|Year : 2006 | Volume
| Issue : 1 | Page : 11-18
Epidemiological surveillance of employees in a mercury thermometer plant: An occupational health study
T Rajgopal1, HV Ravimohan2, P Mascarenhas2
1 Medical and Occupational Health, Hindustan Lever Limited, India
2 Hindustan Lever Limited, India
Medical and Occupational Health, Hindustan Lever Limited
Source of Support: None, Conflict of Interest: None
A cross-sectional epidemiological survey of 255 individuals (130 current permanent employees, 64 contract workers, 55 ex-employees and 6 scrap dealers) coupled with a retrospective cohort study of the occupational health of 290 employees (all permanent employees who ever worked in the factory over a span of 15 years) was conducted in a mercury thermometer plant at Kodaikanal in India. The cross-sectional study done in March 2001 was based on a clinical protocol developed by the US Dept. of Labor, Mines Safety and Health Administration and was supplemented by the analysis of mercury in urine (HgU) through Inductively Coupled Plasma Emission Spectrometry (ICP) and relevant biochemical investigations. Group averages of HgU in this study was 23.8 mg/L and were well within WHO-recommended limits of group means (50 mg/L). Group analysis was supplemented by appropriate individual analysis. The retrospective cohort study (for the years 1988-2001) included clinical evaluation coupled with analysis of biological monitoring done through Cold Vapor Atomic Absorption Spectrometry (CVAAS). Group averages of mercury in urine measured between 12.9 to 31.9 mg/L over the working life of the factory, and they too were supplemented by appropriate individual analysis. The protocol for epidemiological surveillance and indeed for the occupational health surveillance conducted over the life of the factory (biological monitoring, workplace environmental monitoring, shop floor health and safety practices and clinical evaluations) have been independently validated by the Netherlands-based TNO, the All India Institute of Medical Sciences, and the Indian Association of Occupational Health. None of the employees in this factory were found to be suffering from any ill health that could be attributed to Hg exposure.
Keywords: Biological monitoring, cohort, environmental monitoring, epidemiological surveillance, mercury
|How to cite this article:|
Rajgopal T, Ravimohan H V, Mascarenhas P. Epidemiological surveillance of employees in a mercury thermometer plant: An occupational health study. Indian J Occup Environ Med 2006;10:11-8
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Rajgopal T, Ravimohan H V, Mascarenhas P. Epidemiological surveillance of employees in a mercury thermometer plant: An occupational health study. Indian J Occup Environ Med [serial online] 2006 [cited 2020 Apr 9];10:11-8. Available from: http://www.ijoem.com/text.asp?2006/10/1/11/22889
| Introduction|| |
The current study deals with the epidemiological health surveillance of employees in a thermometer plant at Kodaikanal in India. The study combines a cross-sectional epidemiological survey supplemented with a retrospective cohort study and was undertaken to allay apprehension from the local communities in Kodaikanal on the health impact of the factory operations.
The Kodaikanal plant was set up in 1984 by Ponds India Ltd. with equipment from the USA. The unit got merged with Hindustan Lever Limited (HLL) in 1998. It was one of the largest manufacturers of thermometers in the world with an annual capacity of 20 million thermometers. The unit was certified to EN 46002 standards.
The factory was set up in Kodaikanal (under an industrial licence) since the ambient temperature there (Kodaikanal is at an altitude of 2120 m above sea level), which varied between 2 and 20oC, would be conducive to negligible mercury vaporization. The factory, which was set up to US standards, had the following occupational health and safety measures in place.
Indoor air monitoring and regulation:
The plant was divided into non-mercury and mercury areas, which were physically separated by walls. The non-mercury area was the place where glass-forming operations were carried out before mercury was filled into the thermometers. The mercury area was the place where all operations like mercury filling, top chambering, contracting, scaling, grading to final packing of the thermometers took place. The plant also ran a glass crushing and mercury recovery unit to recover mercury from the scrap glass generated during manufacturing operation. The plant used a gold film mercury vapor analyser (Jerome 431 X Mercury Vapor Analyzer) with a self-calibrating facility to monitor air from 22 locations spread across these areas in the non-mercury and mercury areas. This analyzer is considered quite sensitive to monitor Hg vapor, with a sensitivity of detecting Hg in air upto 0.003 mg/m. The intention was to regulate mercury in the atmosphere to less than 0.05 mg/m 3sub of air by adopting the following methods:
• The main manufacturing area had a dimension of 60' x 100' with a ceiling height of 12'. A total of 25 exhaust fans fitted along the southeastern wall of the mercury area turned over the air in this area every 45 min for 16 h/day for all the operating days in a year. Similarly the mercury crusher building and the mercury distillation building also had adequate exhaust fans that would turn over the air in that area at a greater frequency (every 5 min). The flooring of the workplace was a cemented one.
