Elsevier

Atmospheric Environment

Volume 44, Issue 35, November 2010, Pages 4346-4354
Atmospheric Environment

Back-extrapolation of estimates of exposure from current land-use regression models

https://doi.org/10.1016/j.atmosenv.2010.07.061Get rights and content

Abstract

Land use regression has been used in epidemiologic studies to estimate long-term exposure to air pollution within cities. The models are often developed toward the end of the study using recent air pollution data. Given that there may be spatially-dependent temporal trends in urban air pollution and that there is interest for epidemiologists in assessing period-specific exposures, especially early-life exposure, methods are required to extrapolate these models back in time. We present herein three new methods to back-extrapolate land use regression models. During three two-week periods in 2005–2006, we monitored nitrogen dioxide (NO2) at about 130 locations in Montreal, Quebec, and then developed a land-use regression (LUR) model. Our three extrapolation methods entailed multiplying the predicted concentrations of NO2 by the ratio of past estimates of concentrations from fixed-site monitors, such that they reflected the change in the spatial structure of NO2 from measurements at fixed-site monitors. The specific methods depended on the availability of land use and traffic-related data, and we back-extrapolated the LUR model to 10 and 20 years into the past. We then applied these estimates to residential information from subjects enrolled in a case–control study of postmenopausal breast cancer that was conducted in 1996.

Observed and predicted concentrations of NO2 in Montreal decreased and were correlated in time. The estimated concentrations using the three extrapolation methods had similar distributions, except that one method yielded slightly lower values. The spatial distributions varied slightly between methods. In the analysis of the breast cancer study, the odds ratios were insensitive to the method but varied with time: for a 5 ppb increase in NO2 using the 2006 LUR the odds ratio (OR) was about 1.4 and the ORs in predicted past concentrations of NO2 varied (OR∼1.2 for 1985 and OR∼1.3–1.5 for 1996). Thus, the ORs per unit exposure increased with time as the range and variance of the spatial distributions decreased, and this is due partly to the regression coefficient being approximately inversely proportional to the variance of exposure. Changing spatial variability complicates interpretation and this may have important implications for the management of risk. Further studies are needed to estimate the accuracy of the different methods.

Introduction

A particular challenge for epidemiologic studies is to accurately estimate historical exposure to traffic-related air pollution within cities. Land use regression (LUR) is a method to predict concentrations of pollutants at locations within cities for which measurements were not taken (Beelen et al., 2007, Brauer et al., 2003, Briggs et al., 1997, Crouse et al., 2009, Henderson et al., 2007, Hochadel et al., 2006, Jerrett et al., 2007, Madsen et al., 2007, Moore et al., 2007, Ross et al., 2007, Sahsuvaroglu et al., 2006, Wheeler et al., 2008). The method involves measuring ambient pollutants, usually using a dense environmental sampling campaign, and then developing a prediction model whereby the measured concentrations of air pollutants are regressed against proximate characteristics of land use and vehicular traffic. This method has been used in cohort studies to estimate the association between long-term exposure to air pollution and chronic health outcomes (Ballester et al., 2010, Beelen et al., 2008, Brauer et al., 2007, Brauer et al., 2008, Brunekreef et al., 2009, Gehring et al., 2009, Jerrett et al., 2009, Suglia et al., 2008, von et al., 2009, Yorifuji et al., 2010), but can also be relevant to case–control studies. Often, the LUR is developed toward the end of the study (e.g., at end of follow-up) so it is important to understand whether these models can characterize exposure adequately during the relevant etiological periods. The validity of the methodology is especially critical for outcomes that have long latency (e.g., most cancers). Given that there may be non-homogeneous, spatially-dependent temporal trends in urban air pollution and that there is interest for epidemiologists in assessing period-specific exposures, especially early life exposure, methods are required to back-extrapolate these models into the past.

We present here three new methods to extrapolate a “current” LUR back in time by incorporating historical trends in spatially-dependent concentrations of pollutants as well as temporal changes in land use and vehicular traffic. For the purpose of illustration, we sought to back-extrapolate approximately 10 years (to 1996) and 20 years (to 1985) a current LUR that we developed using measurements of nitrogen dioxide (NO2) in Montreal, Quebec, Canada, from a dense monitoring campaign that we conducted in 2005 and 2006 (Crouse et al., 2009). As a specific application of these new methods to an epidemiologic study, we applied the models to data from a case–control study of breast cancer that we conducted in the mid-1990s (Lenz et al., 2002, Labrèche et al., 2003, Labrèche et al., 2010).

Section snippets

Fixed-site monitoring data

Environment Canada, in collaboration with the City of Montreal, administers the Canadian National Air Pollution Surveillance (NAPS) network, a network of fixed-site monitors in the Montreal region (Fig. 1). The number of fixed-site monitors used to measure ambient concentrations of NO2 varied from 8 to 13 during the period of 1985 and 2006. Measurements of NO2 were made every hour and were analyzed using chemiluminescence (Thermo Environmental Instruments (TEI) Model 42C).

We obtained mean daily

Alternative LUR model for 2006

Table 2 shows the results of the alternative 2006 LUR model developed using the supervised forward stepwise model selection approach. Population density (partial R2 = 0.29), road network (partial R2 = 0.23), point source pollution (partial R2 = 0.06), and land use/cover measures (i.e., area of open water, distance to shoreline) (partial R2 = 0.07) included in the model explained 65% of the intraurban variability in the natural logarithm of NO2. In contrast, the original 2006 LUR model included 47

Discussion

We presented three new methods to extrapolate into the past estimates of exposure from current land use regression models. By incorporating non-homogeneous spatially-dependent temporal trends in ambient concentrations and changes in land use and vehicular traffic, these extrapolation methods allowed the spatial gradient of estimated concentrations from present models to vary over time and space.

The issue of accurately reconstructing historical exposure to traffic-related air pollution is

Conclusions

In summary, we developed three methods to extrapolate current land use regression models back in time, and we showed in a concrete example that plausible estimates of risk were obtained. Using these methods in other jurisdictions will depend on the availability in the past of the number and spatial distribution of fixed-site monitoring stations. Further studies are needed to estimate the accuracy of the different methods.

Competing interest declaration

We declare that we have no competing financial interests.

Acknowledgements

Support for this project was provided by grants from the Canadian Breast Cancer Initiative and the Canadian Institutes of Health Research (CIHR). Hong Chen gratefully acknowledges receipt of a CIHR Doctoral Research Award.

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