Survey
* Your assessment is very important for improving the workof artificial intelligence, which forms the content of this project
* Your assessment is very important for improving the workof artificial intelligence, which forms the content of this project
The health of the workers in a rapidly developing country: effects of occupational exposure to noise and heat J. Gomes*, O. Lloyd† and N. Norman† *Department of Community Health & Epidemiology and Centre for Agricultural Medicine, University of Saskatchewan, Saskatoon, Canada; and †Department of Community Medicine, Faculty of Medicine & Health Sciences, UAE University, United Arab Emirates Occupational hygiene and safety have not been high on the agenda of industrial management in developing countries for a variety of reasons. This cross-sectional study was undertaken to assess the exposure to noise and heat, and to study the level of occupational hygiene practiced, at a foundry in a rapidly developing country (Dubai, United Arab Emirates). Audiometry, muscle cramps and visual acuity were measured in workers at a foundry and compared with the results from workers at a soft-drink bottling plant. Thermal stress, relative humidity, ventilation, illumination and noise levels were measured at different work units at the foundry and at the soft-drink bottling factory. Thermal stress index was high while relative humidity and ventilation were low at the foundry compared with the bottling plant. Noise levels were also high at the foundry, exceeding 90 dB at almost all work units except the fabrication workshop. Mild or moderate visual defects were observed among 31% of foundry workers, compared with 19% of the bottling plant workers. Muscle cramps were reported by 30% of all workers at the foundry, compared with 5% at the bottling plant. Visual disability was the highest among furnace operators and fabricators. Mean hearing disability was 8.69 ± 1.08% among foundry workers, compared with 4.56 ± 0.82% among bottling plant workers. The high thermal stress, noise levels and exposure to non-ionizing radiations at the foundry might have contributed to the higher frequency of muscle cramps and the greater hearing and visual disabilities, respectively, among these workers. Non-use of personal protective equipment and poor occupational hygiene and safety measures were also seen to affect eye and ear health adversely among the workers at the foundry. Key words: Foundry; hearing disability; muscle cramps; noise; thermal stress; ventilation; visual disability. Received 28 June 2001; revised 4 February 2002; accepted 11 March 2002 Introduction In many rapidly developing countries, where labour is cheap, proper occupational hygiene and pollution control methods are often neglected at worksites. Protective equipment for factory workers is considered a luxury, and is hence not provided. The workers, being economic Correspondence to: J. Gomes, Department of Community Health & Epidemiology and Centre for Agricultural Medicine, University of Saskatchewan, 103 Hospital Drive, Saskatoon, Saskatchewan S7N 0W8, Canada. e-mail: [email protected] migrants, accept adverse conditions as part of the job, and do not demand hygiene measures and personal protective equipment. As a result, workers in these countries tend to be exposed to excessive amounts of both physical and chemical pollutants. Foundry workers, in particular, are routinely exposed to dust, gases, fumes and heat, amongst other pollutants [1]. The level of exposure to these pollutants depends on many factors, chief amongst them in this context being the level of occupational hygiene and pollution control methods employed in the factory. Reductions in the exposure levels could be Occup. Med. Vol. 52 No. 3, pp. 121–128, 2002 Copyright © Society of Occupational Medicine. Printed in Great Britain. All rights reserved. 0962-7480/02 122 Occup. Med. Vol. 52, 2002 brought about, primarily, by implementing appropriate measures to control chemical and physical pollutants in the work environment, and secondarily, by providing personal protective equipment to the exposed workers. We have previously reported that the level of occupational hygiene is low and that pollution control methods are poorly implemented at the foundry under study (in Dubai, United Arab Emirates) [1]. We found impaired pulmonary function among workers exposed to dusts, fumes and gases, with the risks exacerbated through the failure to use personal protective equipment [1]. Safety and occupational hygiene practices in newly industrializing countries such as the Arabian Gulf States are largely ignored, resulting in increased exposures to unsuspecting and needy economic migrants working in these countries. Pulmonary function