Document 933qxrww7web76me0MwG2Boyq

pfevf* r-ebifw '$0 Reprinted from the Archives ot Environmental Health January 1971, Volume 22 Copyright 1971, American Medical Association E. P. Wbeeiaf Occupational Acroosteolysis II. An Industrial Hygiene Study Warren A. Cook; Paul M. Giever, MPH; Bertram D. Dinman, MD, ScD; and Harold J. Magrmson, MD, MPH, Aim Arbor, Mich AS V 00QB53Z 74 Occupational Acroosteolysis II. An Industrial Hygiene Study Warren A. Cook; Paul M. Giever, MPH; Bertram D. Dinman, MD, ScD; and Harold J. Magnuaon. MD, MPH, Ann Arbor, Mich An Industrial hygiene survey was conducted in respect to oceupstional acroosteolysis (AOL) in 32 plants engaged in production and compound ing of polyvinyl chloride. This survey was limited to inspection of facilities, interrogation of tech nical personnel, and statistical analyses. All manufacturing processes and chemicals utilized were explored. A major objective was the iden tification of variables in processes and chemicals that wars peculiar to those plants affording known cases of AOL No such processes or chemicals were found. The survey brought to light a num ber of situations suspected of relationship to the precise cause of AOL some of which require additional exploration. Moat positive ol these was the finding that essentially all of the persons who developed AOL had served as reactor cleaners using manual methods. Polyvinyl chloride (PVC) has been in production, and widespread use for more than 30 years. An extensive account of the chemistry, methods of production, materials utilized, properties, and uses of the PVC resins was recently published in a series of technical articles by. Albright.15 Uses in clude such diverse products as floor tiles, films for food wrappings, sheeting for show er curtains, phonographic records, and coat ings for cables. As an indication of the magnitude of the PVC industry, the average operating capaci ty in this country for the year 1969 was about 3 billion lb.* Much PVC is produced in other countries. Even with this extensive production involving thousands of operators, the occurrence of occupational acroosteolysis (AOL) among these workers was not recog nized until about 1961.T Submitted for publication Feb 9, 1970; accepted April 16, 1970. From the Institute of Environmental end Indus trial Health, University of Michigan. Ann Arbor. Read before the American Industrial Hygiene Conference, Denver, May 15, 1969. Repript request* to School of Public Health, University of Michigan, Ann Arbor, Mich 48104 (Dr. Dinman). The clinical and epidemiological aspects of this condition are discussed in separate papers in this issue of the archives.8-8 Industrial Hygiene Survey Surveys were made of 32 plants by the authors of this paper, most of the plants being visited by a team of one physician and one industrial hygienist. Twenty-six of these were polymer production plants. Vinyl chloride mon omer production plants and plants engaged in compounding and fabricating of the polymer ized resin were a part of the manufacturing complex at a number of these locations. Five plants conducted compounding and fabricating operations only, and one plant produced only the vinyl chloride monomer. These plants were located throughout the United States and cne in Canada. This survey was designed to obtain informa tion on equipment used, procedures followed, materials involved, extent of exposure to these, and names and descriptions of jobs in order to compare practices in the plants where cases of AOL occurred with those in plants experienc ing no cases. The extent of exposures was estimated on the basis of general observation, a knowledge of the physical, chemical, and physiologies! prop- Arch Environ Health--Vol 22. Jan 1971 RSV 0008533 OCCUPATIONAL ACROOSTEOLYSIS--COOK ET AL VC ICC STILL 75 Fig I.--Flow diagram for production of PVC from vinyl chloride monomer. erties of the material*, and discussion with technically informed persons at the plants. By setting up three broad categories of duration and of relative severity of the exposure, semi* quantitative estimates were made. Since mate rials responsible for causing AOL might be absorbed either through the respiratory tract or through the skin or both, such estimates were made for each of these avenues of absorption. Production Operations Vinyl Chloride Production.--The two processes for production of vinyl chloride described by Albright12 were found to be in current use. One of these involves the reac tion of hydrogen chloride with acetylene in the presence of a mercuric chloride catalyst. In the other process, 1, 2-dichloroethane is pyrolyzed in the presence of chlorine as a catalyst for the production of vinyl chloride and HC1. In some plants, both methods were used, with the HCl produced in the latter of these processes being used in the former. Polyvinyl Chloride Production.