clayton and Associates. Results of that study are reported herein. BACKGROUND The Gypsum Association, located at 1603 Orrington Avenue in Evanston, Illinois is a trade association which represents ten to fifteen in dustrial companies which are engaged in the manufacture of products incorporating gypsum or gypsum-like materials. As with most indus trial concerns, the activities of the Gypsum Association have Irecome more broad with the passage and implementation of federal regulations such as the Metal and Non-Metallic Mine Safety Act and the Occupa tional Safety and Health Act. Technical committees composed of per sonnel from companies comprising the Gypsum Association have been es tablished with particular interest in the occupational safety and health field. Of particular concern in this respect was the poten tial hazard associated with exposure of workers to airborne asbestos during mixing and sanding of compounds used to seal cracks and joints formed during installation of wallboard material. Although the spe cific formulations used by the various companies manufacturing and supplying the joint compound vary,it is understood that essentially all of them incorporate asbestos in the product whether as a dry com pound or a ready-mix product. In order to evaluate the exposure of workers to asbestos during han dling and use of the joint compound products, the Gypsum Association decided to undertake a test program during which several products would be mixed and sanded. George D. Clayton and Associates was re tained to collect and analyze samples which would represent the ex posure of workers engaged in the study. The tests were performed cn November 19, 1973 in a development of townhouses known as King's Mill Townhouses, which were under construction in a suburban area north of Denver, Colorado. POTENTIAL HEALTH HAZARD ASSOCIATED WITH EXPOSURE TO ASBESTOS Asbestos is a generic term referring to various mineral silicates. The types used most widely in industrial applications include c r . r y s o tile, or "white asbestos" (a hydrated magnesium silicate), amoscte, or "grey asbestos" (an iron magnesium silicate), crocidolite, or "blue asbestos" (a sodium iron silicate), tremolite (a calcium mag nesium silicate), and anthophyl1ite (another iron magnesium sili cate). Of these, chrysotile accounts for over 90 percent of the total usage of asbestos in this country, with amosite and crocido lite being the only other types used to any significant extent. Asbestos exists naturally in bundles of extremely fine fibers which can be subdivided easily into many smaller fibers. The potential health hazard associated with exposure to asbestos is that of inhala tion of airborne fibers resulting in a type of pneumoconiosis referred to as "asbestosis." Small asbestos fibers can pass readily through the upper respiratory tract and be deposited in the terminal bronchi oles of the lung. There, they produce a local irritation which the body attempts to overcome by Initiating a tissue response resulting in the encapsulation of the fibers and consequent formation of "as bestos bodies." If sufficient quantities of fibers are inhaled over an extended period of time, a generalized diffuse peribronchiolar' fibrosis can develop. This pulmonary fibrosis can impair the trans fer of oxygen across the aveolar membranes and result in respiratory insufficiencies, or even cardiac failure. It has been determined, through toxicological and epidemiological studies, that long fibers, 20 to 50 micrometers in length, are most active in the production of the fibrosis. Fibers' shorter than about two micrometers in length, are practically without an irritating effect. There is some evidence that other minerals having fibrous characteristics can produce .simi lar react ions. Many recent studies have indicated an association between exposure to asbestos in both industrial and urban atmospheres and an increase in a relatively rare type of lung cancer known as mesothelioma. Al though it has not been possible to establish a connection with asbes tos in all cases of this disease, there is a strong correlation be tween exposure to crocidolite and occurrence of mesotheliomas. Other types of asbestos have been implicated to a much lesser extent. How ever, this "new hazard" has received much public attention because it has been suggested that very minimal, non-occupational exposure can be sufficient to produce the disease in some individuals. For many years the American Conference of Governmental Industrial Hy gienists has recommended a threshold limit value (TLV) of five mil lion particles per cubic foot of air (mppcf) for all types of asbes tos-bearing dusts containing less than one percent crystalline silica. The threshold limit value is defined as the concentration of an air borne contaminant