# Ambient Air Monitoring Plan

20 1 1

Chattanooga/Hamilton County Air Pollution Control Bureau

Knox County Health Department, Department of Air Quality Management

Memphis/Shelby County Health Department, Air Pollution Control Program

Metropolitan Health Department, Division of Air Pollution Control

Tennessee Dept. of Environment and Conservation, Air Pollution Control Division



# July 1 , 20 1 1

## 2 Table of Contents

Section P age 

## Introduction to the 2011 Ambient Air Monitoring Plan for Tennessee

................................ ......................... 3 Tennessee Geographic Regions and Descriptions

................................ ................................ .......................... 6 Tennessee Geographic Regions

................................ ................................ ................................ ...................... 9 Climate Synopsis for Tennessee

................................ ................................