HomeMy WebLinkAboutAQ_AM_20230629_BP_AnnPln_Final 2023-2024 Appendix C Forsyth CountyPage -1-
May 25, 2023
Katy R. Lusky, Chief
Air Data and Analysis Section
Air Analysis and Support Branch/Air and Radiation Division
U.S. Environmental Protection Agency – Region 4
61 Forsyth Street, SW
Atlanta, GA 30303
Dear Ms. Lusky:
This letter and accompanying Annual Network Plan report on the status of the Ambient Air
Monitoring commitments for the FY-23 105 Grant Work plan for Forsyth County, North
Carolina (Reporting Organization 37-067). The entire Plan follows the Executive Summary,
complete with staff field reviews as well as a copy of the published public notice.
Sincerely,
Jason R. Bodenhamer, Program Manager
Analysis and Monitoring Division
Forsyth County Office of Environmental Assistance and Protection
Enclosures
cc:
Steve Lyda (FCEAP)
Minor Barnette (FCEAP)
Ryan Brown (EPA-Region IV)
Patrick Butler (NCDAQ)
Forsyth County
Office of Environmental Assistance and Protection
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Executive Summary
Submit by July 1, 2023 an evaluation to demonstrate the requirements of 40 CFR Part 58.10
(a)(1) (Annual Network Evaluation) have been met.
This review was conducted and submitted on May 25, 2023 to allow for the entire 30-day public comment
period to take place.
Quality Assurance Procedures.
This Office has received approval of the Criteria Pollutant QAPP on June 29,2022. Our current QMP was
approved on June 18, 2018 and this Office has submitted a new revision for approval on March 21, 2023.
We are currently working through the approval process with EPA so it will be in place by June 18, 2023.
SOPs are up to date and approved within our network including: SO2, NO2, Ozone, PM 2.5 (Cont. &
FRM), PM 10 and Course, Calibrators, Zero Air Supplies, and Data Handling.
Categorization of Ambient Monitors and Auxiliary Equipment.
The evaluation was completed in May, 2023. We currently have backup equipment for each monitoring
device stored in our office in the case of equipment failure. The current emphasis remains on
maintenance of the monitoring buildings and consolidation of the network. Capital funds are available in
limited quantity and are available for proper planning for future network needs.
Notify EPA within 30 days after exceedances/violations of NAAQS.
The Forsyth County Office of Environmental Assistance and Protection remained an active participant in
the AirNow program. Part of that program ensures that all local and regional exceedances/violations of
the NAAQS are submitted to EPA and all others affected in a timely fashion.
Comply with Exceptional Events Policy.
No situations requiring exceptional event flagging occurred since the last Annual Network Review period.
Submit list of urban areas for which AQI is reported.
Forsyth County reports the AQI for our part of the Greensboro-Winston-Salem-High Point MSA. AQI
statistics are available in local newspapers, on the Office’s web site at http://www.forsyth.cc/EAP/, Real
time data (updated hourly) are also available at: http://www.forsyth.cc/EAP/airmonitoringdata.aspx
Attend Region 4 QA Meeting & AIRS Conference.
The 2023 EPA Region 4 Ambient Monitoring Workshop was held this spring in Chattanooga, TN. All of
our division was able to attend, either in person or virtually. The virtual option was an added benefit to
our division.
Submit air quality forecasts for MSA's >500,000 population to EPA AIRNOW.
Forsyth County has been a leader in this area and submits air quality forecasts for multiple pollutants to
AIRNOW on a year-round basis. Several presentations on this program have been given at recent EPA
National Forecasting and Outreach Conferences.
Changes in the SLAMS/NAMS Network
There were no changes in our SLAMS network.
Data Submittal Criteria
All SLAMS and PARS data were submitted to AQS within 90 days of the end of each quarter. AQS data
reports were also reviewed after data submittal was completed to verify AQS data was correct. All data
was certified by May 1, 2023.
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National Performance Audit Program
All NPAP audits were completed by an EPA contractor and the results were submitted into AQS.
Continued-Annual Network Evaluation
Forsyth County has continued to review the local monitoring network to account for changes in
population, land use, and traffic patterns.
OZONE
The maximum impact downwind site is operated by the State program in Rockingham County (Bethany
School, 37-157-0099). The secondary wind direction is measured by the Union Cross site (37-067-1008).
In addition, the Clemmons Middle site (37-067-0030), established in 2005, monitors the southwest sector
of Forsyth County. Another ozone monitor at Hattie Avenue (37-067-0022) has operated since 1993.
CARBON MONOXIDE
We no longer operate a CO monitor. The most recently run microscale Peters Creek site (37-067-0023)
was shut down December 31, 2015.
