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Engineering Controls

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The manufacture of tyres and other rubber products exposes workers to a large variety of chemicals. These include many different powders, solids, oils and polymers used as compounding ingredients; anti-tack dusts to prevent sticking; mist, fumes and vapours generated by heating and curing rubber compounds; and solvents used for cements and process aids. The health effects related to most of these are not well known, except that they are usually chronic in nature rather than acute at typical exposure levels. Engineering controls are generally aimed at overall reduction of the level of dust, heated rubber emissions or curing fumes to which workers are exposed. Where there is exposure to specific chemicals, solvents or agents (such as noise) that are known to be harmful, control efforts can be targeted more specifically and in many cases the exposure can be eliminated.

Elimination or substitution of harmful materials is perhaps the most effective means of engineering control of hazards in rubber manufacturing. For example, β-naphthylamine contained as an impurity in an anti-oxidant was identified in the 1950s as a cause of bladder cancer and was banned. Benzene was once a common solvent but has been replaced since the 1950s by naphtha, or white gasoline, in which the benzene content has been steadily reduced (from 4-7% to commonly less than 0.1% of the mixture). Heptane has been used as a substitute for hexane and works just as well or better. Lead sheathing is being replaced by other materials for curing hose. Rubber compounds are being designed to reduce dermatitis in handling and the formation of nitrosamines in curing. Talcs used for anti-tack purposes are selected for low asbestos and silica content.

Rubber Compounding

Local exhaust ventilation is used for control of dust, mist and fumes in rubber compound preparation and mixing and in finishing processes involving buffing and grinding of rubber products (see figure 1). With good work practices and ventilation designs, dust exposures are usually well under 2 mg/m3. Effective maintenance of filters, hoods and mechanical equipment is an essential element of engineering control. Specific hood designs are given in the American Conference of Governmental Industrial Hygienists ventilation manual and the Rubber and the Plastics Research Association of Great Britain ventilation handbook (ACGIH 1995).

Figure 1. A canopy hood controls fumes in finishing a tube casting at an industrial rubber plant in Italy

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Compounding chemicals have traditionally been scooped from bins into small bags on a weighing scale, then placed on a conveyor to be poured into the mixer or onto a mill. Dust exposures are controlled by a slotted side-draft hood behind the scale (see figure 2). and in some cases by slotted hoods at the edge of the stock bins. Dust control in this process is improved by substituting larger-particle-sized or granular forms for powders, by combining ingredients in a single (often heat-sealed) bag and by feeding compounds automatically from the storage bin to the transfer bag or directly to the mixer. Operator work practices also strongly influence the amount of dust exposure.

Figure 2. Slotted local exhaust ventilation at a compound weighing station

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The Banbury mixer requires an effective enclosing hood to capture the dust from charging and to collect the fumes and oil mist coming from the heated rubber as it mixes. Well-designed hoods are often disrupted by drafts from pedestal fans used to cool the operator. Powered equipment is available to carry bags from pallets to the charging conveyor.

Mills are provided with canopy hoods to capture emissions of oil mist, vapours and fumes rising from the hot rubber. Unless more enclosed, these hoods are less effective in capturing dust when compounds are mixed on the mill or the mill is dusted with anti-tack powders (see figure 3). They are also sensitive to drafts from pedestal fans or misdirected general ventilation make-up air. A push-pull design has been used which places an air curtain in front of the operator directed up into the canopy. Mills are often raised to put the roller nip point out of the operator’s reach, and they also have a trip wire or bar in front of the operator to stop the mill in an emergency. Bulky gloves are worn that will be pulled into the nip before the fingers are caught.

Figure 3. A curtain at the edge of a canopy hood over a mixing mill helps contain dust.

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Rubber slabs taken off mills and calenders are coated to keep them from sticking together. This is sometimes done by dusting the rubber with powder, but is now more often done by dipping it in a water bath (see figure 4). Applying the anti-tack compound this way greatly reduces dust exposure and improves housekeeping.

Figure 4. A rubber strip taken from a Banbury batch-off mill goes through a water bath to apply anti-tack compound.

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Ray C. Woodcock

Dust and fumes are ducted to bag-house or cartridge-type dust collectors. In large installations, air is sometimes recirculated back into the factory. In that case, leak detection equipment is necessary to be sure contaminants are not recirculated. Odours from some ingredients such as animal glue make air recirculation undesirable. Rubber dust burns easily, so fire and explosion protection for ductwork and dust collectors are important considerations. Sulphur and explosive dusts such as cornstarch also have special fire-protection requirements.

