Marie Abele-Bind’s contribution to the Discussion of ‘Methods for estimating the exposure–response curve to inform the new safety standards for fine particulate matter’ by Cork et al.

Methods for Estimating the Exposure-Response Curve to Inform the New Safety Standards for Fine Particulate Matter' by Cork et al.Although the field of causal inference has primarily focused on dichotomous treatment exposures, this interesting article departs from this simple setting and attempts to assess causal inference methods that estimate the effects of a continuous treatment, namely non-randomized air pollution.Classical work in experimental design has already provided methods to assess the effect of a randomized treatment with many levels, and we believe that transporting successful insights from experimental design is essential, especially in complex settings such as those being considered by the current effort.We also believe that it is crucial to embed any causal observational study into a plausible hypothetical randomized experiment, a point that has been emphasized in recent literature (Bind and Rubin, 2019).To achieve this, we need to first define the treatment and its timing, and then try to convince readers that the underlying assumptions, especially the unconfoundedness assumption, are plausible.For instance, if complete randomization is being assumed, researchers should present extensive diagnostics for covariate balance along the full distribution of the continuous treatment, which is tricky to implement.In the context of environmental exposures, days with high vs. low air pollution concentrations generally differ along many dimensions.Ideally, to study the effect of PM 2.5 concentrations, one needs to contrast outcomes on "similar" days with very low, low, medium, high, and very high PM 2.5 concentrations, i.e., outcomes on days with similar levels of all other pollutants (e.g., NO 2 , O 3 ) and similar meteorological conditions (e.g., temperature, relative humidity).All days of very low, low, medium, high, and very high PM 2.5 concentrations also need to be matched on day of the week, month, and year.The problem therefore requires not only extensive datasets, but also multiple measurements various pollution and meteorological conditions across days of the week, months, and years.

Authors

Institutions

Publication Details

Journal
Journal of the Royal Statistical Society Series A (Statistics in Society)
Published
2025-04-25
DOI
https://doi.org/10.1093/jrsssa/qnaf049
Primary Topic
Air Quality and Health Impacts
Type
article
Field-Weighted Citation Impact
0.00
Controls
|||
ALL TIME
JAN
FEB
MAR
APR
MAY
JUN
JUL
AUG
SEP
OCT
article

Marie Abele-Bind’s contribution to the Discussion of ‘Methods for estimating the exposure–response curve to inform the new safety standards for fine particulate matter’ by Cork et al.

Marie‐Abèle Bind
Journal of the Royal Statistical Society Series A (Statistics in Society)
Air Quality and Health Impacts
article

Marie Abele-Bind’s contribution to the Discussion of ‘Methods for estimating the exposure–response curve to inform the new safety standards for fine particulate matter’ by Cork et al.

Marie‐Abèle Bind
article en

Abstract

Methods for Estimating the Exposure-Response Curve to Inform the New Safety Standards for Fine Particulate Matter' by Cork et al.Although the field of causal inference has primarily focused on dichotomous treatment exposures, this interesting article departs from this simple setting and attempts to assess causal inference methods that estimate the effects of a continuous treatment, namely non-randomized air pollution.Classical work in experimental design has already provided methods to assess the effect of a randomized treatment with many levels, and we believe that transporting successful insights from experimental design is essential, especially in complex settings such as those being considered by the current effort.We also believe that it is crucial to embed any causal observational study into a plausible hypothetical randomized experiment, a point that has been emphasized in recent literature (Bind and Rubin, 2019).To achieve this, we need to first define the treatment and its timing, and then try to convince readers that the underlying assumptions, especially the unconfoundedness assumption, are plausible.For instance, if complete randomization is being assumed, researchers should present extensive diagnostics for covariate balance along the full distribution of the continuous treatment, which is tricky to implement.In the context of environmental exposures, days with high vs. low air pollution concentrations generally differ along many dimensions.Ideally, to study the effect of PM 2.5 concentrations, one needs to contrast outcomes on "similar" days with very low, low, medium, high, and very high PM 2.5 concentrations, i.e., outcomes on days with similar levels of all other pollutants (e.g., NO 2 , O 3 ) and similar meteorological conditions (e.g., temperature, relative humidity).All days of very low, low, medium, high, and very high PM 2.5 concentrations also need to be matched on day of the week, month, and year.The problem therefore requires not only extensive datasets, but also multiple measurements various pollution and meteorological conditions across days of the week, months, and years.

Journal of the Royal Statistical Society Series A (Statistics in Society)Vol. 188(4)
Harvard University (US), Massachusetts General Hospital (US)
Openalex Percentile: Top 90%
Air Quality and Health Impacts
AI Navigator

Ask Laika to Summarize, Analyze, and Connect papers live on the map.

Summarize Papers & Methodologies

Extract key findings, datasets, and comparative methods across publications.

Benchmark Rankings & Visual Analytics

Rank top research institutions, authors, funders, topics, and journals by Field-Weighted Citation Impact (FWCI) and paper volume with instant charts.

Connect Distant Disciplines

Bridge topological clusters on the map to find hidden collaborative intersections.