SULFUR DIOXIDE/NITROGEN OXIDES
Sulfur dioxide levels have been measured at the Hattie Avenue site (37-067-0022) since 1983. Readings
are considered to be characteristic of background levels in Forsyth County. On occasion, the site is
impacted by plume touchdowns from the Duke Energy Belews Creek Generating Station located
approximately 20 miles to the northeast in Stokes County. In compliance with the most recent monitoring
data requirements, 5-minute SO2 averaged data from this site is reported along with 1-hour data.
Nitrogen oxide levels have been measured at the Hattie Avenue site (37-067-0022) since 1984. Readings
represent the neighborhood impact of major transportation related emissions from inter-city and intra-city
traffic on Business I-40 and U.S. 52 bisecting Winston-Salem. Both monitors satisfy the most recent
monitoring criteria related to the 1-hour SO2 and NO2 standards.
PARTICULATE
Continuous PM 2.5 (TAPI 640X) concentrations continue to be recorded at the Hattie Avenue site (37-
067-0022) and the Clemmons Middle site (37-067-0030) collects continuous PM 2.5 with a (T640),
These readings are representative of a maximum impact particulate site influenced by background
emissions and locally generated transportation emissions.
FRM STATUS
FRM PM2.5 samplers have been established at Hattie Avenue (37-067-0022); 1/3 frequency and the
Clemmons Middle site (37-067-0030); 1/6 frequency collocated with FRM samplers (ref meth 145) as
part of Forsyth County’s EPA approved PM2.5 monitoring plan. Due to the shutdown of the state lab,
RTI is the new lab, which started in July of 2021.
CONTINUOUS STATUS
A continuous PM2.5 TAPI 640x sampler runs at the Hattie Avenue site. This unit measures PM 2.5, CR,
and 10 (STP). The data set from the new 640x continues to indicate a good correlation between the FRM
PM2.5 data and 24-hour averages but is slightly higher. An additional PM2.5 (only) TAPI 640 unit is
operated at the Clemmons Middle site (37-067-0030).
SPECIATION STATUS
A speciated PM2.5 monitor (1/6 frequency) began operation on September 22, 2001 and a carbon
speciated PM2.5 monitor (1/6 frequency) began operation on February 28, 2007 at Hattie Avenue.
Validated data sets have been received from RTI through March 2023.
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AIR TOXICS
A (1/6) day air toxic sampler operated in conjunction with the NCDAQ has been resident at the Hattie
Avenue site since 2000. Air toxic data remains under NCDAQ control. This Office does not review or
upload this data to AQS.
LEAD
No lead monitors are currently in place at any sites within Forsyth County. Based on the interpretation of
the lead monitoring requirements, recent population data, and recent source emission inventory data, there
are no sources that emit more than 700 lbs of lead per year. Therefore, there are no immediate plans for
lead monitoring in the County.
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2023 Annual Monitoring Network Plan
Forsyth County
Office of Environmental Assistance and Protection
♥ Forsyth County Office of Environmental Assistance and Protection
201 North Chestnut Street, 5th Floor
Winston-Salem, NC 27101
Phone 336-703-2440 • Fax 336-727-2777
May 25, 2023
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CERTIFICATION
By the signatures below, the Forsyth County Office of Environmental Assistance and Protection
(FCEAP) certifies that the information contained in the 2023 Annual Monitoring Network Plan
is complete and accurate at the time of submittal to EPA Region 4. However, due to
circumstances that may arise during the sampling year, some network information may change.
A notification of change and a request for approval will be submitted to EPA Region 4 at that
time.
Print Name: Jason R.Bodenhamer Signature:Date: 5/25/23
Program Manager, Analysis and Monitoring Division, FCEAP
Print Name: W. Minor Barnette Signature: Date: 5/25/23
Director, FCEAP
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2023 ANNUAL MONITORING NETWORK PLAN
TABLE OF CONTENTS
EXECUTIVE SUMMARY 3
CERTIFICATION 7
2019 ANNUAL MONITORING NETWORK PLAN 8
INTRODUCTION 9
SITE DESCRIPTION BACKGROUND INFORMATION AND DEFINITIONS 10
1. Site Description 10
2. Date Established 10
3. Site Approval Status 10
4. Monitoring Objectives 10
5. Monitoring Stations’ Designations 10
SLAMS 11
NAMS 11
SPM 11
NCORE 11
6. Monitoring Methods 11
Particulate Matter 10 microns in size (PM10) 12
Particulate Matter 2.5 microns in size (PM2.5) 12
Particulate Matter 10-2.5 microns in size (PM10-2.5) 12
PM2.5 Speciation sampling and analysis 12
Sulfur Dioxide 12
Ozone 13
Nitrogen Dioxide 13
Air Toxics 13
7. Quality Assurance Status 13
8. Scale of Representativeness 13
9. Data Processing and Reporting 14
Network Summary 15
1. Site Table and Criteria Pollutants Monitored 15
2. Site Map 16
3. Monitoring Methods 17
AIR MONITORING STATION DESCRIPTIONS 18
1. Clemmons Middle School 18
(a) Site Table 18
(b) Site Description and Statement of Purpose 18
(c) Site Photographs 19
2. Hattie Avenue 20
(a) Site Table 20
(b) Description and Statement of Purpose 20
(c) Site Photographs 23
3. Union Cross 24
(a) Site Table 24
(b) Site Description and Statement of Purpose 24
(c) Site Photographs 25
REFERENCES 26
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INTRODUCTION
The Forsyth County Office of Environmental Assistance and Protection’s (FCEAP) monitoring
program provides air quality monitoring services in Forsyth County, NC. FCEAP is a state
“certified local air pollution program” whose purpose(s) are to improve and maintain ambient air
quality and reduce exposure to unhealthful air pollutants.
