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Relationship between traffic-related air pollution and inflammation biomarkers using structural equation modeling

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Abstract

Background: Evidence suggests that exposure to traffic-related air pollution (TRAP) and social stressors can increase inflammation. Given that there are many different markers of TRAP exposure, socio-economic status (SES), and inflammation, analytical approaches can leverage multiple markers to better elucidate associations. In this study, we applied structural equation modeling (SEM) to assess the association between a TRAP construct and a SES construct with an inflammation construct. Methods: This analysis was conducted as part of the Community Assessment of Freeway Exposure and Health (CAFEH; N = 408) study. Air pollution was characterized using a spatiotemporal model of particle number concentration (PNC) combined with individual participant time-activity adjustment (TAA). TAA-PNC and proximity to highways were considered for a construct of TRAP exposure. Participant demographics on education and income for an SES construct were assessed via questionnaires. Blood samples were analyzed for high sensitivity C-reactive protein (hsCRP), interleukin-6 (IL-6), and tumor necrosis factor-α receptor II (TNFRII), which were considered for the construct for inflammation. We conducted SEM and compared our findings with those obtained using generalized linear models (GLM). Results: Using GLM, TAA-PNC was associated with multiple inflammation biomarkers. An IQR (10,000 particles/cm3) increase of TAA-PNC was associated with a 14 % increase in hsCRP in the GLM. Using SEM, the association between the TRAP construct and the inflammation construct was twice as large as the associations with any individual inflammation biomarker. SES had an inverse association with inflammation in all models. Using SEM to estimate the indirect effects of SES on inflammation through the TRAP construct strengthened confidence in the association of TRAP with inflammation. Conclusion: Our TRAP construct resulted in stronger associations with a combined construct for inflammation than with individual biomarkers, reinforcing the value of statistical approaches that combine multiple, related exposures or outcomes. Our findings are consistent with inflammatory risk from TRAP exposure.

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... IL-6 and CRP are the two most commonly increased inflammatory factors, and the nerve growth factor (NGF) is the most commonly decreased factor in depression and schizophrenia [67]. On the other hand, exposure to traffic-related air pollution is associated with increased peripheral IL-6, CRP, and TNF-α receptor II (TNFRII) [68]. Inflammatory factors, such as IL-6 and CRP, may also have the potential to serve as early warning indicators for air pollutionrelated risk of mental disorders ( Figure 1). ...
... IL-6 and CRP are the two most commonly increased inflammatory factors, and the nerve growth factor (NGF) is the most commonly decreased factor in depression and schizophrenia [67]. On the other hand, exposure to traffic-related air pollution is associated with increased peripheral IL-6, CRP, and TNF-α receptor II (TNFRII) [68]. Inflammatory factors, such as IL-6 and CRP, may also have the potential to serve as early warning indicators for air pollution-related risk of mental disorders ( Figure 1). ...
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Air pollution affects billions of people worldwide, yet ambient pollution measurements are limited for much of the world. Urban air pollution concentrations vary sharply over short distances (≪1 km) owing to unevenly distributed emission sources, dilution, and physicochemical transformations. Accordingly, even where present, conventional fixed-site pollution monitoring methods lack the spatial resolution needed to characterize heterogeneous human exposures and localized pollution hotspots. Here, we demonstrate a measurement approach to reveal urban air pollution patterns at 4–5 orders of magnitude greater spatial precision than possible with current central-site ambient monitoring. We equipped Google Street View vehicles with a fast-response pollution measurement platform and repeatedly sampled every street in a 30-km² area of Oakland, CA, developing the largest urban air quality data set of its type. Resulting maps of annual daytime NO, NO2, and black carbon at 30 m-scale reveal stable, persistent pollution patterns with surprisingly sharp small-scale variability attributable to local sources, up to 5–8× within individual city blocks. Since local variation in air quality profoundly impacts public health and environmental equity, our results have important implications for how air pollution is measured and managed. If validated elsewhere, this readily scalable measurement approach could address major air quality data gaps worldwide.