• Vacuum cleaners with water seals were used to collect broken thermometers when breakage occurred. The factory floor was scrubbed and washed once a day with water to remove traces of mercury for further treatment at the effluent treatment plant.
• Operators in the mercury area of the plant were provided with special safety masks to filter out mercury vapors.
• All the above procedures were backed by an emergency procedure of opening all windows and cleaning the entire floor when mercury vapors exceeded 0.05 mg/m 3sub .
Occupational health surveillance
All employees underwent a monthly monitoring of mercury in urine through the use of a Cold Vapor Atomic Absorption Spectrometer (CVAAS). Employees whose urine mercury level exceeded 100 mg/L were deployed out of the mercury area and in all such cases, the mercury levels came back to acceptable levels within 1-2 months. Such employees were very rare during the working life of the plant (~1%). The biological monitoring was supplemented by an annual clinical evaluation with specific emphasis on the oral cavity, skin, kidneys, the central nervous system and the cardiopulmonary system. The medical tests included a hemogram and a urine examination for albumin, red blood cells, casts and crystals.
Over the years, the factory has been subject to statutory inspections and health evaluations by the factory inspectorate of the government, who did not find any mercury-related illness amongst the employees.
| Materials and Methods|| |
Health impact assessment
The health impact assessment used a combination of a cross-sectional epidemiological survey supplemented with a retrospective cohort study. The health impact assessment has been conducted in accordance with guidelines on studies in environmental epidemiology. The design of the study allowed an assessment of both current and historical exposures and outcome. Exposure assessment in both designs looked at environmental monitoring data coupled with results of biological monitoring. For biological monitoring, we used urinary mercury concentrations (HgU) as an appropriate biomarker. In risk assessment, biomarkers may be used in hazard identification, exposure assessment and to associate a response with the probability of a disease outcome. Clinical evaluations utilized a combination of an administered questionnaire as well as appropriate clinical tests including relevant biochemical investigations.
Cross-sectional epidemiological survey
In the year 2001, following apprehension from the local communities at Kodaikanal on the health and environmental impact of the factory operations, HLL conducted a comprehensive epidemiological surveillance covering 255 individuals (130 current permanent employees, 64 contract workers, 55 ex-employees and 6 scrap dealers). The ex-employees were those who responded to a newspaper advertisement inviting ex-employees to participate in the study. The clinical surveillance included the following:
A questionnaire modified on the one developed by the US Department of Labor, Mines, Safety and Health Administration for medical surveillance and biological monitoring for miners exposed to Arsenic, Cadmium, Lead and Mercury (technically reviewed by Center for Disease Control and Prevention - CDC, USA and the NIOSH, USA). An epidemiologist (trained at the London School of Hygiene) independently validated at site, the clinical evaluation based on the questionnaire.
The clinical evaluation included a thorough evaluation of the oral cavity, lungs, cardiovascular system, the eyes, skin, kidneys and the central nervous system. With specific reference to the central nervous system, the sensorimotor performance was evaluated using reflex evaluation, grip strength, handwriting analysis and vibration sense (128 Hz at index finger/great toe). Psychomotor tests included hand-eye coordination, visual fields and color discrimination tests, memory evaluation and gait test.
The clinical surveillance was supplemented by biological monitoring through the analysis of mercury in urine by Inductively Coupled Plasma Emission Spectrometer (ICP). The ICP method for detection of mercury in urine is sensitive, with detection limits in the sub-ppb range., The laboratory performing the ICP was a government approved one and followed appropriate internal and external quality control measures.
Other investigations included the analysis of blood for hemoglobin, total and differential counts, urine analysis for albumin and sugar as well as the estimation of blood urea and serum creatinine as markers for kidney functions.
A team of local doctors from Kodaikanal who were appropriately trained to ensure that there was no inter- and intra-observer variability administered the questionnaire and conducted the clinical evaluation. Each individual undergoing the evaluation gave his informed consent. Since the local community had expressed apprehension vis-a-vis the health of ex-employees of the thermometer plant, the community-designated doctor was invited, who participated in the validation of the clinical evaluation.
