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Measuring Effects of Exposures

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Epidemiology involves measuring the occurrence of disease and quantifying associations between diseases and exposures.

Measures of Disease Occurrence

Disease occurrence can be measured by frequencies (counts) but is better described by rates, which are composed of three elements: the number of people affected (numerator), the number of people in the source or base population (i.e., the population at risk) from which the affected persons come, and the time period covered. The denominator of the rate is the total person-time experienced by the source population. Rates allow more informative comparisons between populations of different sizes than counts alone. Risk, the probability of an individual developing disease within a specified time period, is a proportion, ranging from 0 to 1, and is not a rate per se. Attack rate, the proportion of people in a population who are affected within a specified time period, is technically a measure of risk, not a rate.

Disease-specific morbidity includes incidence, which refers to the number of persons who are newly diagnosed with the disease of interest. Prevalence refers to the number of existing cases. Mortality refers to the number of persons who die.

Incidence is defined as the number of newly diagnosed cases within a specified time period, whereas the incidence rate is this number divided by the total person-time experienced by the source population (table 1). For cancer, rates are usually expressed as annual rates per 100,000 people. Rates for other more common diseases may be expressed per a smaller number of people. For example, birth defect rates are usually expressed per 1,000 live births. Cumulative incidence, the proportion of people who become cases within a specified time period, is a measure of average risk for a population. 

Table 1. Measures of disease occurrence: Hypothetical population observed for a five-year period

Newly diagnosed cases

10

Previously diagnosed living cases

12

Deaths, all causes*

5

Deaths, disease of interest

3

Persons in population

100

Years observed

5

Incidence

10 persons

Annual incidence rate

Point prevalence (at end of year 5)

(10 + 12 - 3) = 19 persons

Period prevalence (five-year period)

(10 + 12) = 22 persons

Annual death rate

Annual mortality rate

*To simplify the calculations, this example assumes that all deaths occurred at the end of the five-year period so that all 100 persons in the population were alive for the full five years.

Prevalence includes point prevalence, the number of cases of disease at a point in time, and period prevalence, the total number of cases of a disease known to have existed at some time during a specified period.

Mortality, which concerns deaths rather than newly diagnosed cases of disease, reflects factors that cause disease as well as factors related to the quality of medical care, such as screening, access to medical care, and availability of effective treatments. Consequently, hypothesis-generating efforts and aetiological research may be more informative and easier to interpret when based on incidence rather than on mortality data. However, mortality data are often more readily available on large populations than incidence data.

The term death rate is generally accepted to mean the rate for deaths from all causes combined, whereas mortality rate is the rate of death from one specific cause. For a given disease, the case-fatality rate (technically a proportion, not a rate) is the number of persons dying from the disease during a specified time period divided by the number of persons with the disease. The complement of the case-fatality rate is the survival rate. The five-year survival rate is a common benchmark for chronic diseases such as cancer.

The occurrence of a disease may vary across subgroups of the population or over time. A disease measure for an entire population, without consideration of any subgroups, is called a crude rate. For example, an incidence rate for all age groups combined is a crude rate. The rates for the individual age groups are the age-specific rates. To compare two or more populations with different age distributions, age-adjusted (or, age-standardized) rates should be calculated for each population by multiplying each age-specific rate by the per cent of the standard population (e.g., one of the populations under study, the 1970 US population) in that age group, then summing over all age groups to produce an overall age-adjusted rate. Rates can be adjusted for factors other than age, such as race, gender or smoking status, if the category-specific rates are known.

Surveillance and evaluation of descriptive data can provide clues to disease aetiology, identify high-risk subgroups that may be suitable for intervention or screening programmes, and provide data on the effectiveness of such programmes. Sources of information that have been used for surveillance activities include death certificates, medical records, cancer registries, other disease registries (e.g., birth defects registries, end-stage renal disease registries), occupational exposure registries, health or disability insurance records and workmen’s compensation records.