impairment has been described as one of the major adverse health effects in steel factory workers [2, 3]. Noise-induced hearing loss has also been reported in steel workers [4] and metal fabrication workers [5]. Other investigators have reported on the mortality from injuries among steel workers [6], and on the cancer incidence and mortality in them [7–9]. Most of these studies have been in rapidly developing countries, where occupational hygiene and the use of personal protective equipment have not been given the attention they deserve. Moreover, the use of personal protection is often ignored in tropical countries because of the hot and humid climatic conditions, which make the use of these devices impractical. However, the broader spectrum of chronic health problems resulting from exposure to heat, dust, gases and fumes at iron and steel factories in developing countries has not been systematically described. The semi-skilled and unskilled workers from the lesserdeveloped countries who work in these rapidly developing countries are contract workers, and are usually untrained in the job they are employed to do. Being mostly economically underprivileged and anxious to retain their jobs, the workers accept adverse working conditions and do not demand health and safety measures. Therefore, this study was designed to assess the practice of occupational hygiene and safety at the worksite, and to investigate adverse health effects among foundry workers in a rapidly developing country in a desert environment. The problems of noise, heat, ventilation and hygiene at various worksites were assessed. The practice of occupational hygiene, the implementation of control measures and the use of personal protection were also evaluated, together with their associations with the degree of health impairment. Thermal stress, muscle cramps, and visual and hearing disabilities were also examined. Methods Those workers involved in the production process (exposed) at the foundry were invited to participate in the study; all agreed to participate, and so all were included. As an unexposed group, all workers working at a softdrink bottling plant were also invited to participate in the study, and all were included since none refused to participate. Only those workers on annual or other leave during the period of the study did not participate. The management of the factories provided a list of workers, their job titles and their ages, along with the layout of different work units within the factory. Having made prior arrangements with the management of the factory, an appointment was made with the production supervisors to conduct the study on specified days during the study period. The exposed workers worked in shifts round the clock, while the unexposed workers worked only on the general shift. The supervisors requested those workers who had been off duty for at least the past 8 h to report to the site laboratory before beginning their shift, to participate in the study. At the site laboratory, the procedures to be applied were explained to the workers, and their willingness to participate in the study was confirmed by their signing the consent form. The Ethical Committee of the Medical Faculty had earlier given ethical clearance for the procedures to be applied in the study, including the use of a questionnaire. A specifically designed questionnaire was used to collect information on socio-demographic characteristics, general health profile, current medication, use of personal protective equipment at work, water consumption through the day and intake of salt tablets. The questionnaire was used for both the exposed and the unexposed workers, even though there were differences in the working conditions and the need to use personal protective equipment while at work. Since all the workers were of Asian origin and some were unable to converse in English, the questionnaires were applied to all the participants through an interviewer, in their local language (Urdu). Prior to using the questionnaire in their local language, the questionnaire was back-translated twice into Urdu and pilot tested. The comparability of demographic characteristics between the foundry and bottling plant workers has been described elsewhere [1]. Height and weight were measured at the site laboratory for all workers participating in the study. The body mass index (BMI) was calculated as the ratio of weight (in kilograms) to height (in metres) squared. The mean ages and BMIs of the workers at the foundry and those at the bottling plant were similar [1]. Visual acuity was measured, using Snellen’s chart, for all the exposed and unexposed workers participating in the study. A score of 6/6 on Snellen’s chart was considered as