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The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an...

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deCastro B.R.1, Breysse P.N.2, Buckley T.J.3, Wang L.4, Mihalic J.N.2, Geyh A.S.2 1Westat, Rockville, MD. 2Johns Hopkins Bloomberg School of Public Health, Department of Environmental Health Sciences, Baltimore, MD. 3Ohio State University School of Public Health, Division of Environmental Health Sciences, Columbus, OH. 4Johns Hopkins Bloomberg School of Public Health, Department of Epidemiology, Baltimore, MD. The influence of traffic volume and ambient outdoor PAH on indoor PAH exposure was quantified at the Baltimore Traffic Study site, an unoccupied attached 2nd-floor apartment in an inner-city neighborhood “hot spot" surrounded by urban roadways that together carry over 150,000 vehicles per day. Monitoring of outdoor and indoor particle-bound PAH and traffic volume was conducted continously for 12 months at 10-minute intervals (n = 52,560). Time-series modeling accounted for complex and extensive autocorrelation. Vehicle count (0.57 [±SE=0.04] ng/m3 per 100 vehicles every ten minutes) and outdoor PAH (0.16 [±0.001] ng/m3 per ng/m3 outdoor PAH) are statistically significant predictors of indoor PAH, in addition to a mean background indoor exposure without indoor sources of 9.07 ng/m3. Spring 2003 (9.99 [±0.67] ng/m3) and Summer 2003 (9.27 [±1.27] ng/m3) are associated with the greatest increases in indoor PAH, relative to Summer 2002. An additional 1.64 [±0.27] ng/m3 is attributable to work days. Winds from the SW-S-NE quarter, which would have entrained PAH from Baltimore’s densely trafficked central business district and a nearby interstate highway, contribute significantly to indoor PAH (0.31 – 1.16 ng/m3). Dew point, outdoor temperature, and wind speed are also statistically significant predictors. Indoor PAH’s short-term autocorrelation is ARMA[3,3], where lag 3 indicates that PAH concentrations are correlated for up to 30 minutes. Significant autoregressive correlation at lags 144 and 1008 indicate autocorrelations at diurnal and weekly cycles, respectively. In a separate time series model, it was established that outdoor PAH itself depends at a statistically significant on vehicle count at a rate of 3.17 [±0.11] ng/m3 per 100 vehicles every ten minutes. Conclusion: local indoor & outdoor exposure to PAH from mobile sources is substantially modified by meteorologic and temporal conditions, including atmospheric transport processes. PAH concentration also demonstrates statistically significant autocorrelation at several timescales.
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Introduction Methods Results Conclusions The Dependence of Indoor PAH Concentrations on Outdoor PAHs and Traffic Volume in an Urban Residential Environment B. Rey de Castro, Sc.D. Westat Rockville, Maryland USA November 4, 2009 [email protected] Indoor PAHs @ ISES 2009
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Page 1: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

The Dependence of Indoor PAH

Concentrations on Outdoor PAHs and

Traffic Volume in an Urban Residential

Environment

B. Rey de Castro, Sc.D.

WestatRockville, Maryland USA

November 4, 2009

[email protected] Indoor PAHs @ ISES 2009

Page 2: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Outline

1 Introduction

2 MethodsMonitoring SiteMeasurementsImputation of Missing Values

3 ResultsExploratory AnalysisTime Series Models

4 Conclusions

[email protected] Indoor PAHs @ ISES 2009

Page 3: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Outline

1 Introduction

2 MethodsMonitoring SiteMeasurementsImputation of Missing Values

3 ResultsExploratory AnalysisTime Series Models

4 Conclusions

[email protected] Indoor PAHs @ ISES 2009

Page 4: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

PAH Health Risks

PAHs among Mobile Source Air Toxics

Potential population at risk: 17.8 million residences

Toxicity: Cancer

18th Century scrotal cancer among chimney sweepsLung cancer from occupational exposures

Toxicity: Neurodevelopment

Low birthweightRespiratory deficitsChromosomal degradationDiminished cognition

[email protected] Indoor PAHs @ ISES 2009

Page 5: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Monitoring SiteMeasurementsImputation of Missing Values

Outline

1 Introduction

2 MethodsMonitoring SiteMeasurementsImputation of Missing Values

3 ResultsExploratory AnalysisTime Series Models

4 Conclusions

[email protected] Indoor PAHs @ ISES 2009

Page 6: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Monitoring SiteMeasurementsImputation of Missing Values

Monitoring Site

[email protected] Indoor PAHs @ ISES 2009

Page 7: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Monitoring SiteMeasurementsImputation of Missing Values