to which it is believed that nearly all workers car. he exposed for continuous and repeated work days without experiencing adverse effect.. The TLV of five mppcf was based on the impinger sam pling technique which was selected a the standard method in tne early epidemiological studies of occupational exposure to asbestos. Virh this method, air is drawn through an impinger containing water ar.d the total particles (both grains and fibers) in an aliquot of the sample,are counted using light-field microscopic techniques. Within recent years, because of the increasing concern about astestos > in the environment and the resulting need for a more relevant sam pling method, the American Conference of Governmental Industria. Hygienists has proposed a TLV of five fibers (greater than f i v e micrometers in length) per cubic centimeter of air. This standard is based on the membrane filter technique with actual microscopic fiber count ing at 400-450X magnification using phase contrast i11uaination. The Occupational Safety and Health Administration (OSHA) has estab lished the above concentration (five fibers, greater than five micro meters in length, per cubic centimeter of air) as an emergency stand ard and have announced that, effective July 1, 1976, the acceptable limit for an eight-hour, time-veighted average exposure will be re duced to two fibers/cc. In addition, OSHA has established the con centration of ten fibers (greater than five micrometers in length) per cubic centimeter of air as an acceptable ceiling concentration. Workers shall not be exposed to concentrations of asbestos in excess of this value, regardless of duration of exposure. SAMPLING AND ANALYTICAL METHODS The air sampling conducted to evaluate exposures of workers to a s b e s tos was all of the "breathing zone" type. These samples were c o l lected by drawing air through 37-mm diameter membrane filters ( M i i l i pore Type AA) at a rate of about two liters per minute using s ma ll , battery-operated pumps (Mine Safety Appliances Company, Model G)\ T h e sampling units were worn by the workers engaged in either m i x i n g or sanding the joint compound; the pump was attached to the belt ar.d the sampler head fastened on the outside of the worker's shirt "at approximate breathing zone height. Thus, these samples were r e p r e sentative of the time-weighted average conditions to which the men were exposed during the sampling period. The sampling head consisted of a three piece cassette (Millipore); during sampling the f a c e cap was removed and the filter was used in an "open face" mode w i t h t he filter positioned slightly downward so as to minimize dust f a l l i n g d.irectly onto the filter. Sampling was conducted for the entire duration of the mixing o p e r a tions but because of the higher anticipated concentrations a s s o c i ated with sanding of the joint compounds it was decided to c h a n g e filters approximately every ten minutes. Sampling during the s a n d ing on the various joint compounds was conducted over a total p e r i o d of sixty minutes. Therefore six consecutive ten-minute samples w e r e obtained for each sanding test. In addition to the ten-minute t e s t s , samples were collected over thirty-minute periods as well, i.e., t w o consecutive 30-minute samples for each sanding test. After c o l l e c tion of each sample the filter cap was replaced and the cassette, cr ampler head, was sealed immediately and prepared for transfer to t h e analytical laboratory. The method of counting asbestos fibers was essentially the same as that used by the U.S. Public Health Service for the enumeration of asbestos dust on membrane filters. The description of this methoc first appeared in an article written by G.3. Edwards and J.R. Lvr.cn and appeared in the Annals of Occupational Hvgiene, Volume 2, pages 1-6 (1968). r.po U i l in luooary, the method consisted of the following steps. A pie-shaped section of each sample vit mounted on a standard microscope slide using a high viscosity solution of membrane filter in a 1:1 mixture of diethyl oxalate and dimethyl phthalate to render the filter transparent. The* asbestos fibers which were on the surface of the filter were then counted using a 10X eyepiece and a 1OX objective with phase contrast illumina tion. A number of fields, selected at random across the sample, suf ficient to reveal a minimum of 100 fibers were examined and fibers greater than five micrometers in length were counted. Any particle having an aspect ratio of three or greater was con sidered to be a fiber. Although it was conceivable that there would be fibers of paper or other materials present on the fi1-^ ters which would have been dislodged from the wallboard during the sanding operation it did not appear chat these were of any adverse