normal vision, 6/9 as mild defect and 6/12 or greater as moderate-to-severe defect. Visual acuity was measured in each eye separately, and an average of the left and the right eye was used to represent a value for both J. Gomes et al.: Worker health in a rapidly developing country eyes. Audiometric tests were conducted using a clinical/ diagnostic audiometer, Midimate 622 (GN Otometrics A/S, Taastrup, Denmark), for all the exposed and unexposed workers participating in the study. The mean values of the left and the right ear audiometric profiles of the group of workers, identified by job title and performing similar tasks, were compared with the mean values for other groups. Sound pressure levels and octave band frequency analyses in the foundry and the bottling plant affecting the workers as they performed the various tasks at the different worksites were correlated with the workers’ audiometric profiles. Measurements for noise levels, dry and wet bulb temperatures, air speed, illumination and humidity were taken during the normal operation and on a normal working day at the foundry and the bottling plant. These measurements were taken at all sites usually manned by workers, both at the foundry and at the bottling plant. The wet bulb globe temperature (WBGT) index was recorded as a measure of thermal index as reported by a Thermal Stress Monitor (Questemp, Audiometrics, Inc., LA, USA). Relative humidity was measured using a whirling hygrometer (Cassella Ltd, London, UK). Air speed was measured using an air vane (Wheaton Inc., NJ, USA) and illumination was measured using a lux meter (Wheaton Inc., NJ, USA). Noise frequency measurements were made using a Precision Sound Level Meter Type 2232 (Bruel & Kjaer, Huddinge, Sweden). All the measurements at both sites were taken at the end of the summer season (September/October), when the ambient environmental temperatures were between 35 and 45°C. Hearing disability was assessed for the workers at the iron foundry and those at the bottling plant according to the method described by the American Medical Association/American Academy of Otolaryngology Formula (AMA/AAO) for the determination of hearing disability [10–12]. Hearing disability was also calculated for comparison according to the British Association of Otolaryngologists (BAOL)/British Society of Audiologists (BSA) method [13]. The workers at the foundry (the exposed group) 123 were assigned to different work units within the foundry. These tasks within the assigned work units were rotated approximately every 2 years within the unit. At the soft-drink bottling plant, the workers (the unexposed group) attended to the automatic bottling tasks at the factory or were dispatched to supply the finished products to the retailers. Since these tasks were switched between workers on a daily basis, no categorization of tasks was carried out for them. Means and SDs were used to characterize the different parameters for thermal stress, ventilation and illumination, and geometric means and SEs were used for octave band frequency analyses and sound pressure levels; frequencies and percentages were used to describe water consumption, muscle cramps and use of protective equipment while at work. The χ2 test was used to compare frequencies for visual acuity, water consumption and muscle cramps. An independent sample t-test was used to compare thermal stress, ventilation, illumination and noise levels at the foundry and the bottling plant. Visual and hearing disabilities were estimated using the factorial multivariate regression analysis general linear model from Statistical Package for Social Sciences (SPSS) [14]. General linear model analysis was used to estimate the visual and hearing disability values for the exposed and unexposed workers, with age and BMI as covariates in the model. Results The Thermal Stress Monitor only displayed the dry bulb (DB) and wet bulb (WB) temperatures, and the WBGT index for indoors (WBGTin index) (Table 1). The DB temperature ranged between 32.6 and 36.5°C, the WB between 25.7 and 27.3°C. The WBGTin index was calculated by the equation WBGTin = 0.71Twb + 0.3Tg where Tg is globe temperature and Twb is wet bulb temperature. The mean ambient WBGTin at all work Table 1. Thermal stress, relative humidity, air speed and illumination at different work units in the iron foundry (values are mean ± SD) Work unit DB (°C) Furnace Continuous casting Rolling mill Mechanical workshop Fabrication workshop 36.50 35.81 36.22 32.64 36.05 ± 1.80 ± 2.20 ± 2.15 ± 2.98 ± 2.88 Foundry mean Bottling plant mean 35.64 ± 2.08* 31.59 ± 1.93* WB (°C) WBGT 26.22 ± 1.37 25.77 ± 1.37 27.28 ± 0.58 25.95 ± 0.81 27.10 ± 0.90 32.00 32.50 31.89 29.39 31.54 ± 3.58 ± 3.94 ± 0.72 ± 1.02 ± 1.39 26.42 ± 1.70* 25.22 ± 1.81* 32.47 ± 2.09* 25.74 ± 2.25* RH (%) Air speed (m/s) Illumination (lx) 43.38 ± 4.29 42.92 ± 2.66 51.20 ± 10.03 58.00 ± 8.48 50.17 ± 9.51 0.80 ± 0.53 0.10 ± 0.16 0.73 ± 0.57 1.19 ± 0.83 0.67 ± 0.34 221.00 ± 211.00 58.46 ± 43.17 113.00 ± 41.34 93.20 ± 48.71 96.00 ± 45.79 48.03 ± 5.78* 63.45 ± 5.25* 0.62 ± 0.42* 0.91 ± 0.30* 114.90 ± 84.41 105.61 ± 33.50 DB, dry bulb temperature; WB, wet bulb temperature; WBGT, wet bulb globe temperature index; RH, relative humidity. *P < 0.0001 (independent sample t-test). 