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Ambient Air Ambient Air Sampling for Particulate MatterSampling for Particulate Matter
Robert W. VanderpoolRobert W. Vanderpool
Human Exposure and Atmospheric Sciences Human Exposure and Atmospheric Sciences DivisionDivision
Office of Research Office of Research and Developmentand Development
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Research Triangle Research Triangle Park, Park, NCNC
AgriculturalAgriculturalAgriculturalAgricultural AirAirAirAir QQQualityQualityualityuality TTTaskTaskaskask ForceForceForceForce MeetingMeetingMeetingMeeting
September 30, September 30, 20102010
Presentation Outline
Background and statement of issues
Characteristics of ambient aerosols (sources, size ranges,
definitions of MMD, GSD, aerodynamic diameter)
SizeSize-selectiveselective mmeasurementeasurement techniquestechniques ((inertialinertial impactorsimpactors aandnd
cyclones, definitions of cutpoint and slope)
DevelopmentDevelopment ofof healthhealth-basedbased PMPM standardsstandards – physiologicalphysiological
basis for PM sampling conventions
EPA’s method development for PM and PM
10 2.5
Review of TAMU’s methodology for estimating “True” PM
concentrations, and for estimating “oversampling” of EPA
reference methods
Backgground
To protect public health, the EPA has developed national ambient air quality
standardsstandards (NAAQS)(NAAQS) forfor airborneairborne particulateparticulate mattermatter (PM)(PM). ComplianceCompliance withwith thethe
PM NAAQS must be measured using EPA-approved samplers which were
developed to accurately measure PM concentrations independent of wind
speed and direction. FRM development was thoroughly peer-reviewed and
independent evaluations of FRMs have validated their size-selective
performanceperformance.
The agricultural industry typically generates airborne PM with much larger
mass median diameters (MMDs) than urban dusts, and has expressed the
beliefbelief tthathat certaincertain agriculturalagricultural operationsoperations areare bbeingeing overover--regulatedregulated byby EPAEPA duedue
to an over-estimation of PM emissions from these operations.
In particular, the industry has stated that “…all EPA-approved federal
referenreferencece methodmethod (FRM)(FRM) samplerssamplers dodo notnot accuaccuratelratelyy measuremeasure PMPM
concentrations in the presence of the large PM that is typical of PM emitted by
agricultural operations. The term for this phenomenon is “over-sampling”.”
These “over-samppgling” statements are directed towards source samppgling
methods (i.e., in-stack) as well as ambient sampling methods.
Background (cont)
Representatives of the agricultural industry have conducted their own
laboratory and field evaluations of EPA’s PM and PM FRM and have stated
2.5 10
thatthat thesethese FRMsFRMs overover-samplsamplee byby aa ffactoractor ofof 1.51.5 ttoo 1100 ((i.e.,i.e., 150%150% toto 1000%1000% overover-
sampling). Similar statements have been made regarding sampling of PM
aerosols. 2.5
The aggyricultural industry ppostulates that the mechanism for this over-samppgling
is the change in the sampler’s size selective performance (i.e., cutpoint and
slope) in the presence of large agricultural dusts.
EPA has thoroughly examined these statements and does not agree with the
ffunddamenttall bbasiis ffor tthhese sttattementts, ththe meththoddollogy upon whihichh ththe
statements were based, nor the conclusions drawn from this research.
During previous discussions, EPA and agricultural research staff have
acknowlacknowledgededged thatthat thesethese areare complexcomplex technicaltechnical issuesissues. EPAEPA researchresearch staffstaff
appreciates the critical importance of accurately regulating the agricultural
industry, and also for ensuring that public health is protected with an adequate
margin of safety.
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