Rubber Processing

Local exhaust hoods are often used at extruder heads to capture mist and vapours from the hot extrusion, which may then be directed into a water bath to cool it and suppress the emissions. Hoods are also used at many other emission points in the factory, such as grinders, dip tanks and laboratory test equipment, where air contaminants can easily be collected at the source.

The numbers and physical configurations of building stations for tyres and other products usually make them unsuitable for local exhaust ventilation. Confinement of solvents to covered containers as much as possible, along with careful work practices and adequate dilution air volume in the work area, are important for keeping exposures low. Gloves or applicator tools are used to minimize skin contact.

Curing presses and vulcanizers release large amounts of hot curing fumes when they are opened. Most of the visible emission is oil mist, but the mixture is also rich in many other organic compounds. Dilution ventilation is the control measure most often used, often in combination with canopy hoods or curtained enclosures over individual vulcanizers or groups of presses. Large volumes of air are required which, if not replaced by adequate make-up air, can disrupt ventilation and hoods in connecting buildings or departments. Operators should be positioned outside the hood or enclosure. If they must be under the hood, downdraft fresh air ventilators can be placed over their work stations. Otherwise, replacement air should be introduced adjacent to the enclosures but not directed into the canopy. The British occupational exposure limit for rubber curing fumes is 0.6 mg/m3 of cyclohexane soluble material, which is normally feasible with good practice and ventilation design.

Making and applying rubber cement presents special engineering control requirements for solvents. Mixing churns are sealed and vented to a solvent recovery system, while dilution ventilation controls vapour levels in the work area. The highest operator exposures come from reaching into churns to clean them. In applying rubber cement to fabric, a combination of local exhaust ventilation at emission points, covered containers, general ventilation in the workroom and properly directed make-up air controls worker exposure. Drying ovens are exhausted directly, or sometimes air is recirculated in the oven before it is exhausted. Carbon adsorption solvent recovery systems are the most common air-cleaning device. Recovered solvent is returned to the process. Fire-protection standards require that the flammable vapour concentration in the oven be maintained below 25% lower explosion limit (LEL), unless continuous monitoring and automatic controls are provided to ensure that the vapour concentration does not exceed 50% LEL (NFPA 1995).

Automation of processes and equipment often lowers exposure to airborne contaminants and physical agents by placing the operator at a greater distance, by confining the source or by reducing the generation of the hazard. Less physical strain on the body is also an important benefit of automation in processes and material handling.

Noise Control

Significant noise exposures often come from equipment such as braiders and belt grinders, air-exhaust ports, compressed air leaks and steam leaks. Noise-reducing enclosures are effective for braiders and grinders. Very effective silencers are made for air-exhaust ports. In some cases the ports can be ducted to a common header that vents elsewhere. Air noise from leaks can often be reduced by better maintenance, enclosure, design or good work practices to limit the noise cycle.

Work Practices

To prevent dermatitis and rubber allergies, rubber chemicals and fresh rubber batches should not come in contact with the skin. Where engineering controls are insufficient for this, long gauntlet gloves, or gloves and long-sleeved shirts, should be used to keep powders and rubber slabs off the skin. Work clothes should be kept separate from street clothing. Showers are recommended before changing to street clothing to remove residual contaminants from the skin.

Other protective equipment such as hearing protection and respirators may also be necessary at times. However, good practice dictates that priority always be given to substitution or other engineering solutions to reduce hazardous exposures in the workplace.

 

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Contents

Rubber Industry References

American Conference of Governmental Industrial Hygienists (ACGIH). 1995. Industrial Ventilation: A Manual of Recommended Practice, 22nd ed. Cincinnati: OH: ACGIH.

Andjelkovich, D, JD Taulbee, and MJ Symons. 1976. Mortality experience in a cohort of rubber workers, 1964–1973. J Occup Med 18:386–394.

Andjelkovich, D, H Abdelghany, RM Mathew, and S Blum. 1988. Lung cancer case-control study in a rubber manufacturing plant. Am J Ind Med 14:559–574.

Arp, EW, PH Wolf, and H Checkoway. 1983. Lymphocytic leukemia and exposures to benzene and other solvents in the rubber industry. J Occup Med 25:598–602.

Bernardinelli, L, RD Marco, and C Tinelli. 1987. Cancer mortality in an Italian rubber factory. Br J Ind Med 44:187–191.

Blum, S, EW Arp, AH Smith, and HA Tyroler. 1979. Stomach cancer among rubber workers: An epidemiologic investigation. In Dusts and Disease. Park Forest, IL: SOEH, Pathotox Publishers.

Checkoway, H, AH Smith, AJ McMichael, FS Jones, RR Monson, and HA Tyroler. 1981. A case-control study of bladder cancer in the U.S. tire industry. Br J Ind Med 38:240–246.