The employees at the time of the survey (n=130) underwent a repeat biological monitoring for mercury in urine in May 2001 post the closure of the factory. The factory closure was on the cards since thermometer manufacture did not fit in with the core business of Hindustan Lever Limited (detergents, skin care and foods business), and the company decided to exit from the thermometer business
Retrospective cohort analysis
To ascertain the impact of the factory operations on the health of all its employees, a retrospective cohort study of the health of all permanent employees who worked there from 1984 (a total of 290 employees over the working life of the plant) was undertaken. The retrospective study analyzed all available biological monitoring results of HgU, which was conducted over the years through CVAAS, annual clinical evaluations, morbidity and mortality data. The CVAAS as a method to monitor HgU levels is considered to be sensitive and reliable and may be used on either digested or undigested samples., The CVAAS underwent a daily quality control through calibration using standard strength solutions.
In terms of the toxicokinetics of mercury, it is believed that mercury has a half-life in the urine for about 40-90 days., These results reflect the existence of compartments with elimination half-lives of about 2-3 months, presumably in the kidney. WHO also recommends the determination of mercury in urine by the use of AAS as a way to monitor exposure to mercury vapors.
For the purpose of retrospective analysis, the individual and group historic exposure assessment was based on the biological monitoring results gathered from a total of 17,687 urinary mercury measurements by CVAAS. These analyses were based on the results of samples collected from employees, usually on a monthly basis at the beginning of the shift, throughout the working life of the plant.
On-site validation of the CVAAS methodology, calibration and quality control measures in place, was carried out by a team of specialists nominated by the Indian Association of Occupational Health, who observed and interviewed the operator responsible for conducting the analysis.
The retrospective analysis compared the results arising out of biological monitoring and clinical analyses for two distinct groups:, those working in the hazardous section within the plant and those working in the non-hazardous section within the plant. It also included a sickness absenteeism review.
The findings of the biological monitoring and clinical evaluation results were also compared with reports by other investigators on the health effects arising out of exposure to mercury and the available evidence on the threshold limits for exposure resulting in various health effects.
To augment our efforts in ascertaining if there were any health-related effects arising out of working in the factory, our medical officer wrote to leading medical professionals in Kodiakanal outlining our Occupational Health Surveillance Measures in place as well as seeking information from them on any employee who may have reported to them with symptoms attributable to mercury exposure. In addition, we conducted a hospital-based search for any admissions arising out of mercury-related symptoms in the hospitals of Kodaikanal. Data pertaining to mortality of employees was also analyzed with respect to exposure patterns, duration of service and cause of death (wherever available).
Historical exposure levels to mercury in the plant environment were analyzed from the environmental monitoring data records of air sampling (conducted over the years using a Jerome analyzer) covering the period 1988 to 2001.
External peer reviews and validation
At the request of the local community in Kodai, an eco-toxicological and health expert from TNO, Netherlands, reviewed the health and safety measures as well the impact of the factory operations on health and environment. He visited the site on a number of occasions and evaluated on-site health and safety measures and reviewed the health surveillance protocol including biological monitoring.
The protocol for clinical evaluation and the entire epidemiological surveillance was also independently reviewed by a team of experts from the All India Institute of Medical Sciences, Delhi (one of the premier medical institutes in the country).
In addition, an expert committee set up by the Indian Association of Occupational Health (IAOH) visited the site for an on-the-spot assessment, interviewed and validated the methodology of CVAAS analysis for Hg in urine and reviewed all health records and details of epidemiological surveillance conducted over the life of the plant.
| Results|| |
Cross-sectional epidemiological survey
The following tables detail the general information, symptomatology and clinical evaluation results pertaining to the 255 individuals who participated in the cross-sectional epidemiological survey conducted in March 2001 [Table - 1][Table - 2][Table - 3][Table - 4].
We analyzed the symptomatology (grouped by systems) in relation to the results of biological monitoring.
We conducted a repeat biological monitoring in May 2001 for all 130 employees who underwent the occupational health surveillance in March 2001. As compared to a mean HgU value of 23.1 mg/L for these employees in March 2001, these values had dropped to a mean of 10.1 mg/L in May 2001. (The factory was closed down in April 2001.) The WHO recommends group means of 50 mg/L to prevent health-based effects.
Retrospective cohort study
Group analyses: To understand the overall body burden of mercury over the working period of all employees, a total of 17,687 individual urinary mercury measurements (by CVAAS) gathered over the working life of the plant were analyzed.