FCEAP has operated an air quality monitoring program since the early 1970’s. The air
monitoring services provided by the program are conducted to measure concentrations of criteria
air pollutants (NO2, SO2, PM, and O3) in accordance with USEPA regulatory requirements.
Measurements are used to assess compliance with National Ambient Air Quality Standards
(NAAQS). The NAAQS define air pollutant concentration level thresholds judged necessary to
protect the public health and welfare.
The FCEAP air monitoring program operates a network of state and local air monitoring stations
(SLAMS) in Forsyth County. The current network configuration consists of seven monitoring
stations that measure concentrations of criteria air pollutants. In addition to the SLAMS network
the county network also includes monitoring for meteorological parameters and visibility
conditions.
The annual monitoring network plan, as provided for in 40 CFR Part 58.10, Annual Monitoring
Network Plan and Periodic Network Assessment must contain the following information for each
monitoring station in the network:
1. The Air Quality System (AQS) site identification number for existing stations.
2. The location, including the street address and geographical coordinates, for each monitoring
station.
3. The sampling and analysis method used for each measured parameter.
4. The operating schedule for each monitor.
5. Any proposal to remove or move a monitoring station within a period of eighteen months
following the plan submittal.
6. The monitoring objective and spatial scale of representativeness for each monitor.
7. The identification of any sites that are suitable and sites that are not suitable for comparison
against the annual PM2.5 NAAQS.
8. The Metropolitan Statistical Area (MSA), Core-Based Statistical Area (CBSA), Combined
Statistical Area (CSA) or other area represented by the monitor.
The following information below replicates the Forsyth County Air Quality ambient air
monitoring network plan and continues in the following sections outlined below:
II. Site Description Background Information and Definitions: An outline of the designations,
parameters, monitoring methods, and the basis for site selection.
III. Network Summary: This section presents an overview of the total number of sites and
monitors in Forsyth County. Also included is a listing of all proposed changes to the current
network.
IV. Air Monitoring Station Description: Each air monitoring station is described in detail as
per the outline in (II.) above. Modification to the network as determined by an annual review
process will be made each year to maintain a current up-to-date network description document.
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Site Description Background Information and Definitions
1. Site Description
Specific information is provided to show the location of the monitoring equipment at the site, if
the site is located in a CSA/MSA, the AQS identification number, the GPS coordinates, and
evidence that monitors and monitor probes conform to the siting criteria.
2. Date Established
The date when each existing monitoring station was established is shown in the description. For
those stations, which are proposed, a date is provided when it is expected for the station to be in
operation.
3. Site Approval Status
Each monitoring station in the existing network has been reviewed with the purpose of
determining whether it meets all design criteria for inclusion in the SLAMS network. Stations
that do not meet the criteria will either be relocated in a nearby area or, when possible, re-sited at
the present location.
4. Monitoring Objectives
Per 40 CFR 58 Appendix D, Section 1.1:
“The ambient air monitoring networks must be designed to meet three basic monitoring
objectives. These basic objectives are listed below. The appearance of any one objective in the
order of this list is not based upon a prioritized scheme. Each objective is important and must be
considered individually.”
The objectives are summarized below:
(a) Provide air pollution data to the general public in a timely manner.
(b) Support compliance with ambient air quality standards and emissions strategy development.
Data from FRM (Federal Reference Method), FEM (Federal Equivalent Method), and ARM
(Approved Regional Method) monitors for NAAQS pollutants will be used for comparing an
area’s air pollution levels against the NAAQS.
(c) Support for air pollution research studies.
5. Monitoring Stations’ Designations
Most stations described in the air quality surveillance network are designated as State and Local
Air Monitoring Stations (SLAMS). In addition, some of these stations fulfill other
requirements, which must be identified. In this description of the network, designations are also
made for National Air Monitoring Stations (NAMS), Special Purpose Monitors (SPM), and
National Core (community oriented) stations (NCore). The following is the criteria used for
each of these designations.