Measures of Association

Epidemiology attempts to identify and quantify factors that influence disease. In the simplest approach, the occurrence of disease among persons exposed to a suspect factor is compared to the occurrence among persons unexposed. The magnitude of an association between exposure and disease can be expressed in either absolute or relative terms. (See also "Case Study: Measures").

Absolute effects are measured by rate differences and risk differences (table 2). A rate difference is one rate minus a second rate. For example, if the incidence rate of leukaemia among workers exposed to benzene is 72 per 100,000 person-years and the rate among non-exposed workers is 12 per 100,000 person-years, then the rate difference is 60 per 100,000 person-years. A risk difference is a difference in risks or cumulative incidence and can range from -1 to 1. 

 


Table 2. Measures of association for a cohort study

 

 

Cases

Person-years at risk

Rate per 100,000

Exposed

100

20,000

500

Unexposed

200

80,000

250

Total

300

100,000

300

Rate Difference (RD) = 500/100,000 - 250/100,000

= 250/100,000 per year

(146.06/100,000 - 353.94/100,000)*

Rate ratio (or relative risk) (RR) =  

Attributable risk in the exposed (ARe) = 100/20,000 - 200/80,000

= 250/100,000 per year

Attributable risk per cent in the exposed (ARe%) =

 Population attributable risk (PAR) = 300/100,000 - 200/80,000

= 50/100,000 per year

Population attributable risk per cent (PAR%) =

 * In parentheses 95% confidence intervals computed using the formulas in the boxes.


 

Relative effects are based on ratios of rates or risk measures, instead of differences. A rate ratio is the ratio of a rate in one population to the rate in another. The rate ratio has also been called the risk ratio, relative risk, relative rate, and incidence (or mortality) rate ratio. The measure is dimensionless and ranges from 0 to infinity. When the rate in two groups is similar (i.e., there is no effect from the exposure), the rate ratio is equal to unity (1). An exposure that increased risk would yield a rate ratio greater than unity, while a protective factor would yield a ratio between 0 and 1. The excess relative risk is the relative risk minus 1. For example, a relative risk of 1.4 may also be expressed as an excess relative risk of 40%.

In case-control studies (also called case-referent studies), persons with disease are identified (cases) and persons without disease are identified (controls or referents). Past exposures of the two groups are compared. The odds of being an exposed case is compared to the odds of being an exposed control. Complete counts of the source populations of exposed and unexposed persons are not available, so disease rates cannot be calculated. Instead, the exposed cases can be compared to the exposed controls by calculation of relative odds, or the odds ratio (table 3). 

 


Table 3. Measures of association for case-control studies: Exposure to wood dust and adenocarcinoma of the nasal cavity and paranasal sinues

 

 

Cases

Controls

Exposed

18

55

Unexposed

5

140

Total

23

195

 

Relative odds (odds ratio) (OR) =

Attributable risk per cent in the exposed () =

Population attributable risk per cent (PAR%) =

where = proportion of exposed controls = 55/195 = 0.28

 

* In parentheses 95% confidence intervals computed using the formulas in the box overleaf.

Source: Adapted from Hayes et al. 1986.


 

Relative measures of effect are used more frequently than absolute measures to report the strength of an association. Absolute measures, however, may provide a better indication of the public health impact of an association. A small relative increase in a common disease, such as heart disease, may affect more persons (large risk difference) and have more of an impact on public health than a large relative increase (but small absolute difference) in a rare disease, such as angiosarcoma of the liver.

Significance Testing

Testing for statistical significance is often performed on measures of effect to evaluate the likelihood that the effect observed differs from the null hypothesis (i.e., no effect). While many studies, particularly in other areas of biomedical research, may express significance by p-values, epidemiological studies typically present confidence intervals (CI) (also called confidence limits). A 95% confidence interval, for example, is a range of values for the effect measure that includes the estimated measure obtained from the study data and that which has 95% probability of including the true value. Values outside the interval are deemed to be unlikely to include the true measure of effect. If the CI for a rate ratio includes unity, then there is no statistically significant difference between the groups being compared.

