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Policy-Relevant Proportions for Direct Effects

VanderWeele, Tyler J.


The letter suggested that the formula for the proportion eliminated {RR(TE) − RR(CDE(m))} / {RR(TE)−1} (calculated from the risk-ratio model) was expressed on a risk-difference scale; however, it is in fact expressed on a scale of excess relative risk (i.e., relative risk minus one) and the two do not coincide in this context. For further discussion, refer to the following letter in this issue: Suzuki E, Evans D, Chaix B. On the 'proportion eliminated' for risk differences versus excess relative risks [letter]. Epidemiology. 2014;25:308.

Epidemiology. 25(2):320, March 2014.

doi: 10.1097/EDE.0b013e3182781410

Departments of Epidemiology and Biostatistics, Harvard School of Public Health, Boston, MA,

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To the Editor:

Contemporary concepts from the causal inference literature have provided definitions of direct and indirect effects that can be used in models with interactions and nonlinearities.1,2 So-called controlled direct effects (CDEs) assess the effect of the exposure on an outcome with the intermediate fixed to a particular level. So-called natural direct effects (NDEs) and natural indirect effects (NIEs) allow for the decomposition of a total effect (TE) into direct and indirect effect components. Methods are now available to estimate these effects when they are identified.3–5 When both direct and indirect effects are employed, a measure of the “proportion mediated” (PM) is sometimes calculated as the ratio of the NIE to the TE (eg, PM = NIE/TE). This measure in some sense captures how important the pathway through the intermediate is in explaining the actual operation of the effect of the exposure on the outcome. It measures what would happen to the effect of the exposure on the outcome if we were to somehow disable the pathway from the exposure to the intermediate.2,6

The use of natural direct and indirect effects is sometimes criticized because (1) they require very strong assumptions for identification2,6,7 and (2) they do not in general correspond to any particular intervention that we could actually carry out (this is because they require, for each person, fixing the mediator to the counterfactual level the person would have had in the absence of exposure).6,7 Since such effect estimates do not correspond to actual interventions we could carry out in practice, they are of limited interest from a policy perspective.6–8

An alternative proportion measure may be of more interest in policy settings. The controlled direct effect fixing the intermediate to level M = m, CDE(m), captures the effect of the exposure on the outcome if the intermediate were set, possibly contrary to fact, to level m. This is an intervention we might hope to be able to carry out in practice. We might hope that by intervening on the intermediate we could block a substantial part of the effect of the exposure on the outcome. A proportion measure that could then be used, and that would be of policy relevance, would be the proportion of the effect of the exposure on the outcome that could be eliminated by intervening to set the intermediate to some fixed level m.1 This would be (TE – CDE[m])/TE. If this proportion eliminated (PE) were large, we might try to implement policies to intervene on the intermediate. The PM essentially captures what would happen to the effect of the exposure if we were to somehow disable the pathway from the exposure to the intermediate (leaving it to its natural value); in contrast, the PE measure captures what would happen to the effect of the exposure on the outcome if we were to fix the intermediate to the same fixed value M = m for all persons. The proportion eliminated can also be calculated if a risk ratio scale (or odds ratio scale with a rare outcome) is used to estimate the effects. In this case, with a total effect risk ratio of RR(TE) and a controlled direct effect risk ratio of RR(CDE(m)), then using these risk ratios, one could calculate the proportion eliminated on a risk difference scale by using the formula {RR(TE) − RR(CDE(m))}/{RR(TE) − 1}.

Importantly, the PE measure will not always equal the PM. Suppose that the exposure and the intermediate interacted but that the exposure had no effect on changing the intermediate itself. In this case the indirect effect of the exposure on the outcome through the intermediate would be 0 (because the exposure does not change the intermediate) and we would have a PM of NIE/TE = 0/TE = 0%. However, if, with interaction, the effect of the exposure was large with the intermediate but small without the intermediate, then the PE by fixing the intermediate to 0 might be substantial. If we were to fix the intermediate to 0 for everyone, the exposure may not have much of an effect on the outcome (ie, CDE[m = 0] might be quite small), and the PE = (TE–CDE[m = 0])/TE might be close to 100%. In the extreme case in which there is a pure interaction (so that the exposure has no effect on the outcome unless the intermediate is present) but exposure has no effect on the intermediate itself, then the PM is 0% while the PE by fixing m = 0 is 100%.

More generally, the PM measure (PM = NIE/TE) and the PE measure (PE = [TE–CDE{m}]/TE) may differ because, in the presence of an interaction between the exposure and the intermediate, we may have a different PE measure for every value of m.1,9 Because the TE decomposes into a natural direct effect and NIE (TE = NIE+NDE), we can re-express the PM as PM = [TE–NDE]/TE. In the technical language of the causal inference literature, the PE and the PM may differ because the controlled direct effect may not equal the natural direct effect; the natural direct effect essentially averages over the various CDEs.2 The two measures will coincide when there is no interaction between the exposure and the intermediate (either at the individual level3 or at the expected population level under further assumptions).7

A biomedical example where these two measures do diverge is the effects of chromosome 15q25 genetic variants on lung cancer, with cigarettes smoked per day as an intermediate.10 Each variant allele on 15q25 increases the risk of lung cancer by about 1.3-fold; however, a small proportion (perhaps 5%–15%) of this effect is mediated by increasing cigarettes per day.10 Each variant allele increases cigarettes per day by about 1, which is not enough to explain the association with lung cancer. However, there is strong interaction between these variants and cigarettes per day in their effects on lung cancer and there may, in fact, be a “pure” interaction such that the variants have no effect on lung cancer for those who do not smoke.10 The variants may operate by increasing the nicotine and toxins extracted per cigarettes smoked. In this case, the controlled direct effect if we were able to fix cigarettes per day to 0 for everyone would be CDE(m = 0) = 0, and thus the proportion of the effect eliminated would be PE = (TE–CDE[m = 0])/TE = (TE–0)/TE = 100%. By eliminating smoking, we eliminate all of the effect of the variants. The PM (by cigarettes per day) is small because the variants do not increase the number of cigarettes per day substantially; however, the PE by fixing cigarettes per day to 0 is large because the variants do not seem to affect lung cancer without smoking.

The two measures, PE and PM, have differing interpretations. The PE is in general the more relevant policy measure. It captures how much of the effect of the exposure on the outcome we could eliminate by intervening on the intermediate. The PM captures how much of the effect of the exposure on the outcome is due to the effect of the exposure on the intermediate. It gives insight into the role of different pathways, but not necessarily on what would happen if we were to intervene on particular intermediates. The PE measure is attractive because it describes the estimated effect of actual policy intervention, and because it requires only the estimation of controlled direct effects, which can be identified in a broader range of circumstances than natural direct and indirect effects.11,12 If effect decomposition and evaluation of the operation of various pathways are of interest, natural direct and indirect effects and the PM measure may still be of interest. But for policy purposes, the PE is arguably more relevant.

Tyler J. VanderWeele

Departments of Epidemiology and Biostatistics

Harvard School of Public Health

Boston, MA

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