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SLAMS
Requirements for air quality surveillance systems provide for the establishment of a network of
monitoring stations designated as State and Local Air Monitoring Stations (SLAMS) that
measure ambient air concentrations of those pollutants for which standards have been
established. These stations must meet requirements that relate to four major areas: quality
assurance, monitoring methodology, sampling interval and siting of instruments and instrument
probes.
NAMS
Within the SLAMS network certain monitors are selected to provide the USEPA with timely
data for use in national trends analysis. These NAMS monitors are identified in the summary of
network stations.
SPM
Not all monitors and monitoring stations in the air quality surveillance network are included in
the SLAMS network. In order to allow the capability of providing monitoring for various
reasons such as: special studies, modeling verification and compliance status, and other
objectives; certain monitors are designated as Special Purpose Monitors (SPM). These monitors
are not committed to any one location or for any specified time period. They may be located as
separate monitoring stations or be included at SLAMS locations. Monitoring data may be
reported, provided that the monitors and stations conform to all requirements of the SLAMS
network.
NCORE
National Core (community-oriented) multi-pollutant monitoring station data will be used to
evaluate the regional air quality models used in developing emission strategies, and to track
trends in air pollution abatement control measures’ impact on improving air quality.
6. Monitoring Methods
Sampling and analytical procedures for criteria air pollutant monitoring performed in the FCEAP
ambient air monitoring network are conducted in accordance with applicable USEPA Designated
Federal Reference (FRM) or Equivalent (FEM) Methods unless otherwise noted. Analytical
techniques for non-criteria air pollutant monitoring (methods employed that are not USEPA
Designated Federal Reference (FRM) or Equivalent (FEM) Methods) are documented in the
applicable FCEAP Quality Assurance Project Plans (QAPP), FCEAP Standard Operating
Procedures (SOP), or the appropriate North Carolina Division of Air Quality (NCDAQ) QAPP
or SOP. Methods used by FCEAP for criteria pollutant monitoring are listed below:
Particulate Matter 10 microns in size (PM10)
All PM10 samplers operated by FCEAP are operated as federal reference method (FRM) or
equivalent samplers and are operated according to the requirements set forth in 40 CFR 50 and
40 CFR 53. Listed below is the USEPA Designated Reference or Equivalent Method used in
the FCEAP monitoring network:
Method Designation Number Method Code
T640 PM Mass Monitor w/640X Option EQPM-0516-239 239
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Particulate Matter 2.5 microns in size (PM2.5)
With the exception of speciation samplers, all PM2.5 samplers operated by FCEAP are either
FRM or FEM samplers. Listed below is the USEPA Designated Reference or Equivalent
Method used in the FCEAP monitoring network:
Method Designation Number Method Code
R & P Partisol-Plus 2025i PM-2.5 Seq.
EQPM-0202-145
145
T640 PM Mass Monitor w/640X Option
EQPM-0516-238
238
TAPI Model T640 PM Mass Monitor
EQPM-0516-236
236
Particulate Matter 10-2.5 microns in size (PM10-2.5)
With the exception of speciation samplers all PM2.5 samplers operated by FCEAP are either FRM
or FEM samplers. Listed below is the USEPA Designated Reference or Equivalent Method used
in the FCEAP monitoring network:
Method Designation Number Method Code
T640 PM Mass Monitor w/640X Option EQPM-0516-240 240
PM2.5 Speciation sampling and analysis
In addition to operating PM2.5 samplers that determine only PM2.5 mass values, FCEAP also
operates PM2.5 speciation samplers that collect samples that are analyzed to determine the
chemical makeup of PM2.5. Data collected using this method cannot be compared to the
NAAQS. Listed below is the method used in the FCEAP monitoring network:
Method Designation Number Method Code
MetOne SASS
URG
NA
NA
NA
NA
Sulfur Dioxide
Instruments used to continuously monitor sulfur dioxide levels in the atmosphere employ the
pulsed UV fluorescence method. Listed below is the USEPA Designated Reference or
Equivalent Method used in the FCEAP monitoring network:
Method Designation Number Method Code
Teledyne API T100U EQSA-0495-100 600
Ozone
Ozone is monitored using the UV photometry method. Listed below is the USEPA Designated
Reference or Equivalent Method used in the FCEAP monitoring network:
Method Designation Number Method Code
TAPI. Model 400E, T400 EQOA-0992-087 087
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Nitrogen Dioxide
The chemiluminescence method is used in monitoring the nitrogen dioxide level in the ambient
air. Listed below is the USEPA Designated Reference or Equivalent Method used in the
FCEAP monitoring network:
Method Designation Number Method Code
TAPI Model 200EU, T200U RFNA-1194-599 599
Air Toxics
Air toxics sampling is conducted in Forsyth County using equipment on loan from the State of
North Carolina, Division of Air Quality. Due to staffing issues, the State of NC has put the
toxics program on hold for a 6-month period. They are planning to update the equipment as well
during this time. Listed below is the USEPA Designated Reference or Equivalent Method used
in the FCEAP monitoring network:
Method Designation Number Method Code
Compendium Method for Toxic Organics Compendium Method
TO-15
150
7. Quality Assurance Status
FCEAP has an extensive quality assurance procedure to ensure that all air monitoring data
collected meets established criteria for precision and accuracy. FCEAP operates according to
EPA approved Quality Assurance Project Plans (QAPP) and Standard Operating Procedures.