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Land use regression (LUR) models have been used to assess air pollutant exposure, but limited evidence exists on whether location-specific LUR models are applicable to other locations (transferability) or general models are applicable to smaller areas (generalizability). We tested transferability and generalizability of spatial-temporal particle number concentration (PNC) LUR models for Boston-area (MA, USA) urban neighborhoods near Interstate 93. Four neighborhood-specific regression models and one Boston-area model were developed from mobile monitoring measurements (34-46 days/neighborhood over one year each). Transferability was tested by applying each neighborhood-specific model to all four neighborhoods; generalizability was tested by applying the Boston-area model to each neighborhood. Both were tested with and without neighborhood-specific calibration. Important PNC predictors (adjusted-R(2) = 0.24-0.43) included wind speed and direction, temperature, highway traffic volume, and distance from the highway edge. Direct model transferability was poor (R(2) <0.17). Locally-calibrated transferred models (R(2) = 0.19-0.40) and the Boston-area model (adjusted-R(2) = 0.26, range: 0.13-0.30) performed similarly to neighborhood-specific models. However, the coefficients of locally-calibrated transferred models were sometimes uninterpretable. Our results show that transferability of neighborhood-specific PNC LUR models is limited, but that general models perform acceptably in multiple areas, especially when calibrated with local data.
Article
Relatively few studies have characterized differences in intra- and inter-neighborhood traffic-related air pollutant (TRAP) concentrations and distance-decay gradients in along an urban highway for the purposes of exposure assessment. The goal of this work was to determine the extent to which intra- and inter-neighborhood differences in TRAP concentrations can be explained by traffic and meteorology in three pairs of neighborhoods along Interstate 93 (I-93) in the metropolitan Boston area (USA). We measured distance-decay gradients of seven TRAPs (PNC, pPAH, NO, NOX, BC, CO, PM2.5) in near-highway (<400 m) and background areas (>1 km) in Somerville, Dorchester/South Boston, Chinatown and Malden to determine whether (1) spatial patterns in concentrations and inter-pollutant correlations differ between neighborhoods, and (2) variation within and between neighborhoods can be explained by traffic and meteorology. The neighborhoods ranged in area from 0.5 to 2.3 km(2). Mobile monitoring was performed over the course of one year in each pair of neighborhoods (one pair of neighborhoods per year in three successive years; 35-47 days of monitoring in each neighborhood). Pollutant levels generally increased with highway proximity, consistent with I-93 being a major source of TRAP; however, the slope and extent of the distance-decay gradients varied by neighborhood as well as by pollutant, season and time of day. Correlations among pollutants differed between neighborhoods (e.g., ρ = 0.35-0.80 between PNC and NOX and ρ = 0.11-0.60 between PNC and BC) and were generally lower in Dorchester/South Boston than in the other neighborhoods. We found that the generalizability of near-road gradients and near-highway/urban background contrasts was limited for near-highway neighborhoods in a metropolitan area with substantial local street traffic. Our findings illustrate the importance of measuring gradients of multiple pollutants under different ambient conditions in individual near-highway neighborhoods for health studies involving inter-neighborhood comparisons.