Checkoway, H, T Wilcosky, P Wolf, and H Tyroler. 1984. An evaluation of the associations of leukemia and rubber industry solvent exposures. Am J Ind Med 5:239–249.

Delzell, E and RR Monson. 1981a. Mortality among rubber workers. III. Cause-specific mortality 1940–1978. J Occup Med 23:677–684.

—. 1981b. Mortality among rubber workers. IV. General mortality patterns. J Occup Med 23:850–856.

Delzell, E, D Andjelkovich, and HA Tyroler. 1982. A case-control study of employment experience and lung cancer among rubber workers. Am J Ind Med 3:393–404.

Delzell, E, N Sathiakumar, M Hovinga, M Macaluso, J Julian, R Larson, P Cole, and DCF Muir. 1996. A follow-up study of synthetic rubber workers. Toxicology 113:182–189.

Fajen, J, RA Lunsford, and DR Roberts. 1993. Industrial exposure to 1,3-butadiene in monomer, polymer and end-user industries. In Butadiene and Styrene: Assessment of Health Hazards, edited by M Sorsa, K Peltonen, H Vainio and K Hemminki. Lyon: IARC Scientific Publications.

Fine, LJ and JM Peters. 1976a. Respiratory morbidity in rubber workers. I. Prevalence of respiratory symptoms and disease in curing workers. Arch Environ Health 31:5–9.

—. 1976b. Respiratory morbidity in rubber workers. II. Pulmonary function in curing workers. Arch Environ Health 31:10–14.

—. 1976c. Studies of respiratory morbidity in rubber workers. III. Respiratory morbidity in processing workers. Arch Environ Health 31:136–140.

Fine, LJ, JM Peters, WA Burgess, and LJ DiBerardinis. 1976. Studies of respiratory morbidity in rubber workers. IV. Respiratory morbidity in talc workers. Arch Environ Health 31:195–200.

Fox, AJ and PF Collier. 1976. A survey of occupational cancer in the rubber and cablemaking industries: Analysis of deaths occurring in 1972–74. Br J Ind Med 33:249–264.

Fox, AJ, DC Lindars, and R Owen. 1974. A survey of occupational cancer in the rubber and cablemaking industries: Results of a five-year analysis, 1967–71. Br J Ind Med 31:140–151.

Gamble, JF and R Spirtas. 1976. Job classification and utilization of complete work histories in occupational epidemiology. J Occup Med 18:399–404.

Goldsmith, D, AH Smith, and AJ McMichael. 1980. A case-control study of prostate cancer within a cohort of rubber and tire workers. J Occup Med 22:533–541.

Granata, KP and WS Marras. 1993. An EMG-assisted model of loads on the lumbar spine during asymmetric trunk extensions. J Biomech 26:1429–1438.

Greek, BF. 1991. Rubber demand is expected to grow after 1991. C & EN (13 May): 37-54.

Gustavsson, P, C Hogstedt, and B Holmberg. 1986. Mortality and incidence of cancer among Swedish rubber workers. Scand J Work Environ Health 12:538–544.

International Agency for Research on Cancer (IARC). 1992. 1,3-Butadiene. In IARC Monographs on the Evaluation of Carcinogenic Risks to Humans: Occupational Exposures to Mists and Vapours from Strong Inorganic Acids and Other Industrial Chemicals. Lyon: IARC.

International Institute of Synthetic Rubber Producers. 1994. Worldwide Rubber Statistics. Houston, TX: International Institute of Synthetic Rubber Producers.

Kilpikari, I. 1982. Mortality among male rubber workers in Finland. Arch Environ Health 37:295–299.

Kilpikari, I, E Pukkala, M Lehtonen, and M Hakama. 1982. Cancer incidence among Finnish rubber workers. Int Arch Occup Environ Health 51:65–71.

Lednar, WM, HA Tyroler, AJ McMichael, and CM Shy. 1977. The occupational determinants of chronic disabling pulmonary disease in rubber workers. J Occup Med 19:263–268.

Marras, WS and CM Sommerich. 1991. A three dimensional motion model of loads on the lumbar spine, Part I: Model structure. Hum Factors 33:123–137.

Marras, WS, SA Lavender, S Leurgans, S Rajulu, WG Allread, F Fathallah, and SA Ferguson. 1993. The role of dynamic three dimensional trunk motion in occupationally-related low back disorders: The effects of workplace factors, trunk position and trunk motion characteristics on injury. Spine 18:617–628.

Marras, WS, SA Lavender, S Leurgans, F Fathallah, WG Allread, SA Ferguson, and S Rajulu. 1995. Biomechanical risk factors for occupationally related low back disorder risk. Ergonomics 35:377–410.