Confidence intervals are more informative than p-values alone. A p-value’s size is determined by either or both of two reasons. Either the measure of association (e.g., rate ratio, risk difference) is large or the populations under study are large. For example, a small difference in disease rates observed in a large population may yield a highly significant p-value. The reasons for the large p-value cannot be identified from the p-value alone. Confidence intervals, however, allow us to disentangle the two factors. First, the magnitude of the effect is discernible by the values of the effect measure and the numbers encompassed by the interval. Larger risk ratios, for example, indicate a stronger effect. Second, the size of the population affects the width of the confidence interval. Small populations with statistically unstable estimates generate wider confidence intervals than larger populations.

The level of confidence chosen to express the variability of the results (the “statistical significance”) is arbitrary, but has traditionally been 95%, which corresponds to a p-value of 0.05. A 95% confidence interval has a 95% probability of containing the true measure of the effect. Other levels of confidence, such as 90%, are occasionally used.

Exposures can be dichotomous (e.g., exposed and unexposed), or may involve many levels of exposure. Effect measures (i.e., response) can vary by level of exposure. Evaluating exposure-response relationships is an important part of interpreting epidemiological data. The analogue to exposure-response in animal studies is “dose-response”. If the response increases with exposure level, an association is more likely to be causal than if no trend is observed. Statistical tests to evaluate exposure-response relationships include the Mantel extension test and the chi-square trend test.

Standardization

To take into account factors other than the primary exposure of interest and the disease, measures of association may be standardized through stratification or regression techniques. Stratification means dividing the populations into homogenous groups with respect to the factor (e.g., gender groups, age groups, smoking groups). Risk ratios or odds ratios are calculated for each stratum and overall weighted averages of the risk ratios or odds ratios are calculated. These overall values reflect the association between the primary exposure and disease, adjusted for the stratification factor, i.e., the association with the effects of the stratification factor removed.

A standardized rate ratio (SRR) is the ratio of two standardized rates. In other words, an SRR is a weighted average of stratum-specific rate ratios where the weights for each stratum are the person-time distribution of the non-exposed, or referent, group. SRRs for two or more groups may be compared if the same weights are used. Confidence intervals can be constructed for SRRs as for rate ratios.

The standardized mortality ratio (SMR) is a weighted average of age-specific rate ratios where the weights (e.g., person-time at risk) come from the group under study and the rates come from the referent population, the opposite of the situation in a SRR. The usual referent population is the general population, whose mortality rates may be readily available and based on large numbers and thus are more stable than using rates from a non-exposed cohort or subgroup of the occupational population under study. Using the weights from the cohort instead of the referent population is called indirect standardization. The SMR is the ratio of the observed number of deaths in the cohort to the expected number, based on the rates from the referent population (the ratio is typically multiplied by 100 for presentation). If no association exists, the SMR equals 100. It should be noted that because the rates come from the referent population and the weights come from the study group, two or more SMRs tend not to be comparable. This non-comparability is often forgotten in the interpretation of epidemiological data, and erroneous conclusions can be drawn.

Healthy Worker Effect

It is very common for occupational cohorts to have lower total mortality than the general population, even if the workers are at increased risk for selected causes of death from workplace exposures. This phenomenon, called the healthy worker effect, reflects the fact that any group of employed persons is likely to be healthier, on average, than the general population, which includes workers and persons unable to work due to illnesses and disabilities. The overall mortality rate in the general population tends to be higher than the rate in workers. The effect varies in strength by cause of death. For example, it appears to be less important for cancer in general than for chronic obstructive lung disease. One reason for this is that it is likely that most cancers would not have developed out of any predisposition towards cancer underlying job/career selection at a younger age. The healthy worker effect in a given group of workers tends to diminish over time.