--Poly vinyl chloride can be produced in accord ance with four processes, each with many variations among different plants. The final polymer may have a molecular weight vary ing from 50,000 to 150,000, depending on conditions under which it is produced. The production processes are designated as sus pension, emulsion, bulk (or nonsolvent), and solvent. A typical procedure is present ed in the flow-sheet (Fig 1). The essential steps of these operations are outlined in this paper. For more complete details, reference may be made to the papers by Albright.n -'' In the widely used suspension process, deion ized water is first introduced into a large auto clave, usually glass-lined, followed by a wide variety of additives. These include suspending agents such as polyvinyl alcohol, methyl cellu-lose, and gelatin, emulsifying agents such as sulfonated oils, surfactants such as gorbitan monolaurate, and buffers such as sodium bicar bonate. Trichloroethylene may be added to pro duce the lower molecular weight polymers. Cat alysts are added to initiate the polymerization. These are nearly all organic peroxides, with lauroyl peroxide and diisopropylperoxydicarbonate (IPP) being used at the greater number of plants. The reactor is then closed, evacuated to remove oxygen, and vinyl chlo ride, normally a gas, is piped in as a liquid under pressure from the tank farm or the vinyl chloride plant. In some plants, the catalyst is added to a charge tank from which it is intro duced into the closed reactor following addition of the vinyl chloride. The mixture is agitated with rotating propel ler blades, and steam initially is directed into the reactor jacket to raise the temperature to 50 or 55 C. Since the polymerization reaction is exothermic, cooling water must be run into the jacket after the reaction has begun tD avoid excessive heating. After ten to 16 hours, the polymerization is essentially complete, and the reactor is brought down to atmospheric pres sure. In most plants, it is placed under vacuum for removal of unpolymerized vinyl chloride monomer and transfer to the monomer recov ery area. The suspension of PVC is then dis charged into a blowdown tank below the reac tor. This tank is placed under vacuum for transfer of remaining vinyl chloride to the recovery area. In some plants, the blowdown tank is eliminated. The general appearance of the charging floor of a polymer plant is shown Arch Environ Health--Vol 22. Jan 1971 RSV 0008334 76 OCCUPATIONAL ACROOSTEOLYSIS--COOK ET AL Fig 2.-Charging floor of PVC production plant showing top portion of reactor*. in Fig 2. The reactors extend for ten feet or so down to the floor below. The polymer slurry is pumped to blend tanks, then to centrifuges for removal of much of the water. The dewatered polymer is passed through a rotary dryer with heated air, the temperature of the polymer being kept below 140 F to avoid degradation. The dried granular polymer is pneumatically conveyed into a cy clone separator, with finer particles being re moved from the air stream by means of a filter-type collector. The polymer particles are sized by vibrating screens, then bagged for transfer to compounding and fabricating plants or shipped in bulk. In some plants, the polymer is stored in bins prior to being shipped. In the emulsion process, the equipment and process is essentially the same as in the suspen sion process up to the drying operations. In order to produce the finer polymer particles characteristic of the emulsion process, a wide variety of emulsifying agents is used. These may be soaps such as ammonium or sodium laurate, surfactants such as salts of naphthalene sulfonic acid, or various synthetic detergents. Water-soluble initiators such as ammonium persulfate and hydrogen peroxide are used as catalysts. Since the fine polymer particles can not be readily separated from the emulsion by centrifuging or filtering, a spray dryer is em ployed in this process. The bulk process is similar to suspension polymerization but is characterized by the pre cipitation of the polymer from the liquid phase, as about 10% of the vinyl chloride becomes polymerized. Solution polymerization is much the same as suspension polymerization, but no water is in troduced. Instead, the polymerization is con ducted in such solvents as cyclohexane, acetone, or n-butane. Copolymer and Terpolymer Production. --In addition to the production of the homopolymer PVC, many of the plants also produce copolymer and terpolymere, includ ing vinyl chloride. The greater percentage of the monomer tends to be the vinyl chloride in ail of these. The copolymer vinyl chlor ide-vinyl acetate is in highest production Arch Environ Health--Vn! 22, -inn 1971 RSV 0008935 OCCUPATIONAL ACBOOSTEOLYSIS--COOK ET AL 77 among this group but is a Table l.