consequence during the analysis of the samples. Although it is realized that the counting technique is not specific in terms of being able to identify the chemical nature of the fibers present in the sample, all of the fibers observed in these sam ples appeared to have physical features characteristic of asbestos fibers. For those samples collected over a thirty-minute period, and which were too heavily loaded to evaluate directly under the, microscope, the collected material on the filters was dislodged in a highly purified distilled water bath using an ultrasonic unit (Dynasonic Corporation, Model G6 generator and Model 76 tank) and diluted to one liter. An aliquot of the resulting suspension was drawn, passed through a membrane filter (Millipore Type HA) and was then analyzed according to the procecure described above. PRESENTATION OF RESULTS A total of four joint compound products were used during this s t u d y , These products (two dry mix and two "ready mix") were supplied by two manufacturers whose identities were not known to the investiga tor. The products were identified by code (2D, 2R, 4D and 4R), a number referring to the supplier and the letter indicating whether the product was a "dry" or "ready-mix" compound. The results of the sampling program conducted during the mixing of the two dry mix products and sanding tests on all four joint com pounds are presented in Tables I through IV. Examination of these data revealsthe following: 1. During mixing of Joint Compound 2D, the worker was exposed to a concentration of 31.4 fibers, greater than five micro meters in length, per cubic centimeter of air. 2. The amount of total particulate generated during the sand ing operation on Joint Compound 2D was so great that direct analysis of the ten-minute samples was not possible. Anal ysis of the thirty-minute samples, which were redeposited, indicated an average concentration of 39. 4 fibers, greater than five micrometers in length,per cubic centimeter of air. 3. The results of analyzing four of the six ten-minute samples collected during sanding on Joint Compound 2R indicated an average concentration of 4.2 fibers per cubic centimeter; two of the samples were too heavily loaded to analyze di rectly. Results of analysis of the two thirty-minute sam ples collected during the sanding on Joint Compound 2R indi cated an average concentration of 11.1 fibers per cubic cen timeter, a factor of over 2.5 times as high as the average obtained from analysis of the ten-minute samples. 4. The sample obtained during the mixing of Joint Compound 4D Indicated a concentration of 7.6 fibers, greater than five micrometers in length, per cubic centimeter of air. 5. Results of analyzing four of the six ten-minute samples col lected during the sanding on Joint Compound 4D indicated an average concentration of 4.4 fibers per cubic centimeter. Analysis of the two thirty-minute samples, which were sub jected to the redepositing procedure, indicated an average concentration of 14.8 fibers per cubic centimeter, a factor of 3.4 times as high as results obtained iron the ten-ninute samp 1es . 6. The results of analysis of five of the six samples obtained during the sanding on Joint Compound 4R indicated an aver age concentration of 10.8 fibers per cubic centimeter. Re sults of analysis of the two thirty-minute samples indicated an average concentration of 9.7 fibers per cubic centimeter, a value essentially the same as that obtained from analysis of the ten-minute samples. 7. Six of the thirteen ten-minute samples obtained during sand ing on the four joint compounds indicated concentrations in excess of five fibers per cubic centimeter. Both mixing operations generated asbestos concentrations in excess of five fibers per cubic centimeter. 8. Two of the thirteen ten-minute samples collected during the sanding tests indicated concentrations in excess of ten fibers per cubic centimeter, the acceptable ceiling concen tration. One of the two mixing operations generated an as bestos-in-air concentration in excess of ten fibers per cubic centlmeter. 9. Of the four products tested, sanding on 2R and 4D resulted in concentrations less than, but approaching, the current acceptable limit for continuous exposure of workers, five fibers per cubic centimeter. Product 4R consistently pro duced very high concentrations of. total dust which obscured the asbestos fibers on the samples'. o A cn CONCLUSIONS The fallowing conclusion# are presented on the basis of observations and measurements aide during the study reported herein. 