Proportional Mortality

Sometimes a complete tabulation of a cohort (i.e., person-time at risk) is not available and there is information only on the deaths or some subset of deaths experienced by the cohort (e.g., deaths among retirees and active employees, but not among workers who left employment before becoming eligible for a pension). Computation of person-years requires special methods to deal with person-time assessment, including life-table methods. Without total person-time information on all cohort members, regardless of disease status, SMRs and SRRs cannot be calculated. Instead, proportional mortality ratios (PMRs) can be used. A PMR is the ratio of the observed number of deaths due to a specific cause in comparison to the expected number, based on the proportion of total deaths due to the specific cause in the referent population, multiplied by the number of total deaths in the study group, multiplied by 100.

Because the proportion of deaths from all causes combined must equal 1 (PMR=100), some PMRs may appear to be in excess, but are actually artificially inflated due to real deficits in other causes of death. Similarly, some apparent deficits may merely reflect real excesses of other causes of death. For example, if aerial pesticide applicators have a large real excess of deaths due to accidents, the mathematical requirement that the PMR for all causes combined equal 100 may cause some one or other causes of death to appear deficient even if the mortality is excessive. To ameliorate this potential problem, researchers interested primarily in cancer can calculate proportionate cancer mortality ratios (PCMRs). PCMRs compare the observed number of cancer deaths to the number expected based on the proportion of total cancer deaths (rather than all deaths) for the cancer of interest in the referent population multiplied by the total number of cancer deaths in the study group, multiplied by 100. Thus, the PCMR will not be affected by an aberration (excess or deficit) in a non-cancer cause of death, such as accidents, heart disease or non-malignant lung disease.

PMR studies can better be analysed using mortality odds ratios (MORs), in essence analysing the data as if they were from a case-control study. The “controls” are the deaths from a subset of all deaths that are thought to be unrelated to the exposure under study. For example, if the main interest of the study were cancer, mortality odds ratios could be calculated comparing exposure among the cancer deaths to exposure among the cardiovascular deaths. This approach, like the PCMR, avoids the problems with the PMR which arise when a fluctuation in one cause of death affects the apparent risk of another simply because the overall PMR must equal 100. The choice of the control causes of death is critical, however. As mentioned above, they must not be related to the exposure, but the possible relationship between exposure and disease may not be known for many potential control diseases.

Attributable Risk

There are measures available which express the amount of disease that would be attributable to an exposure if the observed association between the exposure and disease were causal. The attributable risk in the exposed (ARe) is the disease rate in the exposed minus the rate in the unexposed. Because disease rates cannot be measured directly in case-control studies, the ARe is calculable only for cohort studies. A related, more intuitive, measure, the attributable risk percent in the exposed (ARe%), can be obtained from either study design. The ARe% is the proportion of cases arising in the exposed population that is attributable to the exposure (see table 2 and table 3 for formula). The ARe% is the rate ratio (or the odds ratio) minus 1, divided by the rate ratio (or odds ratio), multiplied by 100.

The population attributable risk (PAR) and the population attributable risk per cent (PAR%), or aetiological fraction, express the amount of disease in the total population, which is comprised of exposed and unexposed persons, that is due to the exposure if the observed association is causal. The PAR can be obtained from cohort studies (table 28.3 ) and the PAR% can be calculated in both cohort and case-control studies (table 2 and table 3).

Representativeness

There are several measures of risk that have been described. Each assumes underlying methods for counting events and in the representatives of these events to a defined group. When results are compared across studies, an understanding of the methods used is essential for explaining any observed differences.

 

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Epidemiology and Statistics References

Ahlbom, A. 1984. Criteria of causal association in epidemiology. In Health, Disease, and Causal Explanations in Medicine, edited by L Nordenfelt and BIB Lindahl. Dordrecht: D Reidel.

American Conference of Government Industrial Hygienists (ACGIH). 1991. Exposure Assessment for Epidemiology and Hazard Control, edited by SM Rappaport and TJ Smith. Chelsea, Mich.:Lewis.

Armstrong, BK, E White, and R Saracci. 1992. Principles of Exposure Measurement in Epidemiology. Oxford: Oxford Univ. Press.