Staff members audit instrumentation on a scheduled basis to ensure that each instrument is
calibrated and operating properly. Data validation is performed monthly to ensure data reported
by each instrument is recorded accurately in the air quality monitoring database.
8. Scale of Representativeness
Each station in the monitoring network must be described in terms of the physical dimensions of
the air parcel nearest the monitoring station throughout which actual pollutant concentrations are
reasonably similar. Area dimensions or scales of representativeness used in the network
description are:
(a) Microscale - defines the concentration in air volumes associated with area dimensions
ranging from several meters up to about 100 meters.
(b) Middle scale - defines the concentration typical of areas up to several city blocks in size with
dimensions ranging from about 100 meters to 0.5 kilometers.
(c) Neighborhood scale – defines concentrations within an extended area of a city that has
relatively uniform land use with dimensions ranging from about 0.5 to 4.0 kilometers.
(d) Urban scale - defines an overall citywide condition with dimensions on the order of 4 to 50
kilometers.
(e) Regional Scale - defines air quality levels over areas having dimensions of 50 to hundreds of
kilometers.
Closely associated with the area around the monitoring station where pollutant concentrations are
reasonably similar are the basic monitoring exposures of the station. There are six basic
exposures:
(a) Sites located to determine the highest concentrations expected to occur in the area covered by
the network.
(b) Sites located to determine representative concentrations in areas of high population density.
(c) Sites located to determine the impact on ambient pollution levels of significant sources or
source categories.
(d) Sites located to determine general background concentration levels.
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(e) Sites located to determine the extent of regional pollutant transport among populated areas;
and in support of secondary standards.
(f) Sites located to measure air pollution impacts on visibility, vegetation damage, or other
welfare-based impacts.
The design intent in siting stations is to correctly match the area dimensions represented by the
sample of monitored air with the area dimensions most appropriate for the monitoring objective
of the station. The following relationship of the six basic objectives and the scales of
representativeness are appropriate when siting monitoring stations:
Site Type Appropriate Siting Scales
1. Highest concentration Micro, middle, neighborhood (sometimes
urban or regional for secondarily formed
pollutants).
2. Population oriented Neighborhood, urban.
3. Source impact Micro, middle, neighborhood.
4. General/background & regional transport Urban, regional.
5. Welfare-related impacts Urban, regional.
Table 1 - Siting Objectives and Scales
9. Data Processing and Reporting
All ambient air quality data are stored on the Achilles Server managed by the Forsyth County
MIS (IT) department located on the 3rd floor of the Forsyth County Government Center, FCEAP,
201 N. Chestnut Street, Winston-Salem, North Carolina. The AirVision SQL based database is
accessed from computers located on the 5th floor of the Forsyth County Government Center,
FCEAP, 201 N. Chestnut Street, Winston-Salem, North Carolina. On a daily basis, All data are
backed up and maintained at an off-site location. After all monthly data validation procedures
are successfully completed, data is transmitted to the USEPA’s national Air Quality System
(AQS) database. The AQS database is maintained by EPA as the official repository of the fully
quality assured ambient air quality dataset.