--Abaofuto Prmaturt-TImm Valuta minor product in compan ion to the homopolymer. Absolute Pressure-Time Values Below 10 Absolute Pressure -Time Values of 10 or Above Other copolymers are vinyl chloride-vinylidene chloride and vinyl chloride-lauryl- Plant Code No. of No. of Reactor Expected Cleaners AOL Cases Plant Code No. of No. of Reactor Expected Cleaners AOL Cases vinyl ether. An example of a terpolymer is vinyl chloride-n-butyl maleate-dibutyl maleate. Processes, additives, and catalysts essentially identi Plants With AOL Cases EE 31 o.a B E F R Plants With Possible AOL Cases CC 32 0.9 Totals 63 1.7 216 165 16 39 436 5.8 4.5 0.4 l.l 11.8 cal to those used for the homopolymer are employed in the production of the co polymers and terpolymers with the addition to the re action mixture of the addi tional monomers. Vinyl Chloride Recovery.-- The unpolymerized vinyl chloride removed from the P Q V w Totals DO Totals 30 22 91 50 193 Plants With No AOL Cases 0.B O 0.6 H 2.5 L 1.4 S T Z AA 5.3 27 26 2B 17 9 17 e 132 Plants Started in Operation in 1965 or 1966 21 0.6 C 54 J 13 21 0.6 67 0.7 0.7 0.8 0.5 0.2 0.5 0.2 3.6 1.5 0.4 1.9 batch following completion of polymerization is conveyed to a vinyl chloride recovery area Tabla 2.---CfslffeUon of Standard Job Tltioa by the suction pump that Job Title Code Job Title Code places the reactor and the stripping tank under reduced pressure- Here the vinyl chlo ride gas that is removed is placed under pressure to con dense it together with water vapor to a liquid. The water and the vinyl chloride are im miscible, permitting their sep aration. Zn aome plants, an inhibitor, usually phenol, is added to the vinyl chloride Additive makeup (other 1 than catalyst) Bagging and shipping operator 2 Catalyst makeup man 3 Clerical, other office, staff 4 Compounding and fabricating 5 Dryer operator 6 General laborer, custodial 7 Laboratory supervisor a Laboratory technician 9 Maintenance, electrical 10 Maintenance, mechanical 11 Monomer maintenance operator 12 Monomer operator 13 Monomer recovery operator Monomer supervisor Plant guard, security office' Reactor cleaner Reactor cleaner, solvent Reactor oparator Blurry blender Supervisor, polymer Tsnk farm operator Utilities area operator (water treatment, etc) Warehouse operator Transfer operator Other than PVC 14 15 16 17 18 19 2D 21 22 23 24 25 30 to prevent spontaneous poly merization during its distillation, the method due on the agitator blades may require hammer used for its purification. The recovered vinyl and chisel for removal and sometimes even chloride, with the higher boiling phenol remain axes. ing in the still, is then pumped to storage for Four plants use water jets with pressures of reuse. from 300 to 3,000 lb/gq in for the cleaning Reactor Cleaning Operation*.--After the operation. One of these used water jets only in polymer has been discharged from the reactor one of two production buildings, as the struc- and the pressure brought to atmospheric, the tional features interfered with movement of the reactor is aerated. This is accomplished by portable high-pressure water unit about the dropping a flexible duct connected to a portable building. Three other plants have been using blower to the bottom of the reactor, with dis solvents for reactor cleaning. One of these charge normally through the open manhole at started to use this method late in 1964, a the top of the reactor into the charging-floor second in 1966. and the third from the begin area. The loose residue is washed out with ning of plant operation in 1966. The reactor is water, after which one or two men enter the filled with the solvent which must be heated reactor to remove the akin of polymer remain and agitated for a prolonged period, as the ing on the reactor surfaces. The usual method PVC is difficulty soluble. is hy manual scraping with putty knives. Resi Polyvinyl Chloride Compounding--Com- Arch Environ Health--Vnl 22, Jon 797/ 1 RSV 000&536 78 OCCUPATIONAL ACROOSTEOLYSIS--COOK ET AL Tibia 3.--Magnitude of Dosaga Expressed as Slngla Concept at a weekly, monthly, or Magnitude* of Dosage Slight 1 2 3 A 5 6 Intermediate 7 B 9 10 11 12 Severity/Oui'ation Exposure Pa rameterst Less Than 1 hr/Week 1-8 hr/week More Than 8 hr/Week Negligible Moderate Moderate Moderate None Negligible None Negligible None None Negligible None None Negligible Aporeciable Appreciable Appreciable None Negligible Moderate Moderate None None Negligible None Negligible Moderate other period. A classification of 26 job titles for the statistical pur poses of this study was pre pared (Table 1). These job titles corresponded to com parable operations in all the plants and to a common group of types of exposures to production materials. Ev ery job in each of the plants was given its fraction of time related to the job title as defined for the study. De Major 13 14 15 16 17 18 Appreciable Appreciable Moderate Appreciable Appreciable Appreciable None Moderate None Negligible Moderate Appreciable * Expressed in order of increasing dosage received from exposure, which is the summation of the three columns to the right. t Severity of exposure is estimated as none, negligible, moderate, or appreciable for indicated durations. tails of the manner in which this was done are discussed in the accompanying paper on epidemiological aspects of AOL.8 Job Progression.