124 Occup. Med. Vol. 52, 2002 both eyes were seen in 22% of furnace workers and 29% of fabrication workshop workers (Table 3). A significantly (P < 0.01) higher percentage (15%) of foundry workers had mild visual defects and 16% had moderate-to-severe visual defects in both eyes, compared with 11 and 9%, respectively, among the bottling plant workers. Having acclimatized to the working conditions of the foundry, the consumption of water among foundry workers averaged 3–4 l during a working shift. No intake of salt tablets was reported by any of the furnace or bottling plant workers. Muscle cramps were reported by ~30% of the steel foundry workers, compared with 5% of the bottling plant workers (Table 4). Among the foundry workers, muscle cramps were reported by most of the furnace (43%) and the continuous casting unit (31%) workers. The majority (63%) of the workers at the iron foundry consumed ≤3 l of water, with fewer (37%) workers consuming >3 l of water per day on a normal working day (Table 4). Among the foundry workers, 35% of those units at the foundry was >27.5°C [the threshold limit value (TLV) for 75% work and 25% rest] [15]. The mean WBGTin index for the foundry was significantly (P < 0.0001) higher than the mean WBGTin index for the bottling plant. Relative humidity ranged between 43 and 58%, and the air speed between 0.1 and 1.19 m/s, in the different areas of the foundry. The mean relative humidity and the air speed in the iron foundry were significantly (P < 0.0001) lower than the corresponding mean values at the bottling plant. Natural or electric illumination was generally lower at the iron foundry compared with the bottling plant. Furnace flames or molten metal contributed to a higher radiance at certain locations within the foundry. The sound pressure levels were >85 dB (the TLV for 8 h exposure) [15] in all the units of the foundry, being highest (100 dB) in the casting area (Table 2). The mean (92.7 ± 0.9) sound pressure level at the foundry was significantly (P < 0.01) higher than that (77.6 ± 0.6) at the bottling plant. Moderate-to-severe eye defects in Table 2. Octave band frequency analyses and sound pressure levels at different worksites within the foundry and at the bottling plant (geometric means ± SE of the means are reported for the octave bands and dB) Work unit Furnace unit 31.5 Hz (dB) 63 Hz (dB) 125 Hz (dB) 250 Hz (dB) 500 Hz (dB) 1000 Hz (dB) 2000 Hz (dB) 4000 Hz (dB) 8000 Hz (dB) 16 000 Hz (dB) SPL (dB) 54.7 64.3 77.0 87.8 94.6 90.1 83.9 82.3 72.4 63.4 96.9 ± 1.2 ± 0.9 ± 0.9 ± 0.9 ± 1.2 ± 1.2 ± 1.2 ± 1.3 ± 1.4 ± 1.1 ± 1.0 Continuous casting unit Rolling mill unit 57.3 ± 1.8 65.7 ± 1.8 76.9 ± 2.0 86.0 ± 2.2 94.6 ± 2.7 92.5 ± 2.5 87.6 ± 2.2 85.1 ± 2.2 77.3 ± 1.2 66.7 ± 1.7 100.4 ± 3.0 48.4 ± 1.9 58.8 ± 1.5 70.4 ± 1.4 81.4 ± 1.3 89.5 ± 1.9 85.7 ± 0.9 83.9 ± 0.8 82.3 ± 0.7 78.1 ± 1.8 64.4 ± 1.9 93.2 ± 0.9 Mechanical workshop Fabrication workshop Foundry mean Bottling plant mean 44.9 56.3 68.2 79.1 86.9 81.4 80.2 78.1 71.7 59.4 89.8 48.7 ± 0.9 58.7 ± 1.1 68.9 ± 1.1 76.1 ± 1.5 83.6 ± 1.4 80.9 ± 1.3 75.9 ± 1.1 72.2 ± 1.6 65.1 ± 1.6 53.0 ± 2.4 86.1 ± 1.3 50.9 ± 0.7 60.9 ± 0.6* 72.5 ± 0.7* 81.9 ± 0.8** 89.8 ± 0.9** 86.0 ± 0.8** 81.5 ± 0.7** 79.0 ± 0.9** 71.4 ± 0.9** 60.0 ± 0.9** 92.7 ± 0.9** 50.2 ± 0.2 58.9 ± 0.3 70.6 ± 0.2 71.3 ± 0.2 70.4 ± 0.4 67.9 ± 0.3 64.9 ± 0.3 61.1 ± 0.4 57.8 ± 0.4 53.3 ± 0.3 77.6 ± 0.6 ± 0.2 ± 1.1 ± 0.7 ± 1.3 ± 0.9 ± 0.8 ± 1.9 ± 2.4 ± 2.7 ± 3.3 ± 1.9 ANOVA (analysis of variance, means procedure): *P < 0.001; **P < 0.0001. Table 3. Snellen’s vision test for workers in the different units of the iron foundry and the bottling plant [values are n (%)] Normal vision Mild defect Right eye Both eyes Left eye Moderate-to-severe Job categories Left eye Right eye Both eyes Left eye Furnace operators (n = 27) Casting workers (n = 10) Rolling mill operators (n = 10) Machinists (n = 9) Fabricators (n = 14) General workers (n = 11) 13 (48) 7 (70) 7 (70) 6 (67) 7 (50) 9 (82) 13 (48) 8 (80) 7 (70) 4 (44) 5 (36) 9 (82) 15 (56) 9 (90) 7 (70) 7 (78) 8 (57) 10 (91) 6 (22) 2 (20) 1 (10) 2 (22) 3 (21) 2 (18) 7 (26) 1 (10) 2 (20) 4 (44) 5 (36) 2 (18) 6 (22) 0 2 (20) 1 (11) 2 (14) 1 (9) 8 (30) 1 (10) 2 (20) 1 (11) 