Ashford, NA, CI Spadafor, DB Hattis, and CC Caldart. 1990. Monitoring the Worker for Exposure and Disease. Baltimore: Johns Hopkins Univ. Press.

Axelson, O. 1978. Aspects on confounding in occupational health epidemiology. Scand J Work Environ Health 4:85-89.

—. 1994. Some recent developments in occupational epidemiology. Scand J Work Environ Health 20 (Special issue):9-18.

Ayrton-Paris, JA. 1822. Pharmacologia.

Babbie, E. 1992. The Practice of Social Research. Belmont, Calif.: Wadsworth.

Beauchamp, TL, RR Cook, WE Fayerweather, GK Raabe, WE Thar, SR Cowles, and GH Spivey. 1991. Ethical Guidelines for Epidemiologists. J Clin Epidemiol 44 Suppl. I:151S-169S.

Bell, B. 1876. Paraffin epithelioma of the scrotum. Edinburgh Med J 22:135.

Blondin, O and C Viau. 1992. Benzo(a)pyrene-blood protein adducts in wild woodchucks used as biological sentinels of environmental polycyclic aromatic hydrocarbons contamination. Arch Environ Contam Toxicol 23:310-315.

Buck, C. 1975. Popper’s philosophy for epidemiologists. Int J Epidemiol 4:159-168.

Case, RAM and ME Hosker. 1954. Tumour on the urinary bladder as an occupational disease in the rubber industry in England and Wales. Brit J Prevent Soc Med 8:39-50.

Checkoway, H, NE Pearce, and DJ Crawford-Brown. 1989. Research Methods in Occupational Epidemiology. New York: Oxford Univ. Press.

Clayson, DB. 1962. Chemical Carcinogenesis. London: JA Churchill.

Clayton, D. 1992. Teaching statistical methods in epidemiology. In Epidemiology. What You Should Know and What You Could Do, edited by J Olsen and D Trichopoulos. Oxford: Oxford Univ. Press.

Clayton, D and M Hills. 1993. Statistical Models in Epidemiology. New York: Oxford Univ. Press.

Cornfield, J. 1954. Statistical relationships and proof in medicine. Am Stat 8:19-21.

Council for International Organizations of Medical Sciences (CIOMS). 1991. International Guidelines for Ethical Review of Epidemiologic Studies. Geneva: CIOMS.

Czaja, R and J Blair. 1996. Designing Surveys. Thousand Oaks, Calif: Pine Forge Press.

Doll, R. 1952. The causes of death among gas-workers with special reference to cancer of the lung. Brit J Ind Med 9:180-185.

—. 1955. Mortality from lung cancer in asbestos workers. Brit J Ind Med 12:81-86.

Droz, PO and MM Wu. 1991. Biological monitoring strategies. In Exposure Assessment for Epidemiology and Hazard Control, edited by SM Rappaport and TJ Smith. Chelsea, Mich.: Lewis.

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

Gardner, MJ and DG Altman. 1989. Statistics With Confidence. Confidence Intervals and Statistical Guidelines. London: BMJ Publishing House.

Garfinkel, L. 1984. Classics in oncology; E. Cuyler Hammond, ScD. Ca-Cancer Journal for Clinicians. 38(1): 23-27

Giere, RN. 1979. Understanding Scientific Reasoning. New York: Holt Rinehart & Winston.

Glickman, LT. 1993. Natural exposure studies in pet animals: Sentinels for environmental carcinogens. Vet Can Soc Newslttr 17:5-7.

Glickman, LT, LM Domanski, TG Maguire, RR Dubielzig, and A Churg. 1983. Mesothelioma in pet dogs associated with exposure of their owners to asbestos. Environmental Research 32:305-313.

Gloyne, SR. 1935. Two cases of squamous carcinoma of the lung occurring in asbestosis. Tubercle 17:5-10.

—. 1951. Pneumoconiosis: Histological survey of necropsy material in 1,205 cases. Lancet 1:810-814.

Greenland, S. 1987. Quantitative methods in the review of epidemiological literature. Epidemiol Rev 9:1-30.