--Often the first job assignment of the new employee is that of reactor cleaner. Unless there pounding consists of mixing PVC with a multi plicity of plasticizers, antioxidants, pigments, emulsifiers, stabilizers, and other special com pounds in ribbon blenders and mills. The mix tures are then passed through roll mills or mixers, such as are used in the rubber industry, where the temperature may rise sufficiently to vaporize some of the plasticizer and other vola tile constituents. The compounded polymer is then extruded through. rolls or dies to fonn are many reactors, this work does not require the entire time of the employee. Part of his time may be spent in bagging or shipping finished polymer or in the handling of cata lysts and other additives. As job openings arise and with accretion of seniority, this employee may progress to higher skilled jobs such as reactor, monomer recovery or dryer operator, or any combina sheets, films, or pellets. These are used in tion of these at any one time. fabricating operations. In plants producing other products in ad Job Classification dition to vinyl chloride polymers, employees may transfer between these product areas Many variables were introduced in the either as full time for a period of months or plants surveyed and even in different units dividing their time within a given week or of the same plant in regard to nearly every even day. The latter occurs particularly phase of the operations. Investigation of among maintenance personnel. unit jobs in the plants disclosed a wide Where production of vinyl chloride is part assortment of job titles. In fact, a job title as of the operation, operators may rotate be used by the technical supervisors often dif tween job6 in the production of the mono fered from that for the same job in the mer and those associated with the produc same plant as listed by the personnel de tion of the polymer. partment. The length of time spent at various jobs is Furthermore, a job assignment in one a function of production needs, economic plant might include a different group of unit conditions, plant growth rates, and activity operations than in another plant. Also, the of other product lines. proportion of time devoted to the several unit operations often differed. To compound Occupational Exposures to Materials the difficulties of classification, workers Extent of Exposures.---Information was would frequently rotate through several jobs obtained not only on each of the materials Arch Environ Health--Vol 22, Jan 1971 RSV 000S53? OCCUPATIONAL ACROOSTEOLYSIS--COOK ET AL 79 used or produced but also on the extent of exposure to each. Since this is a function of both duration and severity, each of these factors was estimated. The duration of expo* sure was recorded as less than one hour a week, from one to eight hours a week, or more than eight hours a week; the severity as negligible, moderate, or appreciable. Sinoe it was not known whether the materi als might be absorbed through the re spiratory tract, through the skin, or both, the extent of exposure as related to each of these avenues of absorption was recorded. For statistical purposes, it was desirable to combine these two factors of exposure into a single dose value. Although admitted ly the effect of exposure to materials with differing physiological responses would vary somewhat with different combinations of de grees of duration and severity, the 18 possi ble combinations of duration and severity were listed in increasing order of dosage and classified in three groups of dose values des ignated as slight, intermediate, or major. These combinations are presented in Table 2. Materials Involved.--A total of 227 different materials were used or produced in the forma tion of PVG, the copolymer vinyl chloride-vinyl acetate, and other copolymers and terpoiymers incorporating vinyl chloride. These materials included monomers, polymers, catalysts, disper sants, inorganic compounds for coalescence reg ulation, emulsifying agents, surfactants, and or ganic solvents (including hydrocarbons, both aliphatic and aromatic, ketones, esters, and chlorinated hydrocarbons). This total of 227 materials does not include the many more used in the compounding and fabricating plants. A computer analysis of exposures to these materials was undertaken, but up to the pres ent time, this hn disclosed no constellation of materials introduced into the batch at the plants exhibiting cases of AOL that was not used in plants without cases. However, special consideration was given to certain suspect ma terials and also to certain details of procedure. Vinyl Chloride Exposures.