4 (29) 0 7 (26) 1 (10) 1 (10) 1 (11) 4 (29) 0 6 (22) 1 (10) 1 (10) 1 (11) 4 (29) 0 Foundry mean (n = 81) Bottling plant mean (n = 113) 49 (61)* 81 (72) 46 (57)* 76 (67) 56 (69)* 91 (81) 16 (20) 25 (22) 21 (26) 26 (23) 12 (15) 12 (11) 16 (20)* 7 (6) 14 (17)* 11 (10) 13 (16)* 10 (9) Normal vision, 6/6 on Snellen’s chart; mild defect, 6/9 on Snellen’s chart; moderate-to-severe defect, 6/>12 on Snellen’s chart. *P < 0.01 (χ2 test). Right eye Both eyes J. Gomes et al.: Worker health in a rapidly developing country 125 Table 4. Water intake and frequency of muscle cramps among iron foundry workers at different work units [values are n (%)] Water consumption Muscle cramps ≤3 l >3 l ≤3 l >3 l All workers Furnace operators (n = 27) Casting workers (n = 10) Rolling mill operators (n = 10) Machinists (n = 9) Fabricators (n = 14) General workers (n = 11) 17 (81) 5 (39) 5 (50) 6 (60) 10 (83) 8 (53) 4 (19) 8 (62) 5 (50) 4 (40) 2 (17) 7 (47) 8 (47) 1 (20) 1 (20) 2 (33) 3 (33) 3 (38) 1 (25) 3 (38) 1 (20) – – 1 (14) 9 (43) 4 (31) 2 (20) 2 (20) 3 (25) 4 (27) Foundry mean (n = 81) Bottling plant mean (n = 113) 51 (63)* 86 (76)* 30 (37)* 27 (24)* 18 (35)** 4 (5)** Job categories 6 (20)** 2 (7)** 24 (30)** 6 (5)** *P < 0.05 (χ2 test). **P < 0.001 (χ2 test). Table 5. Use of protective equipment by the workers at the iron foundry [values are n (%)] Protective equipment Overalls Shoes Helmet Ear muffs/plugs Goggles Face mask Gloves F (n = 27) CC (n = 10) RM (n = 10) MW (n = 9) FW (n = 14) Gen (n = 11) All workers (n = 81) 0 (0) 21 (100) 19 (91) 0 (0) 21 (100) 19 (95) 20 (95) 0 (0) 12 (92) 10 (77) 0 (0) 11 (85) 9 (69) 12 (92) 0 (0) 10 (100) 5 (50) 0 (0) 8 (80) 4 (40) 8 (80) 0 (0) 9 (90) 6 (60) 0 (0) 8 (80) 6 (60) 9 (90) 0 (0) 12 (100) 7 (58) 0 (0) 12 (100) 7 (58) 11 (92) 0 (0) 13 (87) 6 (40) 0 (0) 10 (67) 7 (47) 13 (87) 0 (0) 77 (95) 53 (65) 0 (0) 70 (86) 52 (42) 73 (90) F, furnace operators; CC, casting workers; RM, rolling mill operators; MW, machinists; FW, fabricators; Gen, general workers. consuming ≤3 l of water reported experiencing muscle cramps, compared with 5% of the bottling plant workers; this difference was statistically significant (Table 4). The figures of 20 and 7%, respectively, for cramp sufferers among those consuming >3 l of water in the two occupational groups also differed highly significantly. Overall, the frequencies of muscle cramps reported by the foundry workers (30%) and the bottling plant workers (5%) differed significantly (Table 4). The use of overalls, shoes, helmet, earmuffs or plugs, safety glasses, face mask and gloves as measures of personal protection was variable (Table 5). Overalls and earmuffs or plugs were never used by any of the workers at the iron foundry, though required. Shoes (95%), gloves (90%) and safety glasses (86%) were used by most of the workers, whereas helmets (65%) and face masks (64%) were used less frequently (Table 5). The estimated visual impairment using factorial general linear model multivariate analysis for the exposed workers was significantly higher compared with that for the unexposed workers (Table 6). When visual disability was estimated with age and BMI as covariates, furnace and fabrication workers at the foundry were observed to have a significantly higher visual disability compared with the other workers (Table 6). Regression analyses identified jobs at the furnace and fabrication workshops as significant predictors of visual disability in both eyes. The mean estimated hearing disability (estimated by both the AMA and the BAOL methods) for the foundry workers (8.59 ± 1.08%) was significantly (P = 0.005) higher compared with that for the workers at the bottling plant (4.63 ± 0.91%) (Table 7). Rolling mill workers and those from the fabrication and mechanical workshops were observed to have a significantly higher estimated hearing disability compared with other workers at the foundry. Regression analyses also identified the jobs of fabricator (P = 0.02) and rolling mill operator (P = 0.05) as significant predictors of hearing disability among foundry workers, while working as a machinist (P = 0.07) was not. Discussion and conclusions Occupational exposures to heat and noise are unavoidable in the metal production and casting industries, but these exposures could be minimized through efficient control measures at the worksite and/or the proper use of appropriate personal protective equipment. However, in rapidly developing countries, personal protective equipment and exposure control measures are rarely used at many worksites, and are given little importance and preference by many employers. This neglect may be due to the fact that the workers in rapidly developing countries 126 Occup. Med. Vol. 52, 2002 Table 6. Estimated