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Bias in casecrossover analyses of environmental time series data

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Title: Bias in casecrossover analyses of environmental time series data


1
Bias in case-crossover analyses of environmental
time series data
  • Paddy Farrington,
  • Heather Whitaker and Mounia Hocine
  • The Open University, UK

2
The message
  • Case-crossover methods are frequently used in
    environmental epidemiology.
  • Some of them are biased, owing to incorrect use
    of the case-control paradigm.
  • This can be fixed by using case series methods.
  • However there is little point in doing so as time
    series methods are more flexible.

3
Environmental time series
  • Data xt on an environmental exposure (eg
    temperature, pollution level) in a given area are
    available at times t 1, 2, , T.
  • Counts of events nt (eg vascular events, asthma
    hospitalizations) are documented at each time
    point.
  • Question is there an association between the
    counts and the exposures?

4
(No Transcript)
5
Case-crossover methods applied to environmental
time series
  • For an event at time t, select a window Wt
    determined by t and containing t (eg times t ?1,
    t and t 1).
  • Treat the exposures in Wt as a matched
    case-control set, xt being the case exposure.
  • Do a conditional logistic regression as if this
    were a matched case-control study.

6
t 1 t t 1
Control Case Control
Exposures xt-1 xt
xt1 Count nt
Likelihood contribution of events at t
7
Overlap bias
  • There is a large industry on how to choose the
    referent window Wt.
  • It has been shown that this method of analysis
    sometimes produces biased estimates.
  • This bias has been called overlap bias.
  • But up till now the source of the bias has not
    been clear.

8
Exchangeability of the exposure distribution
within matched sets
  • Matched case-control studies require the
    distribution of exposures in each matched set to
    be exchangeable
  • given the unordered set of exposures E X0, X1,
    , XM), for any permutation ? of the indices,
  • P(X0,,XME) P(X?(0) ,,X?(M)E)

9
The (full) case-control likelihood
  • Consider a matched set of size M 1 (one case
    and M controls). For each label r 0, 1, , M let

The likelihood contribution for this matched set
is then
provided that exposures are exchangeable.
10
Exchangeability of environmental exposures?
  • For environmental time series, sampling of the
    reference windows Wt determines the exposures.
  • Available orderings of exposures across reference
    windows are determined by the time series (and
    form a finite population).
  • The exchangeability condition may not be met if
    not this results in overlap bias.

11
Binary exposures - Example
  • Consider the exposure series 01011 and case
    positions 2, 3 and 4.
  • Exposure vectors
  • Case position 2 (0,1,0)
  • Case position 3 (1,0,1)
  • Case position 4 (0,1,1)
  • Exposures are not exchangeable e.g. the vectors
    (1,0,0), (0,0,1) do not appear.
  • This will result in overlap bias.

12
Case series methods
  • Overlap bias can be avoided by dropping the
    case-control paradigm.
  • Instead, partition the time series into
    non-overlapping windows Wt and treat event times
    within each window as random.
  • This is a cohort approach, which is not subject
    to overlap bias.
  • It has recently been extended to allow for the
    residual effects of seasonality.

13
Is this approach worth rescuing?
  • The key assumptions of the method when applied to
    such data are
  • The counts are Poisson, and
  • There is no underlying time trend in event rates
    within each window Wt.
  • Failure of either assumption invalidates the
    method.
  • Time series methods make no such assumptions.

14
Example Relative risk of RSV per 10oC
15
Conclusions
  • For modelling environmental time series, the
    case-crossover method is biased as exposures are
    usually not exchangeable.
  • Case series methods are unbiased.
  • They are equivalent to Poisson time series models
    with piecewise constant rate.
  • Time series regression models are far more
    flexible and should be preferred.
  • Whitaker et al, Environmetrics 18 157 (2007)
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