Occupational exposures account for only a minor proportion of the total number of cancers in the entire population. It has been estimated that 4% of all cancers can be attributed to occupational exposures, based on data from the United States, with a range of uncertainty from 2 to 8%. This implies that even total prevention of occupationally induced cancers would result in only a marginal reduction in national cancer rates.
However, for several reasons, this should not discourage efforts to prevent occupationally induced cancers. First, the estimate of 4% is an average figure for the entire population, including unexposed persons. Among people actually exposed to occupational carcinogens, the proportion of tumours attributable to occupation is much larger. Second, occupational exposures are avoidable hazards to which individuals are involuntarily exposed. An individual should not have to accept an increased risk of cancer in any occupation, especially if the cause is known. Third, occupationally induced cancers can be prevented by regulation, in contrast to cancers associated with lifestyle factors.
Prevention of occupationally induced cancer involves at least two stages: first, identification of a specific compound or occupational environment as carcinogenic; and second, imposing appropriate regulatory control. The principles and practice of regulatory control of known or suspected cancer hazards in the work environment vary considerably, not only among different parts of the developed and developing world, but also among countries of similar socio-economic development.
The International Agency for Research on Cancer (IARC) in Lyon, France, systematically compiles and evaluates epidemiological and experimental data on suspected or known carcinogens. The evaluations are presented in a series of monographs, which provide a basis for decisions on national regulations on the production and use of carcinogenic compounds (see “Occupational Carcinogens”, above.
The history of occupational cancer dates back to at least 1775, when Sir Percivall Pott published his classical report on scrotal cancer in chimney-sweeps, linking exposure to soot to the incidence of cancer. The finding had some immediate impact in that sweeps in some countries were granted the right to bathe at the end of the working day. Current studies of sweeps indicate that scrotal and skin cancer are now under control, although sweeps are still at increased risk for several other cancers.
In the 1890s, a cluster of bladder cancer was reported at a German dye factory by a surgeon at a nearby hospital. The causative compounds were later identified as aromatic amines, and these now appear in lists of carcinogenic substances in most countries. Later examples include skin cancer in radium-dial painters, nose and sinus cancer among woodworkers caused by inhalation of wood dust, and “mule-spinner’s disease”—that is, scrotal cancer among cotton industry workers caused by mineral oil mist. Leukaemia induced by exposure to benzene in the shoe repair and manufacturing industry also represents a hazard that has been reduced after the identification of carcinogens in the workplace.
In the case of linking asbestos exposure to cancer, this history illustrates a situation with a considerable time-lag between risk identification and regulatory action. Epidemiological results indicating that exposure to asbestos was associated with an increased risk of lung cancer were already starting to accumulate by the 1930s. More convincing evidence appeared around 1955, but it was not until the mid-1970s that effective steps for regulatory action began.
The identification of the hazards associated with vinyl chloride represents a different history, where prompt regulatory action followed identification of the carcinogen. In the 1960s, most countries had adopted an exposure limit value for vinyl chloride of 500 parts per million (ppm). In 1974, the first reports of an increased frequency of the rare tumour liver angiosarcoma among vinyl chloride workers were soon followed by positive animal experimental studies. After vinyl chloride was identified as carcinogenic, regulatory actions were taken for a prompt reduction of the exposure to the current limit of 1 to 5 ppm.
Methods Used for the Identificationof Occupational Carcinogens
The methods in the historical examples cited above range from observations of clusters of disease by astute clinicians to more formal epidemiological studies—that is, investigations of the disease rate (cancer rate) among human beings. Results from epidemiological studies are of high relevance for evaluations of the risk to humans. A major drawback of cancer epidemiological studies is that a long time period, usually at least 15 years, is necessary to demonstrate and evaluate the effects of an exposure to a potential carcinogen. This is unsatisfactory for surveillance purposes, and other methods must be applied for a quicker evaluation of recently introduced substances. Since the beginning of this century, animal carcinogenicity studies have been used for this purpose. However, the extrapolation from animals to humans introduces considerable uncertainty. The methods also have limitations in that a large number of animals must be followed for several years.
The need for methods with a more rapid response was partly met in 1971, when the short-term mutagenicity test (Ames test) was introduced. This test uses bacteria to measure the mutagenic activity of a substance (its ability to cause irreparable changes in the cellular genetic material, DNA). A problem in the interpretation of the results of bacterial tests is that not all substances causing human cancers are mutagenic, and not all bacterial mutagens are considered to be cancer hazards for human beings. However, the finding that a substance is mutagenic is usually taken as an indication that the substance might represent a cancer hazard for humans.
