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Ecological study
   It is not easy to establish links between
    environmental exposures and health outcomes
    using individual level data
    • Problems for obtaining measures of dose levels for
      individuals
    • There is also often the difficulty to deal with long
      latency times between exposure and diagnosis. (eg
      cancer)
   Ecological study designs provide one way of
    avoiding these difficulties and studying the
    effects of environmental exposures on different
    health outcomes.
Definition: observational study with
 group (instead of individual) being unit
 of observation (unit of analysis)
Types:
  • Exploratory study
  • Multiple group comparison study (geographical
    study)
  • Time series study
 The  simplest ecological study
 Observing differences in rates of disease in
  different geographical areas
 No exposures are measured and, generally, no
  formal data analysis is used.
 The objective is to search for spatial patterns
  that might suggest an environmental etiology
  or a special etiologic hypothesis.
•   Ex1: Age-adjusted cancer mortality rates in the US by
    county for the period 1950-69;

•   Difference statistically significant for oral cancer in
    geographic patterns by sex
    - Men: mortality rates >in the urban Northeast
     tobacco smoking and alcohol consumption

    - Women: mortality rates >in the Southeast
     hypothesis: snuff dipping
    • confirmed by a case-control study

    • [Morgenstern H., AJPH, 1982,72,12, 1336-1344]
 Observe  the association between the
  average exposure level and the disease rate
  among several groups.
 Eg:
  • Emile Durkheim, who investigated suicide in
    western Europe during the 19th century.
  • The data on four groups (religion and suicide rate)
    of Prussian provinces between 1883 and 1890
    studied.
  • Result: Protestants were 7½ times as likely to
    commit suicide as were other residents (most of
    whom were Catholic)
Ecological study
 Observe  the relationship between the change in
  the average exposure level (or intervention) and
  the change in the disease rate for a single
  population
 With time trend studies involving a sudden
  change in exposure (e.g: the start of an
  intervention program):
  • compare the slope in the disease trend before and after
   the intervention.
 With
     time trend studies involving a gradual
 change in average exposure level:
  • must compare trends in both variables.
Ecological study
Ecological study
   Frequently used in environmental epidemiology where it is
    difficult to measure exposure at the individual level
   Generally use pre-existing data, which have been collected for
    other purposes and which can be available on large
    populations
    • there are many sources of environmental data, from environmental
      surveillance systems which can be used (air pollution, drinking water
      quality, temperatures…)
   Can also be used for studyng infectious diseases, especially in
    surveillance, in order to detect signals which can be alerts
   Also useful to evaluate the impact of intervention programs or
    policies
   Data on many variables (e.g., behaviors, or medical hx) may
    not be available at the population level, and the results of
    ecologic analyses are subject to certain limitations.
    • unlikely to give reliable and accurate estimates of risk but they can
      be useful for the purposes of formulating hypotheses, that may
      then be examined by other methods.
   Ecological studies look for associations between the
    occurrence of disease and exposure to known or suspected
    causes.
   However, the unit of analysis is not an individual but a
    population / a group of persons
   Disease rates and exposures are measured in each population
    and their relation is examined
   The principle of this study design is
    To identify changes in the frequency of an health event in
      space and/or time
     To relate these changes with environmental factors
 The    2 major objectives of ecological
     studies are:
4)   to generate or to test etiologic hypotheses, in order to
     explain disease occurrence;
5)   to evaluate the impact of intervention programs or
     policies (if we have the knowledge of disease etiology).
   Use of agregated data and not the individual data
   The statistical unit corresponds to a group of persons
    • Levels of exposure are not measured individually ; but use mean
      exposures in the population
    • Health outcome - use the frequency of the disease in the
      statistical unit
   The principle is to look if there is an association between
    • variation of exposure levels and
    • variation of health indicators
 For   example:
  • to look for an association between mean chlorination
    levels in tap water in the district and the incidence
    rate of bladder cancer in different geographical areas
    (geographical study), or;
  • to look for an association between daily levels of air
    pollution and the daily numbers of hospital admissions
    for respiratory diseases (time series study)
Ecological study

