Comparative evaluation of Spatio-Temporal Exposure Assessment Methods for estimating the health effects of air pollution (STEAM)

Lead Research Organisation: King's College London
Department Name: Health and Social Care Research

Abstract

Background: Epidemiological studies have linked long- and short-term outdoor air pollution exposures to increased risks of death and morbidity. Cohort studies evaluate the health effects of long-term exposure by exploiting spatial heterogeneity in annual air pollution concentrations whereas time-series studies evaluate acute effects exploiting temporal variability in pollution concentrations. The extent to which the adverse health effects reported by these different study designs overlap has important implications for health impact assessment and policy development and to date this has not been investigated outside the US. In the past, both study designs have been limited by the availability of monitored pollution data but the development of dispersion and land use regression models have improved exposure assessment in cohort studies and enabled the investigation of a broader range of pollutants. The extension of these models to provide spatially resolved daily estimates of pollutant concentrations will enable an integrated assessment of health effects arising from both long- and short-term exposures to a wide range of pollutants and with applicability to locations with sparse or no monitoring.
Objectives: 1.To develop, validate and compare dispersion, land use regression and satellite data based pollution models for London at both fine spatial (postcode level) and temporal (daily) scales. 2. To assess the performance of these methods and their combinations in estimating the health effects of long and short-term exposures to air pollutants. 3. To use the optimum integrated exposure method to estimate the relative importance of the effects of long-and short-term exposure for selected health outcomes. To achieve these objectives the project will use the expertise developed within the MRC-PHE Centre for Environment and Health and will need to draw upon the expertise of pioneering international groups (in the U.S. & Greece) in modelling, simulation studies and time series analyses.
Methods: Models will be developed for particulate and gaseous pollutants and validated using measured concentrations from the London Air Quality Network. Their applicability to locations with sparse or no monitoring will be assessed using sequentially smaller parts of the available exposure information. An extensive simulation study, in which the "true" effect is known, will investigate the implications of using each exposure method on the health effect estimation (precision and bias).To enable proof of concept for the simultaneous estimation of long- and short-term effects on various health outcomes, the analysis of selected endpoints including GP consultations, hospital admissions and mortality data will be applied.
Innovation aspects:
1. Application of air pollution modelling approaches at a fine time and spatial resolution
2. Integration of the different exposure assessment methods for optimizing their performance.
3. Use of simulation methods to evaluate simultaneously the performance of models in assessing the effects of long- and short-term exposure to particulate and gaseous pollutants.
4. Simultaneous estimation of health effects of long- and short-term exposure to air pollution in existing large health data sets to enable a comparison of their relative importance.
Policy implications:
1. Information on the advantages and disadvantages of each exposure model will inform the optimum extent and density of monitoring systems and other inputs to local models.
2. The simultaneous estimation of the effects of short and long-term exposures will provide a rationale for the balance between emergency short-term action and long-term pollution management interventions.
3. Informing the development of modelling in areas of Europe and the World where monitoring is not so dense.
4. Informing health studies about the comparative importance of short vs long-term effects in areas of Europe and the World where health outcome data bases are limited

Technical Summary

The aim of this study is to develop, validate and compare three integrated air pollution exposure assessment methods for estimating simultaneously the health effects of short and long-term exposure to outdoor air pollutants. The dispersion model will use CMAQ-urban which couples the USEPA regional model, CMAQ and the Atmospheric Dispersion Modelling System roads model incorporating emissions data. This combined model will provide hourly predictions at 20x20m spatial resolution for Greater London for PM10, PM2.5, NO2 and O3. Spatio-temporal LUR models for PM10, PM2.5, NO2 and O3 will use a semiparametric approach with covariates that vary primarily in space (e.g. distance to major road, traffic counts) and covariates that vary primarily in time (e.g. meteorology) and a bivariate smooth thin plate function for the geographical co-ordinates. New methods, similar to Chudnovsky 2014, will use a hybrid model, with AOD, land use, and meteorological data to estimate daily PM2.5. Spatial predictors will include population and traffic density, land use (Landsat) and emissions as well as time varying predictors (e.g. vegetative index from MODIS, meteorology). Each method will be evaluated using simulation techniques developed from previous work. We propose to construct scenarios where 'true' temporally and spatially resolved air pollution data are associated with health outcomes by a priori defined concentration response functions (such as those proposed by W.H.O. HRAPIE project). Model performance will be assessed under a variety of scenarios using a number of parameters including bias, statistical power and coverage intervals. Finally the model predictions will be used in conjunction with selected health outcomes to demonstrate proof of concept in estimating simultaneous associations between health outcomes and long- and short-term exposure to air pollution.