As a first cut measurement, the group HgU means of all employees were tabulated from the year 1988 to 2001 to have an idea about overall exposures [Table - 5]. This first cut measurement was to have an idea vis-a-vis comparing them with WHO-recommended group means of HgU of 50 mg/L to prevent health-based effects.
Employees were then grouped and analyzed according to the departments in which they worked. Broadly they were categorized into two groups: those working in the hazardous section of the mercury plant (filling, distillation and crusher units) and those working in the rest of the plant.
Biological monitoring data for these groups were analyzed on a three-year cumulative basis. The following table profiles the three-year HgU levels to give an idea about the cumulative body burden for these three-year periods [Table - 6].
To understand individual variations, we undertook an analysis of all the individual HgU readings and prepared a cumulative frequency chart to study the spread of risk across various body burdens of mercury as evidenced by HgU levels in employees over the years. As depicted in [Table - 7], categorizes the cumulative frequency with respect to four different risk profiles, i.e., those employees with a mean annual HgU value of <50 mg/L, those with HgU between 50 and 60 mg/L, those with HgU between 60 and 70 mg/L and those with HgU of >70 mg/L.
Of particular interest were those employees with >70 mg/L since they would have corresponded to an exposure of Hg in air of >0.05 mg/m 3. [In India the permissible limits of mercury in air are 0.05 mg/m 3. (50 mg/m 3)† which correspond to an equivalent of HgU of 70 mg/L.] (Equivalent values are based on guideline provided by WHO.)
Individuals with yearly means of >70 mg/L (0-4% during the years 1988 to 2001) were followed up to determine if any of them continued to show such values in subsequent years. There were no individuals who had two consecutive yearly means of HgU >70 mg/L.
In view of community concerns that some employees may have died because of working in the thermometer plant as a consequence of exposure to mercury due to conditions like renal failure or CNS conditions, we undertook a mortality analysis of 10 employees who had worked with us and died either when in service or after leaving us. The results of this analysis are depicted in [Table - 8].
The exposure pattern of these individuals as evidenced by the analysis of HgU levels (wherever available) for these employees did not reveal any exposure of significance. There was also no correlation between the department they worked and mortality.
Environment monitoring results
Our retrospective analysis also reviewed historical exposure data as evidenced by levels of Hg in the atmosphere.
The [Table - 9] has been prepared based on the basis of monitoring at 15-23 locations across the factory on a daily basis for the years under consideration. The air monitoring data for the years 1994-1997 were not available for review. As seen in the table, the general average levels of mercury in atmosphere were much below the permissible limit (in India) of a time weighted average of 0.05 mg/m 3sub .†
†Indian Factories Act 1948, Second Schedule.
| Discussion|| |
Chronic exposure to mercury could lead to kidney and neurological toxicity (especially tremor), inflammation of the gums, weakness, fatigue, insomnia, allergic skin rash, loss of appetite and impaired memory. Our questionnaire elicited response to these symptoms and morbidities.
A study by Roels et al. used a questionnaire mainly to elicit symptoms related to the central nervous system disturbances. Several symptoms, mainly related to the central nervous system (memory disturbances, depressive feelings, fatigue and irritability), were more prevalent in the exposed subjects rather than the controls. The symptoms were however not related to exposure parameters. The authors therefore considered it possible that the reporting of these symptoms were influenced by the knowledge of mercury vapor exposure. Exposure in the range of 25-80 mg/m 3 increases incidence of symptoms like fatigue, irritability, loss of appetite.
In our study [Table - 2][Table - 3][Table - 4] also, the symptomatology did not have any significant correlation with the body burden of mercury (as HgU). Neither could we correlate any morbidity with exposure to Hg in view of very low levels of exposure, as evidenced by the results of the biological monitoring in these groups [Table - 1]. Three individuals with tremors were considered to be normal since their sample of handwriting taken at the time of the survey did not reveal any tremors.
We looked at some of the confounding factors, which could have caused common morbidity. For example in India, gingivitis is very common and is related to levels of poor oral hygiene.
The main target organs for health-related effects arising out of long-term exposure to mercury are the brain and the kidneys.
In order to understand the relationship between exposure and health effects, we reviewed relevant studies, and the [Table - 10] summarizes key studies correlating the urinary threshold values in relationship to the effects on the nervous system or the kidney.
Rosemann et al. found positive correlation between HgU levels (100 mg - 250 mg/L) and neuropsychological symptoms.