--In evaluating the role of vinyl chloride as a possible in fluence in the causation of AOL, the esti mates of the extent of the exposure of re actor cleaners and reactor operators were reviewed. Since the authors conducted no air analyses, they had to judge the presence of vinyl' chloride in the charging floor area principally on the basis of general ventila- Tablt 4.--Use ot Inhibitors With Vinyl Chloride Use of Inhibitors Plants with AOL cases or possible cases Plants without AOL eases In Virgin Vinyl Chloride In Vinyl Chloride Recovery 22 34 tion provided and odor observed. The odor of vinyl chloride could be detected in the immediate vicinity of reactors as they were first opened and also when they were first being vented into the charging room area. Air analyses conducted by others have shown vinyl chloride concentrations in the reactor prior to ventilating to be in the order of 3,000 ppm. The lower limit of detection of vinyl chloride by odor is accept ed as 400 ppm. Except under the foregoing conditions, the odor of vinyl chloride was not observed in the general room air. The reactor cleaner enters the reactor af ter the aeration has reduced the vinyl chlor ide exposure to what is considered satisfac tory limits, normally 15 or 20 minutes. The test is either by sniffing at the manhole opening or by use of a flammable vapor indicator. With the lower explosive limit of vinyl chloride at 4%, it requires 400 ppm for the usual type of flammable vapor indi cator to give a positive reading. Where air analyses have been made in a small number of plants with more sensitive instruments, such as the gas chromatograph, it has been found that the vinyl chloride concentration inside the reactor during scraping operations tends to be below 100 ppm and usually about 50 ppm. With the residue containing some unpolymerized vi nyl chloride, small amounts of this gas are released as scraping is carried on. Air anal yses have shown vinyl chloride concentra tions close to the hand during scraping in the range of 600 to 1,000 ppm. Although this study provided no evidence to suggest that vinyl chloride per se is the etiological agent, the measurement of vinyl chloride concentrations may serve as a use ful index to the adequacy of reactor ventila tion. Inhibitors in Vinyl Chloride.--An inhibi tor, usually phenol, may be added to the Arch Environ Health--Vol 22, Jan 1971 RSV 000853d 80 OCCUPATIONAL ACROOSTEOLYS1S--COOK ET AL Table S.--Reactor Cleaning Procedures as a possible factor in the Hind Sc*o>ns Plant Attar Every Coda Bateh Less Than Every Cycle Plants with AOL eases BX EX FX KX (through 1964) RX U Every 5-12 cycles (building A) EE X Plants with possible AOL cases BB Every "several" cycles Cleaning by Water Jet From 1965 From 1962 (building B) Cleaning by Solvent mtl*rmittnuy m 1966. entirety causation of AOL. Contact with these inorganic and or ganic peroxides occurs as they are handled prior to their introduction into the reactor and alao during re actor cleaning if any unre acted catalyst remains in the residue. Twenty-two of the 26 plants used lauroyl perox ide. Eight of these were plants with AOL cases or passible AOL cases, and 14 were plants without AOL cases. The next most com- Plants with no AOL cases (to September 1964) X From 1962 1966 C*mMr ------------------------- From September is* mon organic peroxide was the IPP, and it, too, was in use in both the positive and the negative plants, in four of the former and in eight of the latter. No catalyst or Every 2'h cycles Every 4-8 Says WeeKJy From 1965 through 1964, every 2 wee'is 1965-1966 0X SX T X Every 1-3 cycles (emulsion) (suspension) V Every 10 cycles ZX AA Every 4 or more cycles DO X GG From start of operations group of catalysts was used in all positive plants and in no negative plants. Constituents of Scrapings. --Other suspect materials are constituents of scrapings removed from the reactors during manual cleaning. These are believed to include some partially polymerized resins, along with some un reacted catalysts and additives, and unpolymerized vinyl chloride. Little specif vinyl chloride to prevent spontaneous poly merization in storage. An inhibitor may also be added to the vinyl chloride recovered from the reactor. The phenol is removed by treatment with caustic soda prior to its transfer to the reactor. The practice over the years covered by