visual disability using factorial general linear model multivariate analysis for the exposed (different job categories) and unexposed workers Job categories Furnace operators (n = 27) Casting (n = 10) Rolling mill operators (n = 10) Machinists (n = 9) Fabricators (n = 14) General workers (n = 11) Foundry mean (n = 81) Bottling plant mean (n = 113) a Eye Visual disability (mean ± SE) 95% CIa for mean Estimated with covariates at Left Right Both Left Right Both Left Right Both Left Right Both Left Right Both Left Right Both 9.57 ± 0.94 9.29 ± 0.96 9.43 ± 0.91 7.85 ± 1.01 8.08 ± 1.03 7.96 ± 1.00 8.40 ± 1.19 8.70 ± 1.80 8.55 ± 1.43 8.10 ± 1.86 9.00 ± 1.92 8.55 ± 1.86 10.00 ± 1.32 12.10 ± 1.66 11.00 ± 1.46 6.60 ± 0.34 6.60 ± 0.33 6.60 ± 0.29 7.6, 11.6 7.3, 11.3 7.5, 11.3 5.7, 10.4 5.6, 10.1 5.7, 10.2 5.5, 11.3 5.6, 10.1 5.2, 11.9 3.7, 12.5 4.4, 13.5 4.2, 12.9 7.0, 12.9 8.3, 15.7 7.7, 14.3 5.9, 7.3 5.9, 7.3 5.9, 7.3 Age = 42.4; BMI = 25.1 Left Right Both Left Right Both 8.52 ± 0.45* 8.85 ± 0.52 8.69 ± 0.47 7.35 ± 0.28 7.96 ± 0.38 7.66 ± 0.32 7.6, 7.8, 7.7, 6.8, 7.2, 7.0, 9.4 9.8 9.6 7.9 8.7 8.3 Age = 38.7; BMI = 26.4 Age = 40.2; BMI = 24.7 Age = 40.2; BMI = 24.9 Age = 43.1; BMI = 25.9 Age = 38.0; BMI = 25.8 Age = 40.9; BMI = 25.4 Age = 40.7; BMI = 25.6 CI, confidence interval. *Estimated marginal means significantly different at P = 0.05 and 95% CI. Table 7. Estimated hearing disability using factorial general linear model multivariate analysis for the exposed (different job categories) and unexposed workers Hearing disabilitya (mean ± SE) Furnace operators (n = 27) Casting workers (n = 10) Rolling mill operators (n = 10) Machinists (n = 9) Fabricators (n = 14) General workers (n = 11) Foundry mean (n = 81) Bottling plant mean (n = 113) Job categories 95% CI for mean Hearing disabilityb (mean ± SE) 95% CI for mean Estimated with covariates at 7.37 ± 1.88 8.38 ± 3.09 10.93 ± 3.07 10.65 ± 3.24 11.28 ± 2.61 4.56 ± 2.95 3.66 2.29 4.86 4.26 6.14 –1.20 11.07 14.47 16.99 17.04 16.42 10.37 9.84 ± 1.98 10.99 ± 3.26 14.34 ± 3.25 14.08 ± 3.15 13.83 ± 2.75 9.54 ± 3.11 5.93 4.57 7.94 7.33 8.39 3.40 8.59 ± 1.08 4.62 ± 0.91 6.46 2.83 10.71* 6.42 11.66 ± 1.13 7.13 ± 0.96 9.42 5.24 a Hearing impairment (handicap) was calculated according to the method described in the AMA/AAO formula for the determination of hearing handicap [10]. b Hearing impairment (handicap) was calculated according to the method described in the BAOL/BSA formula for the determination of hearing handicap [10]. *ANOVA, P < 0.0001. are economic migrants from other developing countries, who accept occupational exposures as part of the job. The hot and humid climatic conditions further dissuade the workers from using personal protective equipment, even when provided. As in other studies, in the UAE, overalls, earmuffs, face masks and helmets were either not used or were used by only a few workers [16]. Unlike their counterparts in developed countries, these industries in these rapidly developing countries do not implement any control measures to minimize exposures at workplaces. Non-use of personal protection may have contributed to the increased exposure to non-ionizing radiation and noise, and thereby increased visual and hearing disability among those most exposed. The results of the thermal survey (WBGTin index) indicated a high prevalence of thermal stress throughout J. Gomes et al.: Worker health in a rapidly developing country the foundry. The low ambient air speed values at the foundry indicated the absence of any artificial ventilation. Muscle cramps usually occur among those who work in hot environments, and are even higher among those who drink large amounts of water without salt tablets [17]. In this study, we found that muscle cramps were experienced by a higher percentage of foundry workers, who had a higher heat load than the unexposed group; by contrast, the percentage of those consuming >3 l of water who were observed to experience muscle cramps was less than that of those consuming ≤3 l of water. In our study, the foundry workers experienced indoor working conditions with much lower heat than the workers in the study by Awahl et al. [17], who worked outdoors with a higher heat load and consumed more water; this dissimilarity could explain the differences in muscle cramps and water consumption in these two sets of workers. Cool water fountains and rest areas were not available to the workers on-site. The non-use of goggles or other eye protection devices may have affected the vision of the workers. Only 69% of the workers at the foundry were observed to have normal vision in both eyes, compared with 81% of the workers at the bottling plant, although the mean ages for the two groups were similar. The 31% of