—. 1990. Randomization, statistics, and causal inference. Epidemiology 1:421-429.

Harting, FH and W Hesse. 1879. Der Lungenkrebs, die bergkrankheit in den Schneeberger Gruben. Vierteljahrsschr Gerichtl Med Offentl Gesundheitswesen CAPS 30:296-307.

Hayes, RB, JW Raatgever, A de Bruyn, and M Gerin. 1986. Cancer of the nasal cavity and paranasal sinuses, and formaldehyde exposure. Int J Cancer 37:487-492.

Hayes, HM, RE Tarone, HW Casey, and DL Huxsoll. 1990. Excess of seminomas observed in Vietnam service US military working dogs. J Natl Cancer Inst 82:1042-1046.

Hernberg, S. 1992. Introduction to Occupational Epidemiology. Chelsea, Mich.: Lewis.
Hill, AB. 1965. The environment and disease: Association or causation? Proc Royal Soc Med 58:295-300.

Hume, D. 1978. A Treatise of Human Nature. Oxford: Clarendon Press.

Hungerford, LL, HL Trammel, and JM Clark. 1995. The potential utility of animal poisoning data to identify human exposure to environmental toxins. Vet Hum Toxicol 37:158-162.

Jeyaratnam, J. 1994. Transfer of hazardous industries. In Occupational Cancer in Developing Countries, edited by NE Pearce, E Matos, H Vainio, P Boffetta, and M Kogevinas. Lyon: IARC.

Karhausen, LR. 1995. The poverty of Popperian epidemiology. Int J Epidemiol 24:869-874.

Kogevinas, M, P Boffetta, and N Pearce. 1994. Occupational exposure to carcinogens in developing countries. In Occupational Cancer in Developing Countries, edited by NE Pearce, E Matos, H Vainio, P Boffetta, and M Kogevinas. Lyon: IARC.

LaDou, J. 1991. Deadly migration. Tech Rev 7:47-53.

Laurell, AC, M Noriega, S Martinez, and J Villegas. 1992. Participatory research on workers’ health. Soc Sci Med 34:603-613.

Lilienfeld, AM and DE Lilienfeld. 1979. A century of case-control studies: progress? Chron Dis 32:5-13.

Loewenson, R and M Biocca. 1995. Participatory approaches in occupational health research. Med Lavoro 86:263-271.

Lynch, KM and WA Smith. 1935. Pulmonary asbestosis. III Carcinoma of lung in asbestos-silicosis. Am J Cancer 24:56-64.

Maclure, M. 1985. Popperian refutation in epidemiolgy. Am J Epidemiol 121:343-350.

—. 1988. Refutation in epidemiology: Why else not? In Causal Inference, edited by KJ Rothman. Chestnut Hill, Mass.: Epidemiology Resources.

Martin, SW, AH Meek, and P Willeberg. 1987. Veterinary Epidemiology. Des Moines: Iowa State Univ. Press.

McMichael, AJ. 1994. Invited commentary -"Molecular epidemiology": New pathway or new travelling companion? Am J Epidemiol 140:1-11.

Merletti, F and P Comba. 1992. Occupational epidemiology. In Teaching Epidemiology. What You Should Know and What You Could Do, edited by J Olsen and D Trichopoulos. Oxford: Oxford Univ. Press.

Miettinen, OS. 1985. Theoretical Epidemiology. Principles of Occurrence Research in Medicine. New York: John Wiley & Sons.

Newell, KW, AD Ross, and RM Renner. 1984. Phenoxy and picolinic acid herbicides and small-intestinal adenocarcinoma in sheep. Lancet 2:1301-1305.

Olsen, J, F Merletti, D Snashall, and K Vuylsteek. 1991. Searching for Causes of Work-Related Diseases. An Introduction to Epidemiology At the Work Site. Oxford: Oxford Medical Publications, Oxford Univ. Press.