Monitoring Site

[email protected] Indoor PAHs @ ISES 2009

Page 8: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Monitoring SiteMeasurementsImputation of Missing Values

Monitoring Site

[email protected] Indoor PAHs @ ISES 2009

Page 9: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Monitoring SiteMeasurementsImputation of Missing Values

Baltimore Traffic Study Objectives

Sustained, continuous monitoring: 12 months

High temporal resolution: 10-minute intervals

Simultaneous monitoring of traffic & covarying factors

Control expected autocorrelation: time series analysis

Conclude long-term characteristics of PAH exposure

[email protected] Indoor PAHs @ ISES 2009

Page 10: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Monitoring SiteMeasurementsImputation of Missing Values

Measurements

PAHs

EcoChem PAS 2000Selective ionization of particle-bound PAHsAlternating indoor-outdoor 5-minute samplingCombined into 10-minute observations

Traffic

Pneumatic counter5-minute counts

Weather

Rooftop weather station (30-minute)NWS airport measurements (60-minute)

All data transformed to 10-minute observational interval

[email protected] Indoor PAHs @ ISES 2009

Page 11: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Monitoring SiteMeasurementsImputation of Missing Values

Imputation of Missing Values

Linear regression with reference data

Predictions substituted for missing values

Add pseudorandom variate to reduce bias

Yimpute = Ypredict + N(0, σ2)

N = 52,560

July 1, 2002 to June 30, 2003

[email protected] Indoor PAHs @ ISES 2009

Page 12: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Exploratory AnalysisTime Series Models

Outline

1 Introduction

2 MethodsMonitoring SiteMeasurementsImputation of Missing Values

3 ResultsExploratory AnalysisTime Series Models

4 Conclusions

[email protected] Indoor PAHs @ ISES 2009

Page 13: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Exploratory AnalysisTime Series Models

Variability over Time

[email protected] Indoor PAHs @ ISES 2009

Page 14: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Exploratory AnalysisTime Series Models

Workday vs. Non-Workday

[email protected] Indoor PAHs @ ISES 2009

Page 15: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Exploratory AnalysisTime Series Models

Temperature & Dew Point

[email protected] Indoor PAHs @ ISES 2009

Page 16: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Exploratory AnalysisTime Series Models

Mixing Height & Wind Speed

[email protected] Indoor PAHs @ ISES 2009

Page 17: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Exploratory AnalysisTime Series Models

Models With Autocorrelation

Indoor PAHTraffic, outdoor PAHs, wind speed, wind direction,temperature, dew point, season, workdayARMA[3,3] autocorrelation

Yt,in = µin +

p∑i=1

βiXi ,t +MA(1 : 3)

AR(1 : 3)(144)(1008)+ εi ,in

Outdoor PAHTraffic, wind speed, wind direction, temperature, dewpoint, season, workdayARMA[1,1] autocorrelation

Yt,out = µout +

p∑i=1

βiXi ,t +MA(1)

AR(1)(144)(1008)+ εi ,out

[email protected] Indoor PAHs @ ISES 2009

Page 18: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Exploratory AnalysisTime Series Models

Indoor Parameters: Treemap Visualization

[email protected] Indoor PAHs @ ISES 2009

Page 19: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Exploratory AnalysisTime Series Models

Outdoor Parameters: Treemap Visualization

[email protected] Indoor PAHs @ ISES 2009

Page 20: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Exploratory AnalysisTime Series Models