New genetic and molecular biology methods have been developed during the last 15 years, with the aim of detecting human cancer hazards. This discipline is termed “molecular epidemiology.” Genetic and molecular events are studied in order to clarify the process of cancer formation and thus develop methods for early detection of cancer, or indications of increased risk of the development of cancer. These methods include analysis of damage to the genetic material and the formation of chemical linkages (adducts) between pollutants and the genetic material. The presence of chromosomal aberrations clearly indicates effects on the genetic material which may be associated with cancer development. However, the role of molecular epidemiological findings in human cancer risk assessment remains to be settled, and research is under way to indicate more clearly exactly how results of these analyses should be interpreted.
Surveillance and Screening
The strategies for prevention of occupationally induced cancers differ from those applied for control of cancer associated with lifestyle or other environmental exposures. In the occupational field, the main strategy for cancer control has been reduction or total elimination of exposure to cancer-causing agents. Methods based on early detection by screening programmes, such as those applied for cervical cancer or breast cancer, have been of very limited importance in occupational health.
Information from population records on cancer rates and occupation may be used for surveillance of cancer frequencies in various occupations. Several methods to obtain such information have been applied, depending on the registries available. The limitations and possibilities depend largely on the quality of the information in the registries. Information on disease rate (cancer frequency) is typically obtained from local or national cancer registries (see below), or from death certificate data, while information on the age-composition and size of occupational groups is obtained from population registries.
The classical example of this type of information is the “Decennial supplements on occupational mortality,” published in the UK since the end of the nineteenth century. These publications use death certificate information on cause of death and on occupation, together with census data on frequencies of occupations in the entire population, to calculate cause-specific death rates in different occupations. This type of statistic is a useful tool to monitor the cancer frequency in occupations with known risks, but its ability to detect previously unknown risks is limited. This type of approach may also suffer from problems associated with systematic differences in the coding of occupations on the death certificates and in the census data.
The use of personal identification numbers in the Nordic countries has offered a special opportunity to link individual census data on occupations with cancer registration data, and to directly calculate cancer rates in different occupations. In Sweden, a permanent linkage of the censuses of 1960 and 1970 and the cancer incidence during subsequent years have been made available for researchers and have been used for a large number of studies. This Swedish Cancer-Environment Registry has been used for a general survey of certain cancers tabulated by occupation. The survey was initiated by a governmental committee investigating hazards in the work environment. Similar linkages have been performed in the other Nordic countries.
Generally, statistics based on routinely collected cancer incidence and census data have the advantage of ease in providing large amounts of information. The method gives information on the cancer frequencies regarding occupation only, not in relation to certain exposures. This introduces a considerable dilution of the associations, since exposure may differ considerably among individuals in the same occupation. Epidemiological studies of the cohort type (where the cancer experience among a group of exposed workers is compared with that in unexposed workers matched for age, sex and other factors) or the case-control type (where the exposure experience of a group of persons with cancer is compared to that in a sample of the general population) give better opportunities for detailed exposure description, and thus better opportunities for investigation of the consistency of any observed risk increase, for example by examining the data for any exposure-response trends.
The possibility of obtaining more refined exposure data together with routinely collected cancer notifications was investigated in a prospective Canadian case-control study. The study was set up in the Montreal metropolitan area in 1979. Occupational histories were obtained from males as they were added to the local cancer registry, and the histories were subsequently coded for exposure to a number of chemicals by occupational hygienists. Later, the cancer risks in relation to a number of substances were calculated and published (Siemiatycki 1991).
In conclusion, the continuous production of surveillance data based on recorded information provides an effective and comparatively easy way to monitor cancer frequency by occupation. While the main purpose achieved is surveillance of known risk factors, the possibilities for the identification of new risks are limited. Registry-based studies should not be used for conclusions regarding the absence of risk in an occupation unless the proportion of individuals significantly exposed is more precisely known. It is quite common that only a relatively small percentage of members of an occupation actually are exposed; for these individuals the substance may represent a substantial hazard, but this will not be observable (i.e., will be statistically diluted) when the entire occupational group is analysed as a single group.
Screening for occupational cancer in exposed populations for purposes of early diagnosis is rarely applied, but has been tested in some settings where exposure has been difficult to eliminate. For example, much interest has focused on methods for early detection of lung cancer among people exposed to asbestos. With asbestos exposures, an increased risk persists for a long time, even after cessation of exposure. Thus, continuous evaluation of the health status of exposed individuals is justified. Chest x rays and cytological investigation of sputum have been used. Unfortunately, when tested under comparable conditions neither of these methods reduces the mortality significantly, even if some cases may be detected earlier. One of the reasons for this negative result is that the prognosis of lung cancer is little affected by early diagnosis. Another problem is that the x rays themselves represent a cancer hazard which, while small for the individual, may be significant when applied to a large number of individuals (i.e., all those screened).