Pearce, N. 1992. Methodological problems of time-related variables in occupational cohort studies. Rev Epidmiol Med Soc Santé Publ 40 Suppl: 43-54.

—. 1996. Traditional epidemiology, modern epidemiology and public health. Am J Public Health 86(5): 678-683.

Pearce, N, E Matos, H Vainio, P Boffetta, and M Kogevinas. 1994. Occupational cancer in developing countries. IARC Scientific Publications, no. 129. Lyon: IARC.

Pearce, N, S De Sanjose, P Boffetta, M Kogevinas, R Saracci, and D Savitz. 1995. Limitations of biomarkers of exposure in cancer epidemiology. Epidemiology 6:190-194.

Poole, C. 1987. Beyond the confidence interval. Am J Public Health 77:195-199.

Pott, P. 1775. Chirurgical Observations. London: Hawes, Clarke & Collins.

Proceedings of the Conference on Retrospective Assessment of Occupational Exposures in Epidemiology, Lyon, 13-15 April, 1994. 1995. Lyon: IARC .

Ramazzini, B. 1705. De Morbis Artificum Diatriva. Typis Antonii Capponi. Mutinae, MDCC. London: Andrew Bell & Others.

Rappaport, SM, H Kromhout, and E Symanski. 1993. Variation of exposure between workers in homogeneous exposure groups. Am Ind Hyg Assoc J 54(11):654-662.

Reif, JS, KS Lower, and GK Ogilvie. 1995. Residential exposure to magnetic fields and risk of canine lymphoma. Am J Epidemiol 141:3-17.

Reynolds, PM, JS Reif, HS Ramsdell, and JD Tessari. 1994. Canine exposure to herbicide-treated lawns and urinary excretion of 2,4-dichlorophenoxyacetic acid. Canc Epidem, Biomark and Prevention 3:233-237.

Robins, JM, D Blevins, G Ritter, and M Wulfsohn. 1992. G-estimation of the effect of prophylaxis therapy for pneumocystis carinii pneumonia on the survival of Aids patients. Epidemiology 3:319-336.

Rothman, KJ. 1986. Modern Epidemiology. Boston: Little, Brown & Co.

Saracci, R. 1995. Epidemiology: Yesterday, today, tomorrow. In Lectures and Current Topics in Epidemiology. Florence: European Educational Programme in Epidemiology.

Schaffner, KF. 1993. Discovery and Explanation in Biology and Medicine. Chicago: Univ. of Chicago Press.

Schlesselman, JJ. 1987. “Proof” of cause and effect in epidemiologic studies: Criteria for judgement. Prevent Med 16:195-210.

Schulte, P. 1989. Interpretation and communcication of the results of medical field investigations. J Occup Med 31:5889-5894.

Schulte, PA, WL Boal, JM Friedland, JT Walker, LB Connally, LF Mazzuckelli, and LJ Fine. 1993. Methodological issues in risk communications to workers. Am J Ind Med 23:3-9.

Schwabe, CW. 1993. The current epidemiological revolution in veterinary medicine. Part II. Prevent Vet Med 18:3-16.

Seidman, H, IJ Selikoff, and EC Hammond. 1979. Short-term asbestos work exposure and long-term observation. Ann NY Acad Sci 330:61-89.

Selikoff, IJ, EC Hammond, and J Churg. 1968. Asbestos exposure, smoking and neoplasia. JAMA 204:106-112.

—. 1964. Asbestos exposure and neoplasia. JAMA 188, 22-26.

Siemiatycki, J, L Richardson, M Gérin, M Goldberg, R Dewar, M Désy, S Campbell, and S Wacholder. 1986. Associations between several sites of cancer and nine organic dusts: Results from an hypothesis-generating case-control study in Montreal, 1979-1983. Am J Epidemiol 123:235-249.

Simonato, L. 1986. Occupational cancer risk in developing countries and priorities for epidemiological research. Presented at International Symposium On Health and Environment in Developing Countries, Haicco.

Smith, TJ. 1987. Exposure asssessment for occupational epidemiology. Am J Ind Med 12:249-268.

