Abstract

ABSTRACT The present study evaluated the positive and negative biases in measurements of condensable particulate matter (CPM) conducted according to U.S. EPA Method 202. To reduce the overestimation of CPM, four factors were investigated: the SO2 absorption, condensate volume, oxygen content, and residence time. The underestimation was assessed by examining the weight loss related to the electrostatic charge of the evaporation beaker, vapor pressure of the particles, volume of the rinsing solvent, size of the evaporation beaker, and leakage between the filter paper and its holder. Additionally, we constructed a forced ventilation chamber to decrease the drying time of the sampled CPM’s organic fraction. The results revealed that our homemade condensate-diverting impinger could neither eliminate nor reduce the artifacts produced by SO2, as the SO2 had already oxidized by the time it passed through the Graham condenser and interacted with water. Since the residence time, condensate volume, and oxygen content can all exacerbate the overestimation of CPM, field sampling should be performed as quickly as possible. Furthermore, the evaporation beaker should be electrostatically neutralized prior to its weighing. Nitrogen purging may reduce the mass of the particle fraction possessing high vapor pressure, as these substances are highly volatile. Also, we found that when we used a smaller beaker, less residual mass remained in it after transferring the CPM sample to the weighing tin. We measured a 4% loss in particles due to the gap between the filter paper and the filter paper holder provided by the original manufacturer; therefore, a gasket to minimize leakage is recommended. Finally, the organic fraction required only 1.5–2.5 h of drying time when it was placed in the forced ventilation chamber, and a sample recovery rate of > 98.5% was subsequently achieved. Although artifacts produced by SO2 are inevitable, the improvements we suggest can enhance the precision of PM2.5 measurements.

Highlights

  • Particulate air pollutants can severely affect the environment, economy, and health (Ramanathan et al, 2007; Apte et al, 2015; Xie et al, 2016)

  • The present study evaluated the positive and negative biases in measurements of condensable particulate matter (CPM) conducted according to U.S EPA Method 202

  • Particulate matter can be divided into filterable particulate matter (FPM), which exists in the solid or liquid phase in stack flue gas, and condensable particulate matter (CPM), which exists in the gas/vapor phase in stack flue gas

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Summary

Introduction

Particulate air pollutants can severely affect the environment, economy, and health (Ramanathan et al, 2007; Apte et al, 2015; Xie et al, 2016). They can travel across large areas and countries, leading to regional or global air pollution (Yang et al, 2008; Karthik et al, 2017). Particulate matter can be divided into filterable particulate matter (FPM), which exists in the solid or liquid phase in stack flue gas, and condensable particulate matter (CPM), which exists in the gas/vapor phase in stack flue gas. As CPM leaves the stack, it cools down in the atmosphere and condenses to form solid or liquid particulate matter.

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