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Network Summary
1. Site Table and Criteria Pollutants Monitored
Site AQS ID # CO NO2 O3 Pb PM2.5 PM10 SO2 Air
Toxics
Clemmons Middle
School 37-067-0030 X X
Hattie Avenue A&B 37-067-0022 X X X X X X
Union Cross 37-067-1008 X
Table 2 - Forsyth County Monitoring Sites
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2. Site Map
AIR QUALITY MONITORING STATIONS
FORSYTH COUNTY, NC 2023
Figure 1 - Forsyth County Monitor Locations
3. Monitoring Methods
Site Parameter Instrument /
Method
Method
Number
Parameter
Number
Monitor
Type†
Serial
Number
Purchase
Date
Replace
Date
Condition
37-067-0022 Ozone UV
Photometric 087 44201 SLAMS 6414 2017 2027 Good
37-067-0022 SO2 Pulsed UV
Fluorescent 600 42401 SLAMS 179 2017 2027 Good
37-067-0022 NO Chemi-
luminescence 599 42601 SLAMS T200U-214 2017 2027 Good
37-067-0022 NO2 Chemi-
luminescence 599 42602 SLAMS T200U-214 2017 2027 Good
37-067-0022 NOx Chemi-
luminescence 599 42603 SLAMS T200U-214 2017 2027 Good
37-067-0022 Air Toxics
Compendium
Method for
Toxic Organics
(TO) 15
150 Multiple NON
4518
NCDENR
Owned 3603
37-067-0022 PM2.5 FRM 145 88101 SLAMS 2025I203541
302 2014 2024 Good
37-067-0022 PM2.5 Speciation 118 Multiple SLAMS A2591 2001 2024 Good
37-067-0022 PM2.5 T640x 238 88101 SLAMS 96 2017 2027 Good
37-067-0022 PM2.5CR T640x 240 86101 SLAMS 96 2017 2027 Good
37-067-0022 PM2.5 Carbon
Speciation 118 88101 SLAMS 3NB0191 2007 2024 Good
37-067-0022 PM10 T640x 239 81102 SLAMS 96 2017 2027 Good
37-067-0030 Ozone UV
Photometric 087 44201 SLAMS 3093 2018 2028 Good
37-067-0030 PM2.5 T640 236 88101 SLAMS 145 2017 2027 Good
37-067-0030 PM2.5 FRM 145 88101 SLAMS 2025B21708
0407 2010 2020 Good
37-067-1008 Ozone UV
Photometric 087 44201 SLAMS 4060 2018 2028 Good
37-067-1008 Temp Climatronics 020 61101 SLAMS 2016 2026 Good
37-067-1008 Humidity Climatronics 020 61103 SLAMS 2016 2026 Good
37-067-1008 WD Climatronics 020 61104 SLAMS 102779 2016 2026 Good
37-067-1008 WS Climatronics 020 61103 SLAMS 102779 2016 2026 Good
37-067-1008 Pressure Climatronics 011 64101 SLAMS 2016 2026 Good
Table 3 - Forsyth County Monitoring Methods
†- Monitor Type:
SLAMS- State and Local Air Monitoring Station
SPM- Special Purpose
NON- Non-regulatory
TRENDS- Trends Speciation
Air Monitoring Station Descriptions
1. Clemmons Middle School
(a) Site Table
Site Name: Clemmons Middle School
AQS Site Id #: 37-067-0030
Location: Fraternity Church Road
Winston-Salem, NC
Latitude: N 36.026612
Longitude: W 80.341962
Elevation: 245 meters
Date Monitor Established: Ozone April 27, 2005
Date Monitor Established: PM2.5 T640 Jan. 1, 2018
Date Monitor Established: PM2.5 FRM Oct 1, 2018
Nearest Road: Fraternity Church Road Distance to Road: 40 meters
Traffic Count3: 4400 Year of Count: 2017
MSA4: Winston-Salem, NC
Metropolitan Statistical Area MSA #: 49180
Parameter Method Method Number Sampling Schedule
Ozone UV Photometric 087 March 1 – Oct. 31,
(Continuous)
PM2.5 T640 236 Continuous
PM2.5 FRM Gravimetric 145 1/6 day
Table 4 - Clemmons Middle School Monitoring Station Summary
(b) Site Description and Statement of Purpose
An ozone monitor and PM2.5 continuous monitor have been located at a manufactured structure
since April 27, 2005. The site is located in a mixed use environment at latitude N36.025931º and
longitude W80.342257º. The site elevation is 245 meters above sea level. The nearest road is
Fraternity Church Road with an annual traffic volume of 4100 vehicles (2017) at a distance of 40
meters from the sample inlet.
The inlet of the samplers is approximately 3 meters above ground level and 1 meter above roof
level. There were trees encroaching on the minimum distance from the inlet and those trees were
removed during the summer of 2015. The last official site evaluation was completed in October
2022. The area is a transition zone of business (~50%) to residential (~50%) within a 1 km
radius. The samplers are SLAMS.
The ozone instrument is operated during the North Carolina ozone monitoring season which
begins March 1 and ends October 31. The ozone instrument operates continuously during this
period.
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OBJECTIVE AND SPATIAL SCALE
The monitoring objectives of the instruments are to measure: 1) upwind background ambient
concentrations and 2) population exposure.
The site is a neighborhood spatial scale for ozone and PM2.5. Data from this site is used to assess
compliance with the NAAQS for ozone and PM2.5.
The site is located in the Winston-Salem, NC Metropolitan Statistical Area4. The principal cities
and counties in the MSA are Winston-Salem, Davie County, Forsyth County, Stokes County,
and Yadkin County, NC.