Wind Direction: Outdoor vs. Indoor

Indoor PAHs, SW–S–SE: 0.59 – 1.16 ng/m3Outdoor PAHs, WSW–S–NE: 0.95 – 9.78 ng/m3

[email protected] Indoor PAHs @ ISES 2009

Page 21: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Outline

1 Introduction

2 MethodsMonitoring SiteMeasurementsImputation of Missing Values

3 ResultsExploratory AnalysisTime Series Models

4 Conclusions

[email protected] Indoor PAHs @ ISES 2009

Page 22: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Conclusions

1 Indoor PAHs depend on both traffic volume & outdoorPAHs

2 Outdoor PAHs depend on traffic volume

3 Observed diminished effect of traffic volume in afternoon

4 Season (Spring & Summer 2003) was strongest predictorof indoor & outdoor PAHs

5 Contributions from wind direction differ between indoor &outdoor PAHs

6 Meteorology & workday had significant effects

7 Autocorrelation was significant

[email protected] Indoor PAHs @ ISES 2009

Page 23: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Conclusions

1 Indoor PAHs depend on both traffic volume & outdoorPAHs

2 Outdoor PAHs depend on traffic volume

3 Observed diminished effect of traffic volume in afternoon

4 Season (Spring & Summer 2003) was strongest predictorof indoor & outdoor PAHs

5 Contributions from wind direction differ between indoor &outdoor PAHs

6 Meteorology & workday had significant effects

7 Autocorrelation was significant

[email protected] Indoor PAHs @ ISES 2009

Page 24: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Conclusions

1 Indoor PAHs depend on both traffic volume & outdoorPAHs

2 Outdoor PAHs depend on traffic volume

3 Observed diminished effect of traffic volume in afternoon

4 Season (Spring & Summer 2003) was strongest predictorof indoor & outdoor PAHs

5 Contributions from wind direction differ between indoor &outdoor PAHs

6 Meteorology & workday had significant effects

7 Autocorrelation was significant

[email protected] Indoor PAHs @ ISES 2009

Page 25: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Conclusions

1 Indoor PAHs depend on both traffic volume & outdoorPAHs

2 Outdoor PAHs depend on traffic volume

3 Observed diminished effect of traffic volume in afternoon

4 Season (Spring & Summer 2003) was strongest predictorof indoor & outdoor PAHs

5 Contributions from wind direction differ between indoor &outdoor PAHs

6 Meteorology & workday had significant effects

7 Autocorrelation was significant

[email protected] Indoor PAHs @ ISES 2009

Page 26: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Conclusions

1 Indoor PAHs depend on both traffic volume & outdoorPAHs

2 Outdoor PAHs depend on traffic volume

3 Observed diminished effect of traffic volume in afternoon

4 Season (Spring & Summer 2003) was strongest predictorof indoor & outdoor PAHs

5 Contributions from wind direction differ between indoor &outdoor PAHs

6 Meteorology & workday had significant effects

7 Autocorrelation was significant

[email protected] Indoor PAHs @ ISES 2009

Page 27: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Conclusions

1 Indoor PAHs depend on both traffic volume & outdoorPAHs

2 Outdoor PAHs depend on traffic volume

3 Observed diminished effect of traffic volume in afternoon

4 Season (Spring & Summer 2003) was strongest predictorof indoor & outdoor PAHs

5 Contributions from wind direction differ between indoor &outdoor PAHs

6 Meteorology & workday had significant effects

7 Autocorrelation was significant

[email protected] Indoor PAHs @ ISES 2009

Page 28: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Conclusions

1 Indoor PAHs depend on both traffic volume & outdoorPAHs

2 Outdoor PAHs depend on traffic volume

3 Observed diminished effect of traffic volume in afternoon

4 Season (Spring & Summer 2003) was strongest predictorof indoor & outdoor PAHs

5 Contributions from wind direction differ between indoor &outdoor PAHs

6 Meteorology & workday had significant effects

7 Autocorrelation was significant

[email protected] Indoor PAHs @ ISES 2009

Page 29: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Acknowledgements

Patrick N. Breysse Timothy J. BuckleyJana N. Mihalic Alison S. Geyh

Lu Wang

EPA grant

On SlideShare: http://cli.gs/BTSpahIndoor

[email protected]

[email protected] Indoor PAHs @ ISES 2009

Page 30: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Summary: Quantitative

Indoor PAHs

0.57 ng/m3 per 100 vehicles every 10 minutes0.16 ng/m3 per ng/m3 outdoor PAHCombination of fresh and aged PAHs

Outdoor PAHs

3.17 ng/m3 per 100 vehicles every 10 minutes

Season (Spring & Summer 2003) was strongest predictor

Indoor PAHs: 9.27 – 9.99 ng/m3Outdoor PAHs: 9.26 – 9.78 ng/m3

Workday

Indoor PAHs: 1.64 ng/m3Outdoor PAHs: 3.01 ng/m3

[email protected] Indoor PAHs @ ISES 2009

Page 31: The Longitudinal Dependence of Indoor PAH Concentration on Outdoor PAH and Traffic Volume in an Urban Residential Environment

IntroductionMethodsResults

Conclusions

Summary: Quantitative

MeteorologyIndoor PAHs

Wind speed: -0.38 ng/m3 per m/sTemperature: -2.48 ng/m3 per 5 CDew point: 1.87 ng/m3 per 5 C

Outdoor PAHs

Wind speed: -0.79 ng/m3 per m/sTemperature: -3.45 ng/m3 per 5 CDew point: 2.77 ng/m3 per 5 C

[email protected] Indoor PAHs @ ISES 2009


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