Screening also has been proposed for bladder cancer in certain occupations, such as the rubber industry. Investigations of cellular changes in, or mutagenicity of, workers’ urine have been reported. However, the value of following cytological changes for population screening has been questioned, and the value of the mutagenicity tests awaits further scientific evaluation, since the prognostic value of having increased mutagenic activity in the urine is not known.
Judgements on the value of screening also depend on the intensity of the exposure, and thus the size of the expected cancer risk. Screening might be more justified in small groups exposed to high levels of carcinogens than among large groups exposed to low levels.
To summarize, no routine screening methods for occupational cancers can be recommended on the basis of present knowledge. The development of new molecular epidemiological techniques may improve the prospects for early cancer detection, but more information is needed before conclusions can be drawn.
During this century, cancer registries have been set up at several locations throughout the world. The International Agency for Research on Cancer (IARC) (1992) has compiled data on cancer incidence in different parts of the world in a series of publications, “Cancer Incidence in Five Continents.” Volume 6 of this publication lists 131 cancer registries in 48 countries.
Two main features determine the potential usefulness of a cancer registry: a well-defined catchment area (defining the geographical area involved), and the quality and completeness of the recorded information. Many of those registries that were set up early do not cover a geographically well-defined area, but rather are confined to the catchment area of a hospital.
There are several potential uses of cancer registries in the prevention of occupational cancer. A complete registry with nationwide coverage and a high quality of recorded information can result in excellent opportunities for monitoring the cancer incidence in the population. This requires access to population data to calculate age-standardized cancer rates. Some registries also contain data on occupation, which therefore facilitates the monitoring of cancer risk in different occupations.
Registries also may serve as a source for the identification of cases for epidemiological studies of both the cohort and case-control types. In the cohort study, personal identification data of the cohort is matched to the registry to obtain information on the type of cancer (i.e., as in record linkage studies). This assumes that a reliable identifying system exists (for example, personal identification numbers in the Nordic countries) and that confidentiality laws do not prohibit use of the registry in this way. For case-control studies, the registry may be used as a source for cases, although some practical problems arise. First, the cancer registries cannot, for methodological reasons, be quite up to date regarding recently diagnosed cases. The reporting system, and necessary checks and corrections of the obtained information, results in some lag time. For concurrent or prospective case-control studies, where it is desirable to contact the individuals themselves soon after a cancer diagnosis, it usually is necessary to set up an alternative way of identifying cases, for example via hospital records. Second, in some countries, confidentiality laws prohibit the identification of potential study participants who are to be contacted personally.
Registries also provide an excellent source for calculating background cancer rates to use for comparison of the cancer frequency in cohort studies of certain occupations or industries.
In studying cancer, cancer registries have several advantages over mortality registries commonly found in many countries. The accuracy of the cancer diagnoses is often better in cancer registries than in mortality registries, which are usually based on death certificate data. Another advantage is that the cancer registry often holds information on histological tumour type, and also permits the study of living persons with cancer, and is not limited to deceased persons. Above all, registries hold cancer morbidity data, permitting the study of cancers that are not rapidly fatal and/or not fatal at all.
There are three main strategies for reducing workplace exposures to known or suspected carcinogens: elimination of the substance, reduced exposure by reduced emission or improved ventilation, and personal protection of the workers.
It has long been debated whether a true threshold for carcinogen exposure exists, below which no risk is present. It is often assumed that the risk should be extrapolated linearly down to zero risk at zero exposure. If this is the case, then no exposure limit, no matter how low, would be considered entirely risk-free. Despite this, many countries have defined exposure limits for some carcinogenic substances, while, for others, no exposure limit value has been assigned.
Elimination of a compound may give rise to problems when replacement substances are introduced and when the toxicity of the replacement substance must be lower than that of the substance replaced.
Reducing the exposure at the source may be relatively easily accomplished for process chemicals by encapsulation of the process and ventilation. For example, when the carcinogenic properties of vinyl chloride were discovered, the exposure limit value for vinyl chloride was lowered by a factor of one hundred or more in several countries. Although this standard was at first considered impossible to achieve by industry, later techniques allowed compliance with the new limit. Reduction of exposure at the source may be difficult to apply to substances that are used under less controlled conditions, or are formed during the work operation (e.g., motor exhausts). The compliance with exposure limits requires regular monitoring of workroom air levels.