(c) Site Photographs
NORTH EAST
SOUTH WEST
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2. Hattie Avenue
(a) Site Table
Site Name: Hattie Avenue (Two buildings {A & B} at one location)
AQS Site Id #: 37-067-0022
Location: 1300 Hattie Avenue
Winston-Salem, NC
Latitude: N 36.110940
Longitude: W 80.224501
Elevation: 284 meters
Date Monitor Established: Ozone May 21, 1993
Date Monitor Established: NO2 January 1, 1984
Date Monitor Established SO2 January 1, 1983
Date Monitor Established: PM2.5 – FRM January 1, 1999
Date Monitor Established: PM2.5 - PM10 - PM10-2.5 January 1, 2018
Date Monitor Established: Air Toxics January 1, 2000
Date Monitor Established: Speciation January 1, 2001
Date Monitor Established: Carbon Speciation January 1, 2007
Nearest Road: Hattie Avenue Distance to Road: 27 meters
Traffic Count3: 6000 Year of Count: 2017
MSA4: Winston-Salem, NC
Metropolitan Statistical Area MSA #: 49180
Parameter Method Method Number Sampling Schedule
Ozone UV Photometric 087 March 1 – Oct. 31,
(Continuous)
NO2 Chemiluminescence 599 Continuous
SO2 UV Pulsed Fluorescence 560 Continuous
PM2.5 FRM FRM Gravimetric 145 1/3 day
PM2.5 PM10 PM10-2.5 T640x, Continuous 238-239-240 Continuous
Air Toxics Compendium Method for
Toxic Organics (TO) 15 150 1/6 day
Speciation MET-one 118 1/6 day
Carbon Speciation URG Sampler 118 1/6 day
Table 5 - Hattie Avenue "A" Monitoring Station Summary
(b) Description and Statement of Purpose
The Hattie Avenue A site monitors ozone, sulfur dioxide, oxides of nitrogen, PM2.5, PM10, PM 10-
2.5, toxics, speciation, and carbon speciation. The site is located in the 1300 block of Hattie
Avenue in downtown Winston-Salem. The site is located approximately 2.2 km NE of
downtown, 1.1 km E of US52 and approximately 1.8 km NNW of Interstate 40 Business in a
residential district at latitude N36.110941º and longitude W80.224423º. The site elevation is 284
meters. The nearest road, Hattie Avenue, is 27 meters from the inlets and has a daily traffic flow
of 6000 vehicles (2017). The nearest tallest building is St. Benedict’s Church (approximately 10
meters). The inlets are approximately 43 meters from the building. The inlets are approximately
4 meters above the ground and 1 meter above the roof of the monitoring station. The last official
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site evaluation was completed in October 2022. The area is residential. The ozone, sulfur
dioxide, and NO2 monitors are all SLAMS.
The ozone instrument is operated during the North Carolina ozone monitoring season which
begins March 1 and ends October 31. The ozone instrument operates continuously during this
period.
The SO2 and NO2 instruments operate continuously.
The PM2.5, PM10, and PM10-2.5 T640x instruments operate continuously.
The PM2.5 primary monitor is a continuous sampler and the co-located FRM is on the 1 in 3 day
schedule. The FRM sampling interval is 24 hours, from midnight to midnight every third day.
The PM2.5 Speciation sampling frequency is 1 in 6 days. The sampling interval is 24 hours, from
midnight to midnight every six days.
Monitoring for Urban Air Toxics (UAT) is currently conducted at this site by the North Carolina
Division of Air Quality (NC-DAQ), Toxics Protection Branch (TPB). Currently, the NC-DAQ
TPB collects whole air samples in stainless steel 6 liter- pressurized canisters. The samples are
then analyzed using cryogenic preconcentration gas chromatography with mass spectrometric
detection (GC/MS) via the Compendium Method for Toxic Organics (TO) 15 for the list of 68
compounds (below).
• Propene
• Freon 12
• Freon 22
• Freon 114
• Chloro Methane
• (Methylchloride)
• Isobutene
• Vinyl chloride
• 1,3-Butadiene
• Bromomethane
• Chloroethane
• Freon 11
• Pentane
• Ethanol
• Isoprene
• Acrolein
• 1,1-Dichloroethene
• (Vinylidene chloride)
• Freon 113
• Methyl Iodide
• Isopropyl Alcohol
• Carbon Disulfide
• Acetonitrile
• Methylene chloride
• Cyclopentane
• MTBE
• Hexane
• Methacrolein
• Vinyl Acetate
• 1,1-Dichloroethane
• Methyl Vinyl Ketone
• Methyl Ethyl Ketone
• 1,2 Dichloroethene
• Chloroform
• 1,1,1-Trichloroethane
• (Methyl chloroform)
• Cyclohexane
• Carbon Tetrachloride
• Benzene
• 1,2-Dichloroethane
• (ethylene dichloride)
• 1-Butanol
• Trichloroethylene
• 2-Pentanone
• 3-Pentanone
• 1,2-Dichloropropane
• 1,4-Dioxane
• Bromodichloromethane
• trans-1,3 Dichloropropene
• Methyl Isobutyl Ketone
• Toluene
• cis-1,3 Dichloropropene
• 1,1,2-Trichloroethane (vinyl
trichloride)
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• Ethylpropylketone
• Tetrachloroethylene
• (perchloroethylene)
• Methyl Butyl Ketone
• Dibromoethane
• Chlorobenzene
• (phenylchloride)
• Ethylbenzene
• m- & p-Xylene
• o-Xylene
• Styrene
• Bromoform
• 1,1,2,2-Tetrachloroethane
• 1,3,5-Trimethylbenzene
• (mesitylene)
• 1,2,4-Trimethylbenzene
• (pseudocumene)
• m-Dichlorobenzene
• 1,2,3-Trimethylbenzene
• p-Dichlorobenzene
• Benzylchloride
• o-Dichlorobenzene
• 1,2,4-Trichlorobenzene
The site complies with the siting requirements of 40CFR58 for criteria air pollutants. It is
recommended that the current site status be maintained.