the study is presented in ic information is currently available concerning these constituents. It has been reported that lauroyl peroxide is definite ly associated with residual PVC particles, whereas little of the IPP remains unreacted in the polymer.1 Further investigation of the scrapings from the reactor may be expected to furnish Table 3. The use of the inhibitor in the virgin vinyl chloride at two of the positive plants and three of the negative plants, with inhibitor being added in the vinyl chloride recovery operation in two positive plants information that may lead to a better under standing of the factors involved in causation of AOL. A difficulty in such investigation is that the composition of the scrapings is continually changing from the time they are and four negative plants, leads to the con clusion that inhibitors probably are not a factor in AOL causation. Catalyst Exposures.--Since the catalysts removed from the surfaces of the reactor. It is obvious that comparatively small mole cules of partially polymerized vinyl chloride are increasing in size with passage of time, are all active compounds, they were suspect and active constituents such as residual cat- Arrh Environ Health--Vol 22. -Jan 197J RSV 0008539 OCCUPATIONAL ACROOSTEOLYSIS--COOK ET AL 81 Tabla 6.--ftuctor Cleaning Procedure* Method Manual scraping after every reactor cycia Manual scraping attar 2 3 cyclts Manual sereping after 4-12 cycias Water-iet cleaning Organic iolvent cleaning Positive Plants 7 0 2 2 1 Negative Plants 9 2 4 2 2 alyst and vinyl chloride monomer are de creasing or may no longer be present Procedures Affecting Exposures oi Reactor Cleaners Since all but one of the 25 operators diagnosed as positive for AOL had worked as reactor cleaners and the one exception had cleaned laboratory reactors,* additional inquiry was made of procedures that might affect the exposures of this group of workers. Reactor Cleaning Procedure---The number of man hours required to clean the reactors depended not only on the number of reactors but also on the frequency of cleaning. In 16 of the 26 production plants, reactors were manual ly cleaned after every batch. This was true of six of the seven positive plants and one of two plants with possible AOL cases. In only nine of the 17 plants with no AOL cases were reactors manually scraped after every batch. The procedures followed in each of these plants anpears in Table 4 and an analysis of the types of procedure by positive and nega tive plants in Table 5. Procedures Following Completion of Poly merization.--Since vinyl chloride and other vol atile components of the residue remaining on the reactor surfaces following discharge of the batch might be factors in AOL causation, infor mation was obtained concerning the degree of vacuum applied to the reactor prior to opening it and the length of tiw that the reactor was under this reduced pressure. The amount of volatile materials remaining in the residue on the reactor surfaces was considered to be roughly proportional to the absolute pressure and inversely proportional to some function of the time. Since the rate of removal of volatile material would tend to decrease with time, the logarithm of this factor was used in calculating an absolute pressure-time (AP-T) value. Tt was hypothesized that the relative amount of vola tile materials remaining in the residue follow ing application of vacuum would approximate a nondimensional value obtained by dividing the absolute pressure in inches of mercury by the logarithm of the time in minutes during which the vacuum was applied. Thus, the lower the AP-T value, the less is the amount of volatile materials remaining in the residue. Another factor affecting removal of vola tile materials is the temperature range over the period that the reactor is under vacuum. The variables in temperature control were so diverse that this factor defied classi fication and could not be incorporated in the parameter under consideration. Actually, variations In degree of vacuum and timing of its application were such that meaningful calculation of an AP-T value could be ac complished only for five of the seven posi tive plants, one of the two with possible cases, and 14 of the 17 negative plants. In the subsequent discussion of these val ues, the three plants that started in opera tion as recently as 1965 and 1966, all with no AOL cases, are not included as it is not known whether sufficient time had elapsed for cases to have developed by the terminal date of the study period. These plants are listed separately in Table 6. The AP-T values ranged from 0.5 to 21. The AP-T values were 10 or above (an entirely arbitrary division line) for four of the live positive plants and for one of the two plants with possible AOL cases. Four of the negative