Hurst Road Air Quality Monitoring Site
Site Location
Views of Site from Four Cardinal Directions
Views from Site in Four Cardinal Directions
Monitoring Siting Criteria for the Hurst Road Air Quality Monitoring Site
Introduction
The Code of Federal Regulation Title 40 Part 58 covers Ambient Air Quality Surveillance. Appendix E to Part 58—Probe and Monitoring Path Siting Criteria for Ambient Air Quality Monitoring contains specific location criteria applicable to State and Local Air Monitoring Stations (SLAMS) ambient air quality monitoring probes and inlets. These siting criteria are necessary to ensure the uniform collection of compatible and comparable air quality data. The probe siting criteria discussed in Appendix E must be followed to the greatest extent possible, although there may be situations where some deviation from the siting criteria may be necessary. Specific siting criteria that are phrased with a "must" are defined as requirements and exceptions must be approved through the waiver provisions. However, siting criteria that are phrased with a “should” are defined as goals to meet for consistency but are not requirements.
The Hurst Road site, located near the North Star Volunteer Fire Department Station 3 in North Pole, is a particulate matter (PM2.5) and sulfur dioxide (SO2) monitoring site. Monitoring objectives for Hurst Road are gathering data on highest concentrations of PM2.5 pollutants expected in an area and impact of significant sources. The site consists of a pair of PM2.5 Thermo Scientific Sequential Partisols, a PM2.5 Met One Beta Attenuation Monitor (BAM), and a Thermo Scientific 43i SO2 analyzer. Additionally, there is an URG 3000N monitor and a Met One Super SASS monitor that are part of the PM2.5 Chemical Speciation Network (CSN). Hurst Road is a Special Purpose Monitoring (SPM) site for PM2.5 pollutants. The site also houses a 72-foot tower featuring three levels of meteorological instrumentation to enable correlation of the pollutant concentrations at breathing level during inversion events.
Placement and Spacing
The table below has siting criteria as outlined in 40 CFR 58, Appendix E. The criteria were reduced to show only relevant criteria for the site.
Particulate Matter (PM2.5 & PM10)
| Applicable Section | Siting Criteria | Observed |
|---|---|---|
| Horizontal and Vertical Placement | 2-15 meters above ground level for neighborhood or larger spatial scale, 2-7 meters for microscale spatial scale sites and middle spatial scale PM10-2.5 sites. 1 meter vertically or horizontally away from any supporting structure, walls, etc., and away from dusty or dirty areas. If located near the side of a building or wall, then locate on the windward side relative to the prevailing wind direction during the season of highest concentration potential. |
Criteria Met. Approximately 4.7 meters for FRM instrument. Approximately 4 meters for BAM. |
| Spacing from Minor Sources | For neighborhood or larger spatial scales avoid placing the monitor near local, minor sources. The source plume should not be allowed to inappropriately impact the air quality data collected at a site. Particulate matter sites should not be located in an unpaved area unless there is vegetative ground cover year-round. |
Criteria Met. Adjacent gravel parking lot with relatively low traffic load. |
| Spacing from Obstructions (a) | To avoid scavenging, the inlet must have unrestricted airflow and be located away from obstacles. The separation distance must be at least twice the height that the obstacle protrudes above the probe inlet. |
Criteria Met. No obstacles. |
| Spacing from Obstructions (b) | The inlet must have unrestricted airflow in an arc of at least 180 degrees. This arc must include the predominant wind direction for the season of greatest pollutant concentration potential. For particle sampling, a minimum of 2 meters of separation from walls, parapets, and structures is required for rooftop site placement. |
Criteria Met. Unrestricted. |
| Spacing from Trees | To reduce possible interference the inlet must be at least 10 meters or further from the drip line of trees. |
Criteria Met. Approximately 10 meters to drip line. |
| Spacing from Roadways | Spacing from roadways is dependent on the spatial scale and ADT count. See 40 CFR 58 Appendix E Section 6.3(b) and Figure E-1 for specific requirements. |
Criteria Met. Approximately 21 meters from roadway. |
Sulfur Dioxide (SO2)
| Applicable Section | Siting Criteria | Observed |
|---|---|---|
| Horizontal and Vertical Placement | 2-15 meters above ground level. 1 meter vertically or horizontally away from any supporting structure, walls, etc., and away from dusty or dirty areas. If located near the side of a building or wall, then locate on the windward side relative to the prevailing wind direction during the season of highest concentration potential. |
Criteria Met. Sample inlet is approximately 3 meters above ground level. |
| Spacing from Minor Sources | For neighborhood scale avoid placing the monitor probe inlet near local, minor sources. The source plume should not be allowed to inappropriately impact the air quality data collected at a site. |
Criteria Met. |
| Spacing from Obstructions | To avoid scavenging, the probe inlet must have unrestricted airflow and be located away from obstacles. The separation distance must be at least twice the height that the obstacle protrudes above the probe inlet. |
Criteria Met. No obstacles. |
| Spacing from Trees | To reduce possible interference the inlet must be at least 10 meters or further from the drip line of trees. |
Criteria Met. Approximately 10 meters to drip line. |
| Probe Material & Residence Time | Sampling train material must be FEP Teflon or borosilicate glass (e.g., Pyrex). |
Criteria Met. FEP Teflon. |