1. Based on the results of the ten-minute samples, it is appar ent that the exposures of workers engaged in mixing and sand ing of the various joint compounds used during this test would be to concentrations approaching or exceeding five fibers, greater than five micrometers in length, per cubic centimeter of air. 2. It is clear that persons engaged in the mixing and sanding cf joint compounds similar to chose used during this test would be exposed to concentrations of airborne asbestos in excess of two fibers per cubic centimeter during the entire course of their work. This value is the proposed acceptable limit for an eight-hour time-weighted average exposure to asbestos which is scheduled to become effective July 1, 1976. 3. With the exception of the tests conducted during sanding on joint compound 4R the results of analysis of the thirty-min ute samples, using the redeposition technique, were consist ently higher than those obtained by direct analysis of the ten-minute samples by a factor of 2-1/2 to 3-1/2. Therefore, it appears that use of the redeposition technique would re sult in the apparent concentrations of asbestos in air being higher than actually present and would therefore err on the "conservative" side. 4. Discounting the results obtained by analysis of the thirtyminute samples, for which the redeposition technique was used, three of the samples collected (mixing of 2D and sand ing on 4R) indicated concentrations in excess of ten fibers per cubic centimeter and are therefore a concern as peak exposures. With those exceptions, the problem is one of con trolling the time-weighted average exposures of workers to asbestos. In that respect, it must be pointed out that the sampling results reported herein are indicative of the expo sures of workers during the mixing or sanding operations and not their time-weighted average exposure for a full workday. RECOMMENDATIONS 1. The results of sampling reported herein should be analyzed in conjunction with a study of the work practices and routine of persons engaged in mixing, sanding or otherwise being exposed to joint compounds similar to those used in this study. In this vay a true evaluation of the time-weighted average exposure of such workers to asbestos can be made. If it is true that, as reported by workers used during this test, it would be unlikely for an individual to mix or sand on the joint compounds for greater than two hours per workday, then the time-weighted aver age exposure of such workers to asbestos likely would be within acceptable limits. Of course, the problem of controlling any exposures to below ten fibers per cubic centimeter would still hive to be contended with. 2. From the standpoint of being able to eliminate or minimise the problem of excessive concentrations of asbestos being generated by handling and use of the joint compounds, consideration should be given to the following aspects. a. The most effective means of eliminating the asbestos prob lem obviously would be to eliminate asbestos from the joint compound formulations if this is feasible. Although the spe cific role that asbestos plays in the joint compound formu lations is not clear it is understood that manufacturers of joint compounds consider it necessary that asbestos be in the formulat ions. b. From an engineering standpoint, it may be necessary to imple ment the following measures in conjunction with mixing and sanding of the joint compounds containing asbestos. i. Mixing of the Joint compounds could be done in such a way that the material is more effectively wetted as it is removed from the containers or could be done within an enclosure, with or without mechanical ventilation', so as to minimize the amount of asbestos fibers released into the breathing zone of the workers. ii. Although the results of the air sampling reported herein Indicate concentrations of asbestos fibers in excess of acceptable limits, either those currently enforced or those proposed to be made effective in July, 1976, it was obvious during the study that the sanding process in general has associated with it exposure of the worker to tremendously high concentrations of total dust. There fore, if means were implemented to maintain the exposure of the workers to total particulate to within acceptable limits there would be an inherent control of the asbestos problem as well. Although more extensive in nature, en gineering control of the total dust generated by the sand ing operations is feasible. Such_control techniques would '..include, but not be limited to, the use ot. a wet sanding technique and/or use of a portable local exhaust ventila tion system incorporating, as the air moving device, a _ unit similar to common industrial vacuum cleaners and bag collectors. 