workers at the foundry with eye defects consisted of 15% with a mild defect and 16% with a moderate-to-severe defect. Exposure to IR radiation from the furnace and the molten metal is capable of causing injuries to the cornea, iris, retina and lens of the eye [18]. Ocular damage can result from incident energy on the cornea at a density of 4–8 Ws/cm2, which is typical of the energy emitted by furnace flames and molten metal [18, 19]. Unprotected exposure to radiation from the furnace and molten metal could be well over the maximum permissible dose (0.4–0.8 Ws/cm2) from incandescent sources [18]. The estimated visual disability was higher for workers from the foundry compared with the bottling plant workers. The workers at the fabrication workshop and furnace area were estimated to have an even greater visual disability. A dose–response effect seemed to be apparent among workers at the foundry, with higher percentages of workers from fabrication workshops and furnace areas being diagnosed with moderate-to-severe defect. Although goggles were provided, fabrication workshop workers seldom used them during welding, and furnace workers were observed using goggles only infrequently during potting, testing and casting the molten metal. Thermal screens were not seen at many of the likely locations in the foundry, and thermal overalls were not made available to the workers on-site. Although the overall mean noise level at the foundry was >85 dB in almost all working areas, none of the workers used earmuffs or plugs, or even a helmet with ear protection. The average length of the workday during the 127 general work shift was 10–12 h, depending on the production targets. In addition, some of the workers worked overtime. The workers therefore exceeded the TLV [15], and this may have reflected on the hearing disability observed among these workers. The higher estimated mean hearing disability value for the workers at the foundry (8.69 ± 1.08%) compared with that for the workers at the bottling plant (4.56 ± 0.82%) indicated greater exposure to occupational noise among the former group. Noise exposure at the furnace and the casting areas was intermittent, as higher levels of noise were emitted only during the charging, potting and casting processes. In contrast, noise emissions from the rolling mill and the mechanical and fabrication workshops were continuous. The noise exposure of these workers may have been greater because the sound pressure levels for these areas in the foundry for frequencies between 250 and 8000 Hz were almost all >70 dB, and these workers were also exposed continuously during each shift. The hearing disability observed among workers from the rolling mill and from the fabrication and mechanical workshops was greater than that among the workers from other areas, these workers being also exposed to higher noise levels. The greater hearing disability among workers exposed to higher ambient noise levels indicates a dose–response relationship between exposure to noise and hearing disability. Similar hearing disability has been reported in other industries in other rapidly developing countries [20]. Noise came from various sources at different locations throughout the foundry, and noise levels exceeded the TLV for noise exposure at all the worksites there. The foundry did not implement noise control measures, nor did it provide noise-free rest areas within the foundry. Even if the workers were provided with some protective equipment, the high ambient heat would have dissuaded them from using it. In conclusion, the workers at the foundry were exposed to higher heat, noise, and UV and IR radiation than were experienced by the comparison workers at the bottling plant. The foundry workers did not use the much-needed personal protection. Vision and hearing problems were more frequent among these foundry workers than those at the bottling plant, where heat, UV and IR radiation, and noise exposures were absent. Muscle cramps were also observed in a higher percentage of the workers at the foundry, who were exposed to thermal stress during the workshift. Workers at the foundry also worked long hours (the average shift length being 12 h). While we recommend that these workers use proper personal protective equipment whilst working on the shop floor, we also suggest that proper equipment appropriate for use in tropical countries be made available to these workers. To protect the workers from excessive exposures to heat, UV and IR radiation, and noise, governmental monitoring agencies need to require that 128 Occup. Med. Vol. 52, 2002 industries implement occupational hygiene and provide personal protective equipment to the exposed workers. Hearing conservation programmes