When exposure cannot be controlled either by elimination or by reduced emissions, the use of personal protection devices is the only remaining way to minimize the exposure. These devices range from filter masks to air-supplied helmets and protective clothing. The main route of exposure must be considered in deciding appropriate protection. However, many personal protection devices cause discomfort to the user, and filter masks introduce an increased respiratory resistance which may be very significant in physically demanding jobs. The protective effect of respirators is generally unpredictable and depends on several factors, including how well the mask is fitted to the face and how often filters are changed. Personal protection must be considered as a last resort, to be attempted only when more effective ways of reducing exposure fail.
It is striking how little research has been done to evaluate the impact of programmes or strategies to reduce the risk to workers of known occupational cancer hazards. With the possible exception of asbestos, few such evaluations have been conducted. Developing better methods for control of occupational cancer should include an evaluation of how present knowledge is actually put to use.
Improved control of occupational carcinogens in the workplace requires the development of a number of different areas of occupational safety and health. The process of identification of risks is a basic prerequisite for reducing exposure to carcinogens in the workplace. Risk identification in the future must solve certain methodological problems. More refined epidemiological methods are required if smaller risks are to be detected. More precise data on exposure for both the substance under study and possible confounding exposures will be necessary. More refined methods for description of the exact dose of the carcinogen delivered to the specific target organ also will increase the power of exposure-response calculations. Today, it is not uncommon that very crude substitutes are used for the actual measurement of target organ dose, such as the number of years employed in the industry. It is quite clear that such estimates of dose are considerably misclassified when used as a surrogate for dose. The presence of an exposure-response relationship is usually taken as strong evidence of an aetiological relationship. However, the reverse, lack of demonstration of an exposure-response relationship, is not necessarily evidence that no risk is involved, especially when crude measures of target organ dose are used. If target organ dose could be determined, then actual dose-response trends would carry even more weight as evidence for causation.
Molecular epidemiology is a rapidly growing area of research. Further insight into the mechanisms of cancer development can be expected, and the possibility of the early detection of carcinogenic effects will lead to earlier treatment. In addition, indicators of carcinogenic exposure will lead to improved identification of new risks.
Development of methods for supervision and regulatory control of the work environment are as necessary as methods for the identification of risks. Methods for regulatory control differ considerably even among western countries. The systems for regulation used in each country depend largely on socio-political factors and the status of labour rights. The regulation of toxic exposures is obviously a political decision. However, objective research into the effects of different types of regulatory systems could serve as a guide for politicians and decision-makers.
A number of specific research questions also need to be addressed. Methods to describe the expected effect of withdrawal of a carcinogenic substance or reduction of exposure to the substance need to be developed (i.e., the impact of interventions must be assessed). The calculation of the preventive effect of risk reduction raises certain problems when interacting substances are studied (e.g., asbestos and tobacco smoke). The preventive effect of removing one of two interacting substances is comparatively greater than when the two have only a simple additive effect.
The implications of the multistage theory of carcinogenesis for the expected effect of withdrawal of a carcinogen also adds a further complication. This theory states that the development of cancer is a process involving several cellular events (stages). Carcinogenic substances may act either in early or late stages, or both. For example, ionizing radiation is believed to affect mainly early stages in inducing certain cancer types, while arsenic acts mainly at late stages in lung cancer development. Tobacco smoke affects both early and late stages in the carcinogenic process. The effect of withdrawing a substance involved in an early stage would not be reflected in a reduced cancer rate in the population for a long time, while the removal of a “late-acting” carcinogen would be reflected in a reduced cancer rate within a few years. This is an important consideration when evaluating the effects of risk-reduction intervention programmes.
Finally, the effects of new preventive factors have recently attracted considerable interest. During the last five years, a large number of reports have been published on the preventive effect on lung cancer of consuming fruits and vegetables. The effect seems to be very consistent and strong. For example, the risk of lung cancer has been reported as double among those with a low consumption of fruits and vegetables versus those with high intake. Thus, future studies of occupational lung cancer would have greater precision and validity if individual data on fruit and vegetable consumption can be included in the analysis.
In conclusion, improved prevention of occupational cancer involves both improved methods for risk identification and more research on the effects of regulatory control. For risk identification, developments in epidemiology should mainly be directed toward better exposure information, while in the experimental field, validation of the results of molecular epidemiological methods regarding cancer risk are needed.