McMichael, AJ, DA Andjelkovich, and HA Tyroler. 1976. Cancer mortality among rubber workers: An epidemiologic study. Ann NY Acad Sci 271:125–137.

McMichael, AJ, R Spirtas, and LL Kupper. 1974. An epidemiologic study of mortality within a cohort of rubber workers, 1964–72. J Occup Med 16:458–464.

McMichael, AJ, R Spirtas, LL Kupper, and JF Gamble. 1975. Solvent exposures and leukemia among rubber workers: An epidemiologic study. J Occup Med 17:234–239.

McMichael, AJ, R Spirtas, JF Gamble, and PM Tousey. 1976a. Mortality among rubber workers: Relationship to specific jobs. J Occup Med 18:178–185.

McMichael, AJ, WS Gerber, JF Gamble, and WM Lednar. 1976b. Chronic respiratory symptoms and job type within the rubber industry. J Occup Med 18:611–617.

Monson, RR and KK Nakano. 1976a. Mortality among rubber workers. I. White male union employees in Akron, Ohio. Am J Epidemiol 103:284–296.

—. 1976b. Mortality among rubber workers. II. Other employees. Am J Epidemiol 103:297–303.

Monson, RR and LJ Fine. 1978. Cancer mortality and morbidity among rubber workers. J Natl Cancer Inst 61:1047–1053.

National Fire Protection Association (NFPA). 1995. Standard for Ovens and Furnaces. NFPA 86. Quincy, MA: NFPA.

National Joint Industrial Council for the Rubber Manufacturing Industry. 1959. Running Nip Accidents. London: National Joint Industrial Council for the Rubber Manufacturing Industry.

—.1967. Safe Working of Calenders. London: National Joint Industrial Council for the Rubber Manufacturing Industry.

Negri, E, G Piolatto, E Pira, A Decarli, J Kaldor, and C LaVecchia. 1989. Cancer mortality in a northern Italian cohort of rubber workers. Br J Ind Med 46:624–628.

Norseth, T, A Anderson, and J Giltvedt. 1983. Cancer incidence in the rubber industry in Norway. Scand J Work Environ Health 9:69–71.

Nutt, A. 1976. Measurement of some potentially hazardous materials in the atmosphere of rubber factories. Environ Health Persp 17:117–123.

Parkes, HG, CA Veys, JAH Waterhouse, and A Peters. 1982. Cancer mortality in the British rubber industry. Br J Ind Med 39:209–220.

Peters, JM, RR Monson, WA Burgess, and LJ Fine. 1976. Occupational disease in the rubber industry. Environ Health Persp 17:31–34.

Solionova, LG and VB Smulevich. 1991. Mortality and cancer incidence in a cohort of rubber workers in Moscow. Scand J Work Environ Health 19:96–101.

Sorahan, R, HG Parkes, CA Veys, and JAH Waterhouse. 1986. Cancer mortality in the British rubber industry 1946–80. Br J Ind Med 43:363–373.

Sorahan, R, HG Parkes, CA Veys, JAH Waterhouse, JK Straughan, and A Nutt. 1989. Mortality in the British rubber industry 1946–85. Br J Ind Med 46:1–11.

Szeszenia-Daborowaska, N, U Wilezynska, T Kaczmarek, and W Szymezak. 1991. Cancer mortality among male workers in the Polish rubber industry. Polish Journal of Occupational Medicine and Environmental Health 4:149–157.

Van Ert, MD, EW Arp, RL Harris, MJ Symons, and TM Williams. 1980. Worker exposures to chemical agents in the manufacture of rubber tires: Solvent vapor studies. Am Ind Hyg Assoc J 41:212–219.

Wang, HW, XJ You, YH Qu, WF Wang, DA Wang, YM Long, and JA Ni. 1984. Investigation of cancer epidemiology and study of carcinogenic agents in the Shanghai rubber industry. Cancer Res 44:3101–3105.

Weiland, SK, KA Mundt, U Keil, B Kraemer, T Birk, M Person, AM Bucher, K Straif, J Schumann, and L Chambless. 1996. Cancer mortality among workers in the German rubber industry. Occup Environ Med 53:289–298.

Williams, TM, RL Harris, EW Arp, MJ Symons, and MD Van Ert. 1980. Worker exposure to chemical agents in the manufacture of rubber tires and tubes: Particulates. Am Ind Hyg Assoc J 41:204–211.

Wolf, PH, D Andjelkovich, A Smith, and H Tyroler. 1981. A case-control study of leukemia in the U.S. rubber industry. J Occup Med 23:103–108.

Zhang, ZF, SZ Yu, WX Li, and BCK Choi. 1989. Smoking, occupational exposure to rubber and lung cancer. Br J Ind Med 46:12–15.