Planned Impact

National and international governmental agencies responsible for air pollution policy development and monitoring and for health impact assessment will be the main beneficiaries of this research. In the UK, Defra, the Department of Health, Public Health England and Local Authorities will be able to utilise the methodologies derived from the project to plan the deployment of air pollution monitoring sites, assess health impacts and determine local and national air pollution mitigation strategies in both the long- and short-term. Similarly, the WHO, the European Environment Agency and other devolved government and government agencies or regulators can also utilise the methodology with particular application in locations where less comprehensive monitoring networks exist. Examples of health impact assessment exercises at national and international levels include exercises here in the UK [COMEAP report] and in the EC [HRAPIE]. The central topic of our project is better estimation of a population exposure to ambient air pollution and the subsequent impact on human health. We therefore anticipate that the general public, both here in the UK as well as abroad, will benefit from better pollution management policies and a greater awareness of the links between air pollutant exposure and health. The academic community (epidemiology/Public Health, and air pollution science) will also benefit especially from the methodological developments.

How will they benefit from this research?
Health effects of acute and chronic exposure to air pollution have usually been studied separately and their results used for separate health impact assessment exercises. In a number of cases the lack of evidence for health effects of long term exposure from cohort studies has been supplemented by the evidence from short-term exposure (time series) studies. The methods used to derive exposure measures in cohort studies often vary and make synthesis difficult. Transferability of results from the regions of the world where studies have been conducted to less well studied locations is also problematical. This project will attempt to address many of these difficulties by 1) assessing the advantages and disadvantages of each exposure model to inform the optimum extent and density of monitoring systems and other inputs to local models required in any region of the world; 2) inform the development of modelling in areas where monitoring networks are sparse to facilitate exposure assessment; 3) facilitate the simultaneous estimation of the effects of long- and short-term exposures and provide a rationale for the balance between emergency short-term action and long-term pollution management interventions applicable to local and national needs; and 4) inform health studies about the comparative importance of short vs long-term effects in areas of Europe and the World where health outcome data bases are limited. The novel methods developed in this project will provide the tools policy analysts require to undertake more informed policy formulation and assessment exercises providing relevant information to local, national and international agencies responsible for air pollution policy.

Publications

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Butland BK (2019) Measurement error in a multi-level analysis of air pollution and health: a simulation study. in Environmental health : a global access science source

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Dimakopoulou K (2022) Development and Evaluation of Spatio-Temporal Air Pollution Exposure Models and Their Combinations in the Greater London Area, UK. in International journal of environmental research and public health

 
Description Investigating the consequences of measurement error of gradually more sophisticated long-term personal exposure models in assessing health effects: The London Study
Amount $800,000 (USD)
Funding ID RFA 19-1 
Organisation Health Effects Institute (HEI) 
Sector Charity/Non Profit
Country United States
Start 07/2020 
End 06/2023
 
