2016
DOI: 10.1016/j.apr.2016.02.003
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A comparative analysis of temporary and permanent beta attenuation monitors: The importance of understanding data and equipment limitations when creating PM 2.5 air quality health advisories

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Cited by 31 publications
(18 citation statements)
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“…The performance of FEMs and near-FEM grade instruments during these high pollution times have not been validated in the field. For example, Schweizer et al [ 44 ] found that the EBAMs commonly used for temporary smoke monitoring networks overreported PM 2.5 compared to BAMs, but only when RH was above 40%. These potential variations in the reference measurement accuracy and precision during smoke impacted times may have led to weaker correlations and introduced variation in the slope of the linear regressions across sites.…”
Section: Resultsmentioning
confidence: 99%
“…The performance of FEMs and near-FEM grade instruments during these high pollution times have not been validated in the field. For example, Schweizer et al [ 44 ] found that the EBAMs commonly used for temporary smoke monitoring networks overreported PM 2.5 compared to BAMs, but only when RH was above 40%. These potential variations in the reference measurement accuracy and precision during smoke impacted times may have led to weaker correlations and introduced variation in the slope of the linear regressions across sites.…”
Section: Resultsmentioning
confidence: 99%
“…The ambient PM 2.5 concentrations measured at the AMS community sites during fire impact periods are on the same order as PM 2.5 concentrations that have been reported for wildland firefighter occupational exposures ( Naeher et al, 2006 ; Miranda et al, 2010 ; Adetona et al, 2011 ), and in some cases higher by > 2 orders of magnitude above downwind community monitoring sites where observable public health effects were documented ( Lee et al, 2014 ; Liu et al, 2015 ; Reid et al, 2016 ; Adetona et al, 2016 ; Kim et al, 2017 ). Ambient PM 2.5 measurements made as part of past routine community monitoring programs and emergency response operations in many cases have not reported concentrations above 800–1000 μg m −3 due to inherent limitations of the continuous monitoring instruments ( Bytnerowicz et al, 2016 ; Schweizer et al, 2016 ) and filter loading related flow restrictions on integrated samplers ( Landis et al, 2017 ). Unfortunately, carbon dioxide (CO 2 ) measurements were not part of the WBEA AMS routine monitoring plan in 2016, so modified combustion efficiencies ( Urbanski, 2013 ) could not be calculated; and the measured ambient concentrations could not be categorized in terms of fire combustion regime (e.g., flaming, smoldering).…”
Section: Resultsmentioning
confidence: 99%
“…eBAMs (Model 9800, MetOne, Grants Pass, OR), which work by beta attenuation method for the measurement of PM 2.5 mass concentration ( Cheng et al., 2008 ; Cisneros et al., 2014 ; Schweizer et al., 2016 ) eBAMs were deployed in North and South sites. eBAMs are relatively mobile instruments and intended for temporary deployment, although have shown good correlation (R 2 = 0.9 for daily mean) with non-mobile federal equivalent method BAM instruments ( Schweizer et al., 2016 ). We employed manufacturer-supplied inlet air heating to avoid humidity-related errors ( MetOne, 2011 ) and manufacturer-supplied PM 2.5 cyclones, with 15 min sampling frequency and 16.7 Lpm flow rate (corresponding to 2.5 μm cut point).…”
Section: Methodsmentioning
confidence: 99%