3. The next phase of the testing program to control workers' expo sures to asbestos during use of the joint cement compounds logi cally would be evaluations of the various potential engineering control concepts indicated or inferred above. fOi'i This report prepared by: 7 iA m v J t , -______ Robert D. Soule, P.E. Vice-President, Industrial Hygiene Services Client Gypsum Association TABLE I GEORGE D .1 CLAYTON & ASSOCIATES INDUSTRIEL HYGIENE SAMPLING SUMMARY Material AsbestoB 1 ?n* 197 3 Date Samp 1e No. JOINT COMPOUND 2D () Dfcscript ion Samp ling Perlod Start Stop Samp 1e We ight Samp 1e Vo Iume Liters Concentrt ion F lber a >5|ii/cc 11/19 11/19 1 I/ 19 11/19 11/19 11/19 .11/19 1 1/ S9 11/19 2 D- M 2D-S-1 2D-S-2 2D-S-3 2D-S-4 2 1)- S - 5 2 1)- S - 6 2D-S-7 2D-S-8 Mixing of c o m p o u n J ^ 1^ Sanding on c o m p o u n d ^ ) Sanding on compound (c ) Sanding on compound Sanding on compound(c ) ic \ Sanding on compound' ' Sanding on compound^c ^ Sanding on compound v ' Sanding on compound(c ) 0 9:28 09:34 11:57 12:27 11:57 12:07 12:07 12:17 f| 12:17 12:27 12:27 12:57 12:27 12:37 12:37 12:47 12:47 12:57 1 3 31.4 60 35.2** _ * - * - * 60 43.6** - * _ * _ * (a) (b) (c) All samples were obtained in the b r e athing zone of the workers. Mixing of Compound 2D was done by Mr. Harold McDowell In King's Mill Townhouse Unit U-81. Sanding of Compound 2D ua> done by Mr. James Pasquariello in King's Mill Townhouse Unit U-77. Psychrometric conditions in U-77 at 11:45 were 56 F dry bulb, 41*F wet bulb { 2 2 7 . relative humidity) too heavily loaded for direct analysis material on filter was taken into suspension and an aliquot redeposited for analysis TABLE II Client 1 973 Date Cypsum Asaoctatlon CEORCE D. CLAYTON & ASSOCIATES INDUSTRIAL HYGIENE SAMPLING SUMMARY Material Asbestos LI'OJ? '? )S S a m p 1e No. JOINT COMPOUND 2R (a) DkacrlptIon S a mpling Per tod Start Stop Samp 1e We 1ght Samp Ie Vo 1ume Litera Conccntrntion Fibers >5pm/cc 11/19 2R-S-I 11/19 2 R -S -2 11/19 2R-S-3 11/19 2R-S-4 1 1/ 19 2R-S-5 11/19 2R-S-6 11/19 2R-S-7 11/19 2R-S-B Sanding compound^*1) Sanding compound^) Sanding compound^) Sanding compound Sanding compound^*1) Sanding compound ^ ) Sanding compound Sanding compound 15:48 16:18 15:48 15:58 15:58 16:08 16:08 16:18 16:18 16:48 16:18 16:28 16:28 16:38 16:38 16;4B 60 20 20 2 0 60 20 20 20 1 2 . 3*< 4 .5 4.2 4 .1 9.9** * 3.8 * (a) All sample were obtained In the breathing zone of the workers. (b) Sanding of Compound 2R was done by Mr. David Potter In King's Mill Townhouse Unit U-79. Psyclirometrlc cundltlons 'in U-79 at 15:45 were 39 F dry bulb, 3 5 "F wet bulb (6671 relative humidity). * too heavily loaded for direct analysis ** mot erial on filter was taken Into suspension and an aliquot redepos ited for analysis Client 1 973 Data Gypsum Association t a b l e III GEORGE D.'CLAYTON & ASSOCIATES INDUSTRIAL' HYGIENE SAMPLING SUMMARY Material Asbestos 8 a m p 1a No. JOINT COMPOUND AD , () Description S amp 1 Ing Perlod Start Stop Samp 1e Weight Sample Voluse Litera Concentrt ion Fibers >5pm/cc 11/19 AD -M 11/19 AD-S-l 11/19 AD-S-2 11/19 AD-S-3 11/19 AD-S-A l I / 19 11/19 AD-S-5 AD-S-6 11/19 A D-S- 7 11/19 AD-S-8 Mixing compound^**) Sanding compound^0 ) Sanding compound^0) Sanding compound^0 ) Sanding compound^0 ) Sanding compound^) Sanding compound^0) Sanding compound^c^ Sanding c o m p o u n d ) 09:09 09:17 10:20 10:50 10:20 10:29 10:29 10 :A0 10 :A0 10: 50 10:50 11:00 10:50 11:20 11:00 11:10 11:10 11:20 1A A 60.0 18.0 22.0 20.0 20.0 60.0 20.0 20.0 7 .6 15.5** 5.2 * 3.7 A .1 1A .1** * A .7 () All H a p l d w a r s obtained In the breathing aone of the vorkara. (b) Mixing of Compound AD was done by Mr. Harold McDowell in King's Mill Townhouse Unit U-80. ' (c) Sanding of Compound AD was done by Mr. James P a s q u a r 1e 11o in King's Mill Townhouse Unit U-7b. Paychrometrtc conditions (dry and wet bulb t empera tures) were not recorded. * too heavily loaded for direct analysis A* material on filter was taken into suspension and an aliquot redcpos ited for analysis (.'lient 1 97 3 Date Gypsum Association T A III.K IV GEORGE D- CLAYTON 6. ASSOCIATES INDUSTRIAL HYGIENE SAMPLING SUMMARY Material Ci02 W o i Asbestos Sample No. JOINT COMPOUND 4R () Description Samp ling Period Start Stop Samp 1e Weight Samp 1e Vo 1use Liters Concentrt Ion Fibers >5|jm/cc 11/19 4R -S -l 11/19 4 R -S -2 11/19 4R-S-3 11/19 4 R - S -4 11/19 4R-S-5 11/19 4 R-S-6 11/19 4R-S-7 11/19 4R-S-8 Sanding compound Sanding compound^) Sanding comoound^) Sanding compound^) Sanding compound^) Sanding c o m p o u n d ^ ') Sanding compound^) Sanding compound^**) 14:31 15:01 14:31 14:41 14:41 14:51 14:51 15:01 15:01 15:31 15:01 15:11 15:11 VOID 15:18 15:31 60.0 20.0 20.0 20.0 60.0 20.0 26.0 11.3** 6.3 7 .5 19.9 8.1** 5. 3 _ 15.0 (a) All samples vert obtained in the b r e athing cone of the workers. (b) Sanding of Compound 4 R v a a done by Mr. David Potter In King's Mill Townhouse Unit U-7B. Ps ychr ome tr ic cond it Ions 'In U-78 at' 14:45 were 44*F dry bulb, 38*F wet bulb (68* relative humidity). ** material on filter was taken into suspension and an aliquot redeposited for analysis ' 1