Title Development of spatio-temporal Models for NO2, NOx, PM10, PM2.5 and O3 in London, UK, within the STEAM project: Combination of different exposure assessment methods. 
Description Air pollution monitoring data We useddaily measurements (µg/m3) of nitrogen dioxide (NO2), nitrogen oxides (NOx) particulate matter with diameter less than 10µm (PM10), particulate matter with diameter less than 2.5µm (PM2.5) and ozone (O3)for 2009 through 2013 from the fixed air pollution monitoring sites run by theLondon Air Quality Network, in the Greater London Area. We calculated the 24h average concentrations of NO2, PM10, PM2.5 and the maximum 8-hour average O3 concentration to represent daily exposure. We used all available monitoring sites in the study area (NO2/NOx: 130 sites; PM10/PM2.5: 115 sites/33 sites & predicted values for 71 site locations; O3:62 sites). Land use data We obtained road geography and information on road traffic flows from the Department of Transport (https://www.dft.gov.uk/traffic-counts/). Land use variables were derived from Land Cover Map Great Britain 2007. In addition, we used building and population density data for 2011 (census data). GIS analyses were conducted to extract 95 potential predictor variables in total.These variables are traffic-related, characterize land use and population density in different buffers around the fixed air pollution monitoring sites. The geographical coordinates of each monitoring site were geocoded. The buffer zones used for traffic-related variables were: 50, 100, 300, 500 and 1000 m and were selected to take account of known dispersion patterns. Total traffic load on a major road was calculated as length of the road segment multiplied by traffic intensity and divided by road segment for all roads within each buffer zone. We also calculated the length of the major road segments in different buffer zones around the fixed monitoring sites, traffic intensity on the nearest major road to the fixed monitoring site and inverse distance to the nearest major road to the fixed monitoring site. The buffer zones used for land use were 100, 300, 500, 1000 and 5000 m to characterize land use (transportation, industry, woodland, grassland, freshwater, urban and suburban areas). Areas of different land cover usewere calculated in m2, within each buffer zone. Temporal variables We used meteorological data from 53 fixed meteorological site located at the study area for the years 2009 - 2013. We extracted over all available sites, mean daily temperature (oC), relative humidity (%), wind speed (m/s), barometric pressure (mb), radiation (Wh/m2/day), cloud coverage (oktas) and wind direction (oN). Moreover, we considered indicator variables for different years (reference category was 2009), day of the week (reference category: Sunday), a variable for day count, accounting for trends within each year (1 to 366). Spatio-temporal LUR model development We developed spatio-temporal semiparametric models. All continuous covariates were entered in the model alternatively as a linear and as a smoothed term, except geographical location for which a bivariate smooth function was used. For each of the potential predictors, we included in the final model the term (linear or smoothed) that provided the better model fit in terms of Restricted Maximum Likelihood (REML). The final set of explanatory variables was selected based on the adjusted-R2 obtained from several alternative models where all the temporal and spatial covariates were tested as above.All covariates were allowed to enter the model only if they were statistically significant (p-value less than 5%) and if their regression coefficients conformed to the pre-specified direction of effect. The final spatio-temporal LUR model for NO2 accounted for temperature (penalized splines with 3 degrees of freedom - df), wind direction (penalized splines with 3 degrees of freedom - df)and wind speed, relative humidity, for the day of the year (penalized splines with 6 degrees of freedom - df)and for different years. a smooth bivariate function (thin plate spline) of the geographical location of the fixed monitoring sites for NO2to account for the residual spatial correlation.Significant spatial predictors weretotal traffic load in a buffer of 50 meters around each monitoring site, inverse distance of the monitoring sites to the nearest major road (included as a non-linear term), urban area land use in a buffer of 300 meters around each monitoring siteand geographical location of the monitoring sites. Appropriate degrees of freedom were estimated via REML. The developed model for NOx included the same set of temporal and spatial covariates as the model for NO2, plus thetotal length of major roads in a buffer of 100 meters around each monitoring site. The final model for PM10 accounted for temperature, wind direction and speed, barometric pressure, for the day of the year and for different years. Temperature, wind direction, barometric pressure and daycount were included as non-linear terms (using penalized splines with 3 / 6 degrees of freedom). Significant spatial predictors weretotal traffic load in a buffer of 100 meters around each monitoring site, inverse distance of the monitoring sites to the nearest major road (included as a non-linear term) and a smooth bivariate function (thin plate spline) of the geographical location of the fixed monitoring sites. The final model for PM2.5 included the same set of temporal covariates as the model for PM10and in addition relative humidity (as a linear term). While, regarding variables on the spatial scale, included was the total length of major roads in a buffer of 300m around each monitoring site, the inverse distance of monitoring sites to the nearest major road (as a non-linear term) and the geographical location of monitoring sites. The final model for O3 accounted for temperature, wind direction and speed, relative humidity, cloud coverage, for the day of the year and for different years. Temperature, wind direction and daycount were included as non-linear terms (using penalized splines with 3 / 6degrees of freedom). Significant spatial covariates weretotal traffic load in a buffer of 100 meters around each monitoring site, inverse distance of the monitoring sites to the nearest major road (a non-linear term)and geographical location of the monitoring sites. Our final models did not include any terms for space-time interactions, since it did not add to the value of the adjusted-R2. Chemical Transport Modeling (CTM) Data After developing the spatio-temporal LUR models as described above, we incorporated a daily predicted value for NO2, NOx, PM10, PM2.5 and O3 estimated from the CMAQ-urban model at fixed site air pollution monitoring locations. We refer to these models as the combined LUR-dispersion models. Aerosol optical depth (AOD) data Furthermore, a spatio-temporal model for estimating daily PM2.5 concentrations over the study area was developed using aerosol optical depth (AOD) data. Model combination Following, a generalized additive model (GAM) was applied to combine predicted concentrations of NO2, NOx, PM10, PM2.5 and O3 at fixed site monitoring locations from 1) developed spatio-temporal LUR models and 2) CMAQ-urban model. Moreover, a GAM was applied to combine predicted PM2.5concentrations from 1) developed spatio-temporal LUR models, 2) CMAQ-urban model and 3) AOD model. The model is of the following form: We refer to these models as the combined GAM models. Model validation We investigated the validity of the spatio-temporal LUR modelsand the combined models (LUR-dispersion and GAM) using 10-fold cross validation (CV). We randomly selected 90% of the sites (training set), fit the model (on the train data) and then used the remaining 10% (validation set) of the sites for model evaluation (get the predictions for the validation set, from the model just fit on the train data). This was repeated ten times, such that each site was in a test set once. The statistical analysis was conducted using the R statistical software (version 2.10.1; R Development Core Team 2009) and the R library "SemiPar" version 1.0-2. Model fit The adjusted R2 values and the CV adjusted R2 values of the final spatio-temporal LUR models ranged from 0.61 to 0.72 and from 0.57 to 0.74 respectively, the combined LUR-dispersion models R2 and CV adjusted R2 ranged from 0.79 to 0.84 and 0.75 to 0.81 respectively and the combined GAM models R2 and CV adjusted R2 from 0.72 to 0.83 and 0.71 to 0.82 respectively 
Type Of Material Improvements to research infrastructure 
Year Produced 2019 
Provided To Others? No  
Impact This models can be used by other researchers for better exposure to air pollutants estimation in London within the context of health studies, such as cohort studies. The methodology can be applied to develop similar combined methods in other locations. At a later stage we will make the estimates available upon request to other researchers and advertise this on the relevant sites 
 