Soskolne, CL. 1985. Epidemiological research, interest groups, and the review process. J Publ Health Policy 6(2):173-184.

—. 1989. Epidemiology: Questions of science, ethics, morality and law. Am J Epidemiol 129(1):1-18.

—. 1993. Introduction to misconduct in science and scientific duties. J Expos Anal Environ Epidemiol 3 Suppl. 1:245-251.

Soskolne, CL, D Lilienfeld, and B Black. 1994. Epidemiology in legal proceedings in the United States. In The Identification and Control of Environmental and Occupational Diseases. Advances in Modern Environmental Toxicology: Part 1, edited by MA Mellman and A Upton. Princeton: Princeton Scientific Publishing.

Stellman, SD. 1987. Confounding. Prevent Med 16:165-182.

Suarez-Almazor, ME, CL Soskolne, K Fung, and GS Jhangri. 1992. Empirical assessment of the effect of different summary worklife exposure measures on the estimation of risk in case-referent studies of occupational cancer. Scand J Work Environ Health 18:233-241.

Thrusfield, MV. 1986. Veterinary Epidemiology. London: Butterworth Heinemann.

Trichopoulos, D. 1995. Accomplishments and prospects of epidemiology. In Lectures and Current Topics in Epidemiology. Florence: European Educational Programme in Epidemiology.

Van Damme, K, L Cateleyn, E Heseltine, A Huici, M Sorsa, N van Larebeke, and P Vineis. 1995. Individual susceptibility and prevention of occupational diseases: scientific and ethical issues. J Exp Med 37:91-99.

Vineis, P. 1991. Causality assessment in epidemiology. Theor Med 12:171-181.

Vineis, P. 1992. Uses of biochemical and biological markers in occupational epidemiology. Rev Epidmiol Med Soc Santé Publ 40 Suppl 1: 63-69.

Vineis, P and T Martone. 1995. Genetic-environmental interactions and low-level exposure to carcinogens. Epidemiology 6:455-457.

Vineis, P and L Simonato. 1991. Proportion of lung and bladder cancers in males resulting from occupation: A systematic approach. Arch Environ Health 46:6-15.

Vineis, P and CL Soskolne. 1993. Cancer risk assessment and management: An ethical perspective. J Occup Med 35(9):902-908.

Vineis, P, H Bartsch, N Caporaso, AM Harrington, FF Kadlubar, MT Landi, C Malaveille, PG Shields, P Skipper, G Talaska, and SR Tannenbaum. 1994. Genetically based N-acetyltransferase metabolic polymorphism and low level environmental exposure to carcinogens. Nature 369:154-156.

Vineis, P, K Cantor, C Gonzales, E Lynge, and V Vallyathan. 1995. Occupational cancer in developed and developing countries. Int J Cancer 62:655-660.

Von Volkmann, R. 1874. Ueber Theer-und Russkrebs. Klinische Wochenschrift 11:218.

Walker, AM and M Blettner. 1985. Comparing imperfect measures of exposure. Am J Epidemiol 121:783-790.

Wang, JD. 1991. From conjectures and refutation to the documentation of occupational diseases in Taiwan. Am J Ind Med 20:557-565.

—. 1993. Use of epidemiologic methods in studying diseases caused by toxic chemicals. J Natl Publ Health Assoc 12:326-334.

Wang, JD, WM Li, FC Hu, and KH Fu. 1987. Occupational risk and the development of premalignant skin lesions among paraquat manufacturers. Brit J Ind Med 44:196-200.

Weed, DL. 1986. On the logic of causal inference. Am J Epidemiol 123:965-979.

—. 1988. Causal criteria and popperian refutation. In Causal Inference, edited by KJ Rothman. Chestnut Hill, Mass.: Epidemiology Resources.

Wood, WB and SR Gloyne. 1930. Pulmonary asbestosis. Lancet 1:445-448.

Wyers, H. 1949. Asbestosis. Postgrad Med J 25:631-638.