Modeling highway-generated air pollution in a residential...

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Modeling highway Modeling highway - - generated air generated air pollution in a residential urban pollution in a residential urban neighborhood neighborhood Allison St. Vincent Allison St. Vincent Urban Environmental Pollution, Boston, MA, USA Urban Environmental Pollution, Boston, MA, USA June 22, 2010 June 22, 2010

Transcript of Modeling highway-generated air pollution in a residential...

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Modeling highwayModeling highway--generated air generated air pollution in a residential urban pollution in a residential urban

neighborhoodneighborhood

Allison St. VincentAllison St. VincentUrban Environmental Pollution, Boston, MA, USAUrban Environmental Pollution, Boston, MA, USA

June 22, 2010June 22, 2010

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Project MotivationProject Motivation

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►►About 10% of the United States population About 10% of the United States population lives within 100 m of a highway.lives within 100 m of a highway.

►►Accurate exposure estimates to quantify Accurate exposure estimates to quantify health effects require knowledge of the health effects require knowledge of the spatial and temporal variations in highwayspatial and temporal variations in highway--generated air pollution.generated air pollution.

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ObjectivesObjectives

►►Develop a model that predicts highwayDevelop a model that predicts highway--generated air pollution concentrations on an generated air pollution concentrations on an hourly basis with 20 m x 20 m spatial hourly basis with 20 m x 20 m spatial resolution.resolution.

►►Use the model to assign personal exposures Use the model to assign personal exposures to highwayto highway--generated air pollution.generated air pollution.

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MethodologyMethodology

►►Conduct intensive air pollution monitoring in Conduct intensive air pollution monitoring in a mobile research lab.a mobile research lab.

►►Develop a model to extrapolate from Develop a model to extrapolate from individual monitoring events to all individual monitoring events to all meteorological and traffic conditions in the meteorological and traffic conditions in the study area.study area.

►►Combine model results with personal timeCombine model results with personal time--activity histories to estimate exposures.activity histories to estimate exposures.

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►► PNC, particle size PNC, particle size distribution, NO/NOdistribution, NO/NOXX, CO, , CO, PPAH, BC, PMPPAH, BC, PM2.52.5

Research LabResearch Lab

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InstrumentationInstrumentation

ParameterParameter EquipmentEquipmentParticle number Particle number

concentrationconcentration condensation particle countercondensation particle counterParticle size distributionParticle size distribution scanning mobility particle sizerscanning mobility particle sizerNO/NONO/NOXX chemiluminescence analyzerchemiluminescence analyzerCOCO gas filter correlation analyzergas filter correlation analyzerPPAHPPAH photoelectric aerosol sensorphotoelectric aerosol sensorBlack carbon (BC)Black carbon (BC) aethalometeraethalometerPMPM2.52.5 laser photometerlaser photometer

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Data CollectedData Collected

►►Collect data representing all typical weather Collect data representing all typical weather conditions.conditions.

►►Currently have data from 6Currently have data from 6--hour blocks on hour blocks on >35 days representing:>35 days representing: Weekdays, Saturdays, SundaysWeekdays, Saturdays, Sundays Summer, Fall, Winter, SpringSummer, Fall, Winter, Spring Morning and AfternoonMorning and Afternoon

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Ultrafine ParticlesUltrafine Particles

►►Diameter <100 nm.Diameter <100 nm.►►More toxic per unit mass than particles with More toxic per unit mass than particles with

larger diameters (e.g., Dockery et al., larger diameters (e.g., Dockery et al., 2007).2007).

►►Currently, in the USA, particles are Currently, in the USA, particles are regulated by mass (PMregulated by mass (PM2.52.5, PM, PM1010), not ), not number.number.

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Wind direction: NWWind speed: 3-23 mph

Temperature: 22.8-23.5 ˚F

400 mbuffer

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California Line Source Dispersion California Line Source Dispersion Model (CALINE4) OverviewModel (CALINE4) Overview

►► Gaussian model Gaussian model designed to model CO.designed to model CO.

►► Inputs: Meteorology, Inputs: Meteorology, source strength, and source strength, and site geometry.site geometry.

►► Output: Pollutant Output: Pollutant concentrations at concentrations at designated receptors.designated receptors.

►► Predicts air quality Predicts air quality impacts within 500 m impacts within 500 m of source.of source. distance

conc

entr

atio

n

wind

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Source StrengthSource Strength

►►Reported as emission factors.Reported as emission factors. e.g., g/vehiclee.g., g/vehicle--milemile

►►Usually tabulated.Usually tabulated.►►Since tables donSince tables don’’t exist for ultrafinest exist for ultrafines………… we fit the emission factor to data as a we fit the emission factor to data as a

model parameter (after Gramotnev et al., model parameter (after Gramotnev et al., 2004).2004).

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Emission Factor CalibrationEmission Factor CalibrationSomerville, MA Jan. 6, 2010 07:30-08:30

Distance from I-93 centerline, m-600 -400 -200 0 200 400 600

part

icle

num

ber

conc

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/cc

0.0

5.0e+4

1.0e+5

1.5e+5

2.0e+5

2.5e+5 MeasurementsModel

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MeasurementsModel

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Emission Factor ResultsEmission Factor Results

Study Emission factor ( x 1014 particles/veh-mile)

particle size range (nm)

This study 9-18 7 – 225

Gramotnev et al., 2003

4.5 <100

Birmili et al., 2009 3.4 (±0.3) < 500

Zhu and Hinds, 2005 8.3 7 – 1,000

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Some possible explanations for our Some possible explanations for our relatively high emission factorrelatively high emission factor

►►Noise barriers shield Noise barriers shield neighborhoods from neighborhoods from highwayhighway--generated generated pollution.pollution.

►►Colder temperatures Colder temperatures than other studies.than other studies.

►►Vehicle speeds may Vehicle speeds may also play a role.also play a role.

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Comparison of Modeled and Comparison of Modeled and Measured CO ResultsMeasured CO Results

wind

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ConclusionsConclusions

►►Generally good agreement between model Generally good agreement between model results and measurements.results and measurements.

►►Large variation on 1Large variation on 1--hour timescale.hour timescale.►►Noise barrier and hills likely have strong Noise barrier and hills likely have strong

effect on highwayeffect on highway--generated pollutant generated pollutant mixing.mixing.

►►More sophisticated models (e.g., QUIC) are More sophisticated models (e.g., QUIC) are needed to accurately predict concentration needed to accurately predict concentration variations over complex urban terrain.variations over complex urban terrain.

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Next StepsNext Steps

►►Validate emission factor estimate using Validate emission factor estimate using additional days of data.additional days of data.

►►Develop Quick Urban & Industrial Complex Develop Quick Urban & Industrial Complex (QUIC) Dispersion Model to include noise (QUIC) Dispersion Model to include noise barrier and elevation.barrier and elevation.

►►Determine which other roads may Determine which other roads may significantly contribute to particle levels.significantly contribute to particle levels.

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AcknowledgmentsAcknowledgments

►►Funding for this work was provided by Funding for this work was provided by NIH grant ES015462 and the CEE NIH grant ES015462 and the CEE Department of Tufts University. Department of Tufts University. 18

►►Jessica PerkinsJessica Perkins►►Piers MacNaugtonPiers MacNaugton►►Eric WilburnEric Wilburn►►Kelly SmithKelly Smith►►And the rest of And the rest of

CAFEHCAFEH

►►John DurantJohn Durant►►Doug BruggeDoug Brugge►►Jeffrey TrullJeffrey Trull►►Wig ZamoreWig Zamore►►Christine RiouxChristine Rioux

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