Article
The link between air pollution and adverse health effects was established clearly and consistently 15 years ago. More recently, improved air quality in American cities was associated with increased life expectancy (Pope III et al., 2009). These observations spurred policy makers to devise air quality legislation and impose an increasing set of tightening emission standards aimed at reducing the anticipated health effects but at an increasing economic cost.Over the last couple of years there was a growing consensus that vehicle related air pollution, may be more toxic or detrimental to public health than the general air pollution mixture. The hypothesis that emissions from mobile sources are a main culprit is based on the observation that tailpipe PM emissions generally fall within the Ultra Fine Particle (UFP<0.1mm) and UFP may have health impacts which are additive to those attributed to PM (Knol et al., 2009). Also a number of studies have observed an association between health effects and the proximity to major roads (Gauderman et al., 2007).In addition there is continued concern over emissions of road trafficbecause suburban sprawl and increased vehicle miles traveled mayin theorycontribute to an increased exposure through an increaseinthe average intake fraction of pollutants from vehicle exhaust.A thorough review of peer reviewed literature concluded thatthere was suggestive but insufficient evidence to decide on a causallink between vehicle emissions and most of the health endpointsexcept for the exacerbation of existing asthma although therewas no unanimity (Health Effects Institute, 2009). Summarizingthe situation in its critical review the Health Effects Institute panelconcluded that most epidemiological studies lack accurate infor-mation on the true exposure of the test-persons involved (HealthEffects Institute, 2009).Nevertheless policy makers often refer to health effects tosupport specific policies, plans, projects and measures targetingthe transport sector. Given the uncertainty about the causal linkbetweenspecificvehicle emissions and health, policy makersshould carefully devise no-regret measures or risk spending budgeton measures that in retrospect may prove to be less effective.Several recent epidemiological studies have used the proximityof the home to major roads as a surrogate for exposure and sug-gested that proximity of people to motorized road traffic partlyexplains observed health effects (Beelen et al., 2007). The use ofsimple proximityas a surrogate for exposure to mobile source emis-sions has its merits, but the HEI now recommends that exposureanalysis should use moreaccurate methods such as land-use regres-sion, or hybrid models including measurements. Unfortunatelymeasuring exposure directly requires a large number of peopleand is therefore often not feasibly or prohibitively expensive.In our opinion, exposure analysis could be improved by deter-mining more accurately where people spend their time. Peopleare only exposed to concentrations occurring in the areas wherethey are active at that time, which during the day is very oftennotat their home address (Beckx et al., 2008, 2009). We thereforesuggest that exposure modelling takes advantage of the new possi-bilities offered by Activity-based models. This new class of modelsis able to predict for individuals where and when specific activities(e.g. work, leisure, shopping,.) are conducted.Both location, time of day and the microenvironment are essen-tial parameters to accurately determine exposure to mobile sourcepollution with a high spatial variability such as NO2and Ultra FineParticles. High resolution data on the temporal and spatial variationof the pollutant concentrations can be derived from measurementsor dispersion models respectively. Similar high resolution data forthe whereabouts of people can only be derived from Activity-basedmodels. Although their obvious advantages for environmentalpurposes were recognized by Shiftan almost a decade ago (Shiftan,2000), applications to exposure modelling remain scarce. Activity-based models have recently been used to provide a better totalestimate of exposure while also enabling the disaggregation of indi-vidual exposure over activities (Beckx et al., 2008, 2009). They cantherefore be used to reduce exposure misclassification and estab-lish relationships between health impacts and air quality moreprecisely. Policy makers for their part can take advantage of theActivity-based paradigm to devise strategies that reduce exposureby changing time activity patterns. This will enable policies thatreduce emissions from those sources that have the largest impacton exposure.
Article
Exposure to high levels of traffic-generated particles may pose risks to human health; however, limited measurement has been conducted at homes near highways. The purpose of this study was to characterize differences between indoor and outdoor particle number concentration (PNC) in homes near to and distant from a highway and to identify factors that may affect infiltration. We monitored indoor and outdoor PNC (6-3000 nm) for 1-3 weeks at 18 homes located <1500 m from Interstate-93 (I-93) in Somerville, MA (USA). Median hourly indoor and outdoor PNC pooled over all homes were 5.2 × 10(3) and 5.9 × 10(3) particles/cm(3), respectively; the median ratio of indoor-to-outdoor PNC was 0.95 (5(th)/95th percentile: 0.42/1.75). Homes <100 m from I-93 (n=4) had higher indoor and outdoor PNC compared with homes >1000 m away (n=3). In regression models, a 10% increase in outdoor PNC was associated with an approximately equal (10.8%) increase in indoor PNC. Wind speed and direction, temperature, time of day and weekday were also associated with indoor PNC. Average mean indoor PNC was lower for homes with air conditioners compared with homes without air conditioning. These results may have significance for estimating indoor, personal exposures to traffic-related air pollution.Journal of Exposure Science and Environmental Epidemiology advance online publication, 16 January 2013; doi:10.1038/jes.2012.116.