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Ecological study

  • 2. It is not easy to establish links between environmental exposures and health outcomes using individual level data • Problems for obtaining measures of dose levels for individuals • There is also often the difficulty to deal with long latency times between exposure and diagnosis. (eg cancer)  Ecological study designs provide one way of avoiding these difficulties and studying the effects of environmental exposures on different health outcomes.
  • 3. Definition: observational study with group (instead of individual) being unit of observation (unit of analysis) Types: • Exploratory study • Multiple group comparison study (geographical study) • Time series study
  • 4.  The simplest ecological study  Observing differences in rates of disease in different geographical areas  No exposures are measured and, generally, no formal data analysis is used.  The objective is to search for spatial patterns that might suggest an environmental etiology or a special etiologic hypothesis.
  • 5. Ex1: Age-adjusted cancer mortality rates in the US by county for the period 1950-69; • Difference statistically significant for oral cancer in geographic patterns by sex - Men: mortality rates >in the urban Northeast  tobacco smoking and alcohol consumption - Women: mortality rates >in the Southeast  hypothesis: snuff dipping • confirmed by a case-control study • [Morgenstern H., AJPH, 1982,72,12, 1336-1344]
  • 6.  Observe the association between the average exposure level and the disease rate among several groups.  Eg: • Emile Durkheim, who investigated suicide in western Europe during the 19th century. • The data on four groups (religion and suicide rate) of Prussian provinces between 1883 and 1890 studied. • Result: Protestants were 7½ times as likely to commit suicide as were other residents (most of whom were Catholic)
  • 8.  Observe the relationship between the change in the average exposure level (or intervention) and the change in the disease rate for a single population  With time trend studies involving a sudden change in exposure (e.g: the start of an intervention program): • compare the slope in the disease trend before and after the intervention.  With time trend studies involving a gradual change in average exposure level: • must compare trends in both variables.
  • 11. Frequently used in environmental epidemiology where it is difficult to measure exposure at the individual level  Generally use pre-existing data, which have been collected for other purposes and which can be available on large populations • there are many sources of environmental data, from environmental surveillance systems which can be used (air pollution, drinking water quality, temperatures…)  Can also be used for studyng infectious diseases, especially in surveillance, in order to detect signals which can be alerts  Also useful to evaluate the impact of intervention programs or policies
  • 12. Data on many variables (e.g., behaviors, or medical hx) may not be available at the population level, and the results of ecologic analyses are subject to certain limitations. • unlikely to give reliable and accurate estimates of risk but they can be useful for the purposes of formulating hypotheses, that may then be examined by other methods.  Ecological studies look for associations between the occurrence of disease and exposure to known or suspected causes.  However, the unit of analysis is not an individual but a population / a group of persons  Disease rates and exposures are measured in each population and their relation is examined
  • 13. The principle of this study design is To identify changes in the frequency of an health event in space and/or time  To relate these changes with environmental factors
  • 14.  The 2 major objectives of ecological studies are: 4) to generate or to test etiologic hypotheses, in order to explain disease occurrence; 5) to evaluate the impact of intervention programs or policies (if we have the knowledge of disease etiology).
  • 15. Use of agregated data and not the individual data  The statistical unit corresponds to a group of persons • Levels of exposure are not measured individually ; but use mean exposures in the population • Health outcome - use the frequency of the disease in the statistical unit  The principle is to look if there is an association between • variation of exposure levels and • variation of health indicators
  • 16.  For example: • to look for an association between mean chlorination levels in tap water in the district and the incidence rate of bladder cancer in different geographical areas (geographical study), or; • to look for an association between daily levels of air pollution and the daily numbers of hospital admissions for respiratory diseases (time series study)