OBJECTIVE AND SPATIAL SCALE
The monitoring objectives of the instruments are to measure: 1) background ambient
concentrations and 2) population exposure.
The site is a neighborhood spatial scale. Data from this site is used to assess compliance with the
NAAQS for ozone, sulfur dioxide, and nitrogen dioxide.
The site is located in the Winston-Salem, NC Metropolitan Statistical Area4. The principal cities
and counties in the MSA are Winston-Salem, Davie County, Forsyth County, Stokes County,
and Yadkin County, NC.
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(c) Site Photographs
NORTH (unable to update due to locked gate) EAST
SOUTH WEST
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3. Union Cross
(a) Site Table
Site Name: Union Cross
AQS Site Identification
Number: 37-067-1008
Location: 3656 Piedmont Memorial Drive
Winston-Salem, NC
Latitude: N 36.051805
Longitude: W 80.144933
Elevation: 285 meters
Date Monitor Established: Ozone April 1, 1998
Nearest Road: Piedmont Memorial Dr. Distance to Road: 55 meters
Traffic Count3: 670 Year of Count: 2017
MSA4:
Winston-Salem, NC
Metropolitan Statistical
Area (2006)
MSA #: 49180
Parameter Method Method Number Sampling Schedule
Ozone UV Photometry 087 March 1 – October 31
(Continuous)
Wind Speed Climatronics 020 Continuous
Wind Direction Climatronics 020 Continuous
Pressure Climatronics 011 Continuous
Outdoor Temperature Climatronics 020 Continuous
Relative Humidity Climatronics 020 Continuous
Table 6 - Union Cross Monitoring Station Summary
(b) Site Description and Statement of Purpose
An ozone monitor has been located at this site since April 1, 1998 along with a meteorological
tower since 1997. The site is located approximately 10 km SE of the central business district at
latitude 36.050746° and longitude -80.143826°. The site elevation is 285 meters above sea level.
The nearest road is Piedmont Memorial Drive with an annual traffic volume of 670 vehicles
(2017) at a distance of 55 meters from the sample inlet.
The inlet is approximately 3 meters above the ground and 1 meter from the roof. The last
official site evaluation was completed in October 2022. The area is residential. The ozone
sampler is SLAMS.
The ozone instrument is operated during the North Carolina ozone monitoring season which
begins March 1 and ends October 31. The ozone instrument operates continuously during this
period.
The site complies with the siting requirements of 40CFR58 for criteria air pollutants. There are
no proposed changes for this site. It is recommended that the current site status be maintained.
All equipment has been moved from the old building (green exterior) to the new building (white
exterior). The old building will be moved from this location and disposed of.
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OBJECTIVE AND SPATIAL SCALE
The monitoring objective of the instrument is to measure population exposure.
The site is a neighborhood spatial scale for ozone. Data from this site is used to assess
compliance with the NAAQS for ozone.
The site is located in the Winston-Salem, NC Metropolitan Statistical Area4. The principal cities
and counties in the MSA are Winston-Salem, Davie County, Forsyth County, Stokes County,
and Yadkin County, NC.
(c) Site Photographs
NORTH EAST
SOUTH WEST
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References
1. Title 40 Code of Federal Regulations Part 58, Ambient Air Quality Surveillance. Part 58 and
Part 58 Amended: Federal Register/Vol. 71 No. 200/Tuesday, October 17, 2006/Rules and
Regulations.
2. Watson, John G., Chow, Judith C., DuBois, David, Green, Mark, Frank, Neil, Pitchford,
Marc. Guidance for Network Design and Optimum Site Exposure for PM2.5 and PM10. Office
of Air Quality Planning and Standards, U. S. Environmental Protection Agency, Research
Triangle Park, NC 27711. December 15, 1997.
3. Winston-Salem Department of Transportation. Current Traffic Counts
Note: Traffic Count taken from nearest road providing most impact to site
4. US Census Bureau. Current Lists of Metropolitan and Micropolitan Statistical Areas and
Definitions. http://www.census.gov/population/metro/data/index.html .
(301) 763-2419. 2006.
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2022 Annual Monitoring Network Plan
Appendix A
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