Title New updated application of the CMAQ-urban dispersion model for predicting air pollution concentrations 
Description A new application of the CMAQ-urban model was developed for the purposes of STEAM, specifically for predictions at specific points and input in the simulation study. More specifically, to model air quality we used the VBS version 5.0.2 CMAQ (Community Multi-scale Air Quality) model (1), coupled to ADMS (2), a model we describe as CMAQ-Urban (3), which outputs hourly air pollution concentrations across Europe every 50km, the UK every 10km, and in London, initially every 2km and every 20m close to roads. The CMAQ-urban outputs were: NOX, NO2, O3, PM10 and PM2.5. Bias in the 2x2km CMAQ PM2.5 and PM10¬ hourly output was corrected using a sample of background sites before the local scale dispersion modelling stage. The discrepancies between the model output and the measurements at a random sample of 50% of background sites in the case of PM10¬, and 5 sites in the case of PM2.5, was interpolated onto the 2x2km grid to create a correction surface. This interpolation was done using two iterations of a multilevel B-spline algorithm (4), which normally takes around eight iterations to interpolate points exactly, so that the resultant error surface provided smoothly varying bias correction across the domain, rather than fixing the model output to the measurements. references 1. Byun DW, Ching JKS., 1999. Science Algorithms of the EPA Models-3 Community Multiscale Air Qualty (CMAQ) Modelling System. U.S. Environmental Protection Agency, Office of Research and Development. EPA/600/R-99/030. 2. CERC, ADMS roads v4 User Guide http://www.cerc.co.uk/environmental-software/assets/data/doc_userguides/CERC_ADMS-Roads4.0_User_Guide.pdf. Accessed Dec 2016. 3. Beevers S D, Kitwiroon N, Williams M L, and Carslaw, D C, One way coupling of CMAQ and a road source dispersion model for fine scale air pollution predictions, Atmospheric Environment, 2012; 59: 47-58 4. Lee S, Wolberg G, and Shin S, Scattered data interpolation with multilevel B-splines, IEEE Transactions on Visualization and Computer Graphics, 1997, 3: 228-244, doi: 10.1109/2945.620490. 
Type Of Material Improvements to research infrastructure 
Year Produced 2018 
Provided To Others? No  
Impact This model application will be published and used in other epidemiological analyses also to be published. 
 