Article
Despite increasing regulatory attention and literature linking roadside air pollution to health outcomes, studies on near roadway air quality have not yet been well synthesized. We employ data collected from 1978 as reported in 41 roadside monitoring studies, encompassing more than 700 air pollutant concentration measurements, published as of June 2008. Two types of normalization, background and edge-of-road, were applied to the observed concentrations. Local regression models were specified to the concentration-distance relationship and analysis of variance was used to determine the statistical significance of trends. Using an edge-of-road normalization, almost all pollutants decay to background by 115-570 m from the edge of road; using the more standard background normalization, almost all pollutants decay to background by 160-570 m from the edge of road. Differences between the normalization methods arose due to the likely bias inherent in background normalization, since some reported background values tend to underpredict (be lower than) actual background. Changes in pollutant concentrations with increasing distance from the road fell into one of three groups: at least a 50% decrease in peak/edge-of-road concentration by 150 m, followed by consistent but gradual decay toward background (e.g., carbon monoxide, some ultrafine particulate matter number concentrations); consistent decay or change over the entire distance range (e.g., benzene, nitrogen dioxide); or no trend with distance (e.g., particulate matter mass concentrations).
Article
Because structural equation modeling (SEM) has become a very popular data-analytic technique, it is important for clinical scientists to have a balanced perception of its strengths and limitations. We review several strengths of SEM, with a particular focus on recent innovations (e.g., latent growth modeling, multilevel SEM models, and approaches for dealing with missing data and with violations of normality assumptions) that underscore how SEM has become a broad data-analytic framework with flexible and unique capabilities. We also consider several limitations of SEM and some misconceptions that it tends to elicit. Major themes emphasized are the problem of omitted variables, the importance of lower-order model components, potential limitations of models judged to be well fitting, the inaccuracy of some commonly used rules of thumb, and the importance of study design. Throughout, we offer recommendations for the conduct of SEM analyses and the reporting of results.
A scoping review of published research on ultrafine particle exposure and health outcomes. Ambient Combustion Ultrafine Particles and Health
  • F Berklein
  • A Finley
  • W Zamore
  • D Brugge
Berklein F, Finley A, Zamore W, Brugge D, & M, C. (2021). A scoping review of published research on ultrafine particle exposure and health outcomes. Ambient Combustion Ultrafine Particles and Health. (pp. 255-298): Nova Science Publishers.
An evidence map of ultrafine epidemiology
  • D Brugge
  • F Berklein
  • Q Yao
  • A Turner
  • W Zamore
  • M Chung
Brugge D, Berklein F, Yao Q, Turner A, Zamore W, & Chung M. (2018). An evidence map of ultrafine epidemiology. Paper presented at the ETH Conference on Combustion Generated Nanoparticles, Zurich.
Integrated science assessment (ISA) for particulate matter
  • U Epa
EPA, U. (2019). Integrated science assessment (ISA) for particulate matter. Agency USEP, editor. Washington, DC2009.
Traffic-Related Air Pollution: A Critical Review of the Literature on Emissions, Exposure, and Health Effects
  • Hei
HEI. (2010). Traffic-Related Air Pollution: A Critical Review of the Literature on Emissions, Exposure, and Health Effects. HEI Special Report 17: HEI Boston, MA.
A scoping review of published research on ultrafine particle exposure and health outcomes
  • Berklein
An evidence map of ultrafine epidemiology
  • Brugge