should be introduced, efforts should be made to control noise levels and ear plugs/muffs should be provided to all the exposed workers. Since the majority of the workers are unskilled, governmental agencies should focus on education and training in safe and appropriate working conditions. Programmes aimed at rewarding those workers who use personal protective equipment, when available, should be introduced. Appropriate control measures, such as insulated heat screens, need to be installed to minimize exposure to heat. Noise-insulated and cooled rest areas should also be provided to the workers for use during breaks while on duty. The average length of a normal day workshift should be limited to 8 h and salt tablets should be provided to all the workers in the foundry. Workers exposed to heat, UV and IR radiation, and noise should be regularly monitored for adverse health effects. Acknowledgements The authors wish to thank the management and the workers at the iron foundry where the study was carried out and the Municipality of Dubai for their cooperation and assistance in facilitating this study. The authors also acknowledge the technical assistance of Mr Jamal Cherkonath in collecting the data. This study was supported in part by the Department of Community Medicine, Faculty of Medicine, UAE University. References 1. Gomes J, Lloyd O, Norman J. Dust exposure and impairment of lung function at a small iron foundry in a rapidly developing country. Occup Environ Med 2001; 58: 656–662. 2. Pham QT, Mastrangelo G, Chau N, Haluzzka J. Five year longitudinal comparison of respiratory symptoms and function in steelworkers and unexposed workers. Bull Eur Physiopathol Respir 1979; 15: 469–480. 3. Wang ML, McCabe L, Hankison JL, et al. Longitudinal and cross-sectional analyses of lung function in steelworkers. Am J Respir Crit Care Med 1996; 153: 1907–1913. 4. Tay P. Severe noise-induced deafness: a ten-year review of cases. Singapore Med J 1997; 37: 362–364. 5. Ishii EK, Talbott EO. Race/ethnicity differences in the prevalence of noise-induced hearing loss in a group of metal fabricating workers. J Occup Environ Med 1998; 40: 661–666. 6. Barreto SM, Swedlow AJ, Smith PG, Higgins CD, Andrade A. Mortality from injuries and other causes in a cohort of 21,800 Brazilian steel workers. Occup Environ Med 1996; 53: 343–350. 7. Cao R, Dong D, Dong G. Mortality study of cancer among Anshan iron and steel workers. Chung Hua Chung Liu Tsa Chih Chinese J Oncol 1995; 17: 195–198. 8. Xu Z, Pan GW, Liu LM, et al. Cancer risks among iron and steel workers in Anshan, China, Part I. Proportional mortality ratio analysis. Am J Ind Med 1996; 30: 1–6. 9. Xu Z, Brown LM, Pan GW, Liu TF, et al. Cancer risks among iron and steel workers in Anshan, China, Part II. Case–control studies of lung and stomach cancer. Am J Ind Med 1996; 30: 7–15. 10. Ward WD. The American Medical Association/American Academy of Otolaryngology formula for determination of hearing handicap. Audiology 1983; 22: 313–324. 11. American Academy of Otolaryngology Committee on Hearing and Equilibrium and the American Council of Otolaryngology Committee on the Medical Aspects of Noise. Guide for the Evaluation of Hearing Handicap. J Am Med Assoc 1979; 241: 2055–2059. 12. American Medical Association Committee on Rating of Mental and Physical Impairment. Guides to the Evaluation of Permanent Impairment. Chicago, IL: American Medical Association, 1979. 13. BAOL and BSA. Method for Assessment of Hearing Disability. London: British Association of Orolaryngologists/British Society of Audiology, 1983; 1–18. 14. Norusis MJ. SPSS for Windows, ver 10.0. Base System User’s Guide. Chicago, IL: SPSS Inc., 1993. 15. ACGIH. 2000 TLVs & BEIs. TLVs for Chemical Substances and Physical Agents & Biological Exposure Indices. Cincinnati, OH: American Conference of Governmental Industrial Hygienists. 16. Gomes J, Lloyd OL, Revitt DM. The influence of protective measures, environmental hygiene and exposures to pesticides on the health of immigrant farmworkers in a desert country. Int Arch Occup Environ Health 1999; 72: 40–45. 17. Awahl SH, Norman JN, Brebner JA. Heat cramps in a hot desert work-site. Kuwait Med J 2000; 32: 382–386. 18. Olishifski J, Zenz C. Infrared radiations. In: Zenz C, ed. Occupational Medicine: Principles and Practical Applications. Chicago, IL: Yearbook Medical Publishers, 1988. 19. Miller G. Non-ionizing radiations. In: Plog BA, Niland J, Quinlan PJ, eds. Fundamentals of Industrial Hygiene. Itasca, IL: National Safety Council, 1996; ch. 11. 20. Hernandez-Gaytan SI, Sants-Burgoa C, Becker-Meyer JP, Macias-Carrillo C, Lopez-Cervantes M. Prevalence of hearing loss and correlated factors in cement plant. Salud Publica Mex 2000; 42: 106–111.