plants gave AP-T values below 10, and seven gave values of 10 or above. Consideration is directed to the number of reactor cleaners and the corresponding num ber of expected AOL cases in the two groups of positive plants as compared with those in the negative plants. The total number of reactor cleaners at risk in the positive or possibly positive plants with an AP-T value of less than 10 is 63; that in such plants with an AP-T value of 10 or more is 436. The relation of these two totals is to be compared with that of the negative plants in which 193 reactor clean ers at risk are in the four plants with an AP-T of less than 10 and 132 are in the seven plants with an AP-T above that value. The number of expected cases of AOL for each plant is also listed in Table 6. Thane values were obtained by dividing the num ber of reactor cleaners at risk by 37 This Arch Environ Health--Voi 22. Jan !97l RSV 0000540 62 OCCUPATIONAL ACROOSTEOLYSIS--COOK ET AL figure derives from the paper on epidemio logical aspects of AOLa which reports the prevalence of AOL or possible AOL as one case per 37 reactor cleaners at risk. Of the negative plants with an AP-T val ue of 10 or more, none of those in operation earlier than 1965 had enough reactor clean ers at risk to expect an AOL case, whereas two of the four plants with an AP-T value under 10 have enough workers to expect cases. Cases would be expected from the total population of reactor cleaners in the entire group of the seven negative plants with AP-T values of 10 or more, but the total number would be 3.6, as compared with 5.3 expected cases from the entire group of four negative plants with an AP-T value of less than 10. This contrasts with expected cases in the group of positive plants with an AP-T value of less than 10 as 1.7, compared with 11.8 in such plants with an AP-T value of 10 or more The proportion of the number of reactor cleaners in the negative plants with an AP-T value of less than 10 to the total number in such plants was 193 to 325. This propor tion for the positive plants was 63 to 499. A Xs test demonstrated that the probability of this difference between the negative and the positive plants occurring by chance is less than 0.001. In order to make this comparison between the positive and negative plants with AP-T values below and above 10, it was necessary to oversimplify a multiplicity of varying de tails of operational procedures from the time the polymerization is completed to the time the cleaner enters the reactor. Accordingly, any interpretation of the findings that re duction of the AP-T value below 10 by reducing the absolute pressure or keeping the reactor at reduced pressure for a longer time or both may results in reduction in development of AOL cases should be ap proached with great caution. Preventive Measures The present knowledge as to AOL is such that categoric statements as to preventive measures are not justified. However, on a somewhat speculative basis, some measures are indicated that may be conducive to AOL prevention: 1. Although some manual removal of resi due from reactor surfaces may be required when solvents or high-pressure water jets are used for cleaning, the more extensive employment of these methods would greatly reduce the number of man hours required for conducting this operation by manual methods. 2- The adequacy of ventilation of reactors prior to entry should be checked with flammable vapor indicator equipped with a scale of greater sensitivity than 1% of the lower explosive limit of vinyl chloride or with other instruments of such sensitivity. 3. Further investigation of the constituen cy of the scrapings from the reactor surfaces should be considered, as such information might disclose the factor responsible for the causation of the disease. References 1. Albright LF: Vinyl chloride processes. Chem Eng 74:123-130. 1967. 2. Albright LF: Msnufsctuie of vinyl chloride. Chem Eng 74:219-226. 1967. 3. Albright LF: Polymerization of vinyl chloride. Chem Eng 74:151-158. 1967. 4. Albrigbt LF: Vinyl chloride polymerization by suspension processes yields polyvinyl chloride res ins. Chem Eng 74:145-152. 1967. 5. Albright LF: Vinyl chloride polymerization by emulsion, bulk sod solution processes. Chem Eng 74:85-92, 1967. 6. PVC producers. Chem Eng Neve 47:18-19, 1969. 7. Wilson RH. McCormick WE, Tstum CF, et e): Occupations! eerooeteolysis: Report of 31 curs JAMA 201:577-581, 1967. 8. Dinman BD, Cook WA, Whitehouse WM. et I: Occupational acrooateolysis: I. An epidemiologi cal study. Arch Environ ffeolfh 22:61-73, 1971. 9. Dodson VN, Dinman BD, Whitehouse WM. et al: Occupational scroosteolysis: III. A clinical tu4y. Arch Environ Health 22:83-91. 1971. Arch Environ Health--Vol 22, Jan 1971 Printed end Published m the United States ol America RSV 00085^1