Title Air pollution and meteorological data 2004-2013 
Description We have recorded all available data on daily temperature, relative humidity, wind speed and direction from fixed sites within the London area, for the period 2004-2013. For the same period we have recorded daily data for all available pollutants including PM10, PM2.5, NO2, NOx and ozone. The data base has been checked and corrected for errors. 
Type Of Material Database/Collection of data 
Year Produced 2017 
Provided To Others? Yes  
Impact The data base has been checked for data consistency and may be made available upon request. 
 
Title Enhancement of the PM2.5 measurements data base for London 2004-2013 with modelling 
Description We have implemented a model to fill in the PM2.5 data base predicting the concentrations by modeling using meteorological variables and other pollutants as predictors of PM2.5 daily levels.We have modelled the 2004-08 and 2009-13 periods separately. The data base includes 100,658 PM2.5 predicted estimates in addition to 19,505 available measurements for 2004-08 and 85,089 PM2.5 predicted estimates in addition to 40,435 available measurements for 2009-13. For this model we have used both reference and non-reference monitors and we are now investigating the possibility of using a correction factor to correct the non-reference measurements. The PM2.5 data base containing predicted PM2.5 values will form a separate data base available to all researchers upon request, when it will be finalized. 
Type Of Material Database/Collection of data 
Year Produced 2017 
Provided To Others? No  
Impact For several epidemiological studies of air pollution health effects a larger measurement data base is required to provide adequate exposure estimation. In London the number of monitors is large for most pollutants but this is not the case with PM2.5 measurements and especially those using reference methods. Thus the usefulness of this data base is that it will provide an enhanced data set of "estimated measurements" that may be used. 
 