In a study conducted by Smith et al, short-term memory was affected in a group of individuals with a mean of 180 mg/L.
Based on neuromuscular, electromyographic and psychomotor tests, Miller et al. recommended that when HgU exceeds 100 mg/L, a person should be routinely examined to determine if any deterioration in the health status has taken place.
WHO also recommends that symptom-free workers with a concentration of mercury in urine >100 mg/L should also be kept away from exposure until the concentration drops to below that level. Langolf et al. found that the subclinical effects of mercury were mainly detectable in those workers whose HgU had exceeded 500 mg/L in the previous year.
Tremor, abnormal Romberg test, dysdiadochokinosis and difficulty with heel-to-toe gait were observed in thermometer plant workers subjected to personal breathing zone concentrations of 0.078 mg/m.
In order to prevent mercury-related ill health, the WHO recommends for workers a group mean of HgU of 50 mg/L as a health-based exposure limit. The results of the retrospective analyses has shown that employees in HLL had group HgU levels significantly lower than the recommended WHO limit [Table - 6][Table - 7]. This could be due to historically low levels of exposure to Hg in the thermometer plant.
Several studies have shown a correlation between airborne mercury and mercury in urine; but the results vary, and it is not clear if the ratio between such concentrations is constant at different exposure levels. Limiting the analysis to studies in which the exposure has been assessed using personal breathing zone mercury concentrations, it was estimated that in continuous 8h/day occupational exposure, an airborne mercury concentration of 1 mg/m 3 leads to an average urinary mercury concentration of 1.4 mg/L.
Using this derived relationship, the historical exposure of Hg in atmosphere to employees in the thermometer factory based on the biological monitoring results [Table - 6] would be as shown in [Table - 11].
The current regulation in India as laid down by the Indian Factories Act prescribes a TLV of 0.05 mg/m 3sub† for Hg in the work environment. †Indian Factories Act 1948, Second Schedule. As indicated [Table - 7], very few individuals had an exposure above these prescribed limits (based on the results of the biological monitoring), and even these few individuals (with a value of HgU of >70 mg/L) did not have a sustained exposure in subsequent years.
A review of the levels of Hg in different sections of the plant on the basis of monitoring at 15-23 locations across the factory on a daily basis indicates that levels in the plant were much lower than the prescribed limits in India [Table - 9]. Workplace safety and health measures contributed to minimizing significant exposures to Hg.
| Conclusions|| |
On the basis of the results of environmental monitoring, biological monitoring, clinical evaluation and review in comparison to published data on dose-response relationships, there is no evidence to suggest that any of the employees in the thermometer plant suffered from health effects that could be attributed to mercury exposure. Analysis of the mortality data of 10 individuals [Table - 8] who died either in service or after leaving employment has also not indicated any mortality that could be attributed to effects of mercury-related exposure. Community concerns have mainly been fanned by interested groups without any scientific evidence to substantiate claims of ill health amongst employees at the thermometer plant.
The ecotoxicological and health expert from TNO who reviewed health and safety measures as well as the epidemiological surveillance at the request of the local communities and a peer review conducted by the All India Institute of Medical Sciences as well as the Indian Association of Occupational Health have all independently validated the occupational health and safety measures at the plant and their efficacy.
Over the years, the factory has been subject to statutory inspections and health evaluations by the factory inspectorate of the government, who did not find any mercury-related illness amongst the employees.
| Acknowledgments|| |
The authors would like to acknowledge the expert inputs and validation report of various experts who reviewed the health data and validated the epidemiological surveillance and the results thereof. They include Dr. Tom Van Teunenbroek, formerly with TNO, Netherlands, and currently the team leader and advisor on international inspections with the ministry of VROM, Netherlands; Dr. Pandav and his team from the All India Institute of Medical Sciences; and the expert committee set up by the Indian Association of Occupational Health.
We are also thankful to Professor Dr. Prakash Kotecha from the Dept. of Community Medicine, Medical College, Vadodara, for validating the clinical evaluation on site.
Thanks are also due to Drs. Elamavazhuthi, Balasubramaniam, Saravanan and Ramesh Rao at Kodaikanal for participating in and conducting the clinical evaluation in March 2001.
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[Table - 1], [Table - 2], [Table - 3], [Table - 4], [Table - 5], [Table - 6], [Table - 7], [Table - 8], [Table - 9], [Table - 10], [Table - 11]
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