Title Land Use Regression (LUR) Database for the London area 
Description For the Work Package A.3.Spatio-temporal LUR modelling with daily predictions We have collected all spatial data required to develop the spatio-temporal LUR models for air pollutants in the greater area of London, in order to estimate daily ambient air pollution concentrations for any point in space for the study area and time period of interest (2004-2013). Subsequently, we will use the estimated concentrations for assessing either short- or long-term effects of air pollution, in health effects analyses. We have collected information on the: 1. Geographical coordinates (latitude, longitude) of each air pollution monitoring site & meteorological monitoring station 2. Digital cartographical data for the study area. Attributes including LSOA polygons of the complete study area. 3. Digital road network for the complete study area with linked traffic intensity data to the complete road network (Meridian dataset). 4. Land use/cover data for the complete study area (OS Mastermap dataset) 5. Building density data (Mastermap/LIDAR dataset) GIS analyses is being conducted to derive the values for the potential predictor variables for the coordinates of the air pollution monitoring sites, in order to be taking into account in the spatio-temporal LUR modeling development procedure. Up to now, we have derived land use/cover variables for the monitoring sites located in the "small" study area, thus all sites located in LSOAs within or intersecting with the M25 motorway. These variables are part of the final spatio-temporal LUR database, which once complete, will incorporate the following information, over the same geographical study area and timescale (daily values for the years 2004-2013): 1. the daily air pollution measurement data 2. spatial data (all GIS potential predictor variables for the coordinates of each air pollution monitoring site) 3. temporal daily data 4. descriptive data This dataset will be used to develop the spatio-temporal LUR models for NOx, NO2, PM10, PM2.5 and O3 concentrations in the greater area of London. 
Type Of Material Computer model/algorithm 
Provided To Others? No  
Impact This data base will provide input for modelling the spatio temporal distribution of pollutants in the London area for the period 2009-2013. The data for 2004 to 2008 will be used as comparison data. 
 
Description King's College and Imperal College for STEAM 
Organisation Imperial College London
Department Imperial Clinical Trials Unit (ICTU)
Country United Kingdom 
Sector Academic/University 
PI Contribution King's has provided data for pollutants and meteorological variables and is implementing one exposure model.
Collaborator Contribution Imperial provided access to Land Use variables.
Impact The land use variables were managed with a Geographical information system to produce variables used as input for various pollution exposure models
Start Year 2016
 
Description King's College and St George's for STEAM 
Organisation St George's University of London
Country United Kingdom 
Sector Academic/University 
PI Contribution We have prepared the data sets and contribute to the exposure modelling.
Collaborator Contribution St George's are preparing the simulation study and will later compile a health outcome data set based on HES and ONS data
Impact Data sets have been prepared for use. The collaboration is multi-disciplinary between epidemiologists, statisticians and exposure scientists.
Start Year 2016
 
Description King's College and University of Athens for STEAM 
Organisation National and Kapodistrian University of Athens
Country Greece 
Sector Academic/University 
PI Contribution The collaboration has been described in the contract of STEAM. We, from King's, provided data bases and are implementing one exposure model during the reporting period.
Collaborator Contribution The University of Athens are working on the calculation of variables from the Geographical Information System and implementing the Land Use Exposure modelling.
Impact So far data bases have been prepared and shared, containing measurements for air pollutants and meteorological variables for the London area.
Start Year 2016
 
Description First meeting of researchers and stakeholders 
Form Of Engagement Activity A formal working group, expert panel or dialogue
Part Of Official Scheme? No
Geographic Reach Regional
Primary Audience Policymakers/politicians
Results and Impact We had a joint meeting of study participants from the U.K. (King's College, Imperial College and St George's), a U.S. Harvard University professor, and colleagues from the University of Athens Greece and members of Public health England and the Department for Environment, Food and Rural Affairs (DEFRA). The participants commented and made suggestions on the project plan for the next 2 and a half years which were very important for our future work.
Year(s) Of Engagement Activity 2016
 
Description Presentation of the STEAM project 
Form Of Engagement Activity A talk or presentation
Part Of Official Scheme? No
Geographic Reach Regional
Primary Audience Other audiences
Results and Impact I presented the STEAM project, its objectives, completed activities and project plans to the Annual International Scientific Advisory Board Meeting of the MRC-PHE Centre for Environment and Health on June 2, 2016.
Year(s) Of Engagement Activity 2016
 
Description Presentation of the STEAM project progress 
Form Of Engagement Activity A talk or presentation
Part Of Official Scheme? No
Geographic Reach International
Primary Audience Professional Practitioners
Results and Impact This was a poster presentation at the "Big Data, Small Area Symposium" organized by Imperial College, November 14-15 in London
Year(s) Of Engagement Activity 2017
 
Description Second meeting of stakeholders and researhers 
Form Of Engagement Activity A formal working group, expert panel or dialogue
Part Of Official Scheme? No
Geographic Reach International
Primary Audience Professional Practitioners
Results and Impact This was a planned meeting for reporting and discussing the project's progress. All the researchers involved were present (from the UK, Greece-via skype- and the US) and the project's advisory board members. There were stakeholders from Public Health England and the Greater London Authority who provided very useful input. Additionally two PhD students attended.
Year(s) Of Engagement Activity 2017
 
Description Symposium on measurement error at the Annual International Conference for Environmental Epidemiology September 2022 
Form Of Engagement Activity Participation in an activity, workshop or similar
Part Of Official Scheme? No
Geographic Reach International
Primary Audience Professional Practitioners
Results and Impact This was a Symposium presented at the Annual International Conference of the International Society for Environmental Epidemiology in Athens, September 2022. The Symposium was chaired by K. Katsouyanni (PI of the award) and Dr D. Evangelopoulos a member of the STEAM project and speakers included Katsouyanni, Evangelopoulos and Butland, all members of the STEAM project. The Symposium was entitled: "Impact of exposure measurement error (ME) on the health effect estimates: quantification and correction". The talks emphasized and built upon the results of the project. The abstracts are available from the Journal: Environmental Health Perspectives
Year(s) Of Engagement Activity 2022
URL https://pcoconvin.eventsair.com/QuickEventWebsitePortal/isee-2022/program/Agenda/AgendaItemDetail?id...
 
Description Workshop on interpretation of multi-pollutant model results for health impact assessment 
Form Of Engagement Activity Participation in an activity, workshop or similar
Part Of Official Scheme? No
Geographic Reach International
Primary Audience Professional Practitioners
Results and Impact This Workshop was organized by the National Institute for Health Research Health Protection Research Unit (NIHR HPRU) in Health Impact of Environmental Hazards King's College together with the STEAM project collaborators. It was addressing methodological topics related to analyses of health outcome data in STEAM. Interpretation of multi-pollutant models is a substantial challenge for quantifying health impacts. This can be difficult to deal with in situations where hard and fast conclusions are needed in a short time. The idea of the workshop was to be more forward thinking about how we can increase the evidence base, to make these decisions a bit easier over the next few years.
A review of the literature for information on the parameters needed to judge potential bias in multi-pollutant models (measurement error, correlations between pollutant errors, covariance etc) and plans to use these for simulations of how big a problem there might be, initially in a time series context, was presented.
In addition to understanding the bias from simulations, several issues arise from this work and in discussions in WHO and COMEAP.
(i) Even assuming better understanding of measurement error etc, how far can we get? Can we increase separation/decrease correlations between pollutants in terms of scale/personal exposure/spatio-temporal studies? Or should regulatory regimes be more focused on mixtures?
(ii) Discussion of whether we should be more sophisticated about how we compare the pollution and climate effects where epidemiological studies were done with the way in which they are applied in health impact assessment (rather than just different areas of the world/urban/rural, consider more about modelling scale, range of concentrations, covariance, ratios between pollutants, measurement error etc).
(iii) What information should be available to assist interpretation of multi-pollutant models in publications? Is there information in the data sets we already have that would help? How can multi-pollutant model evidence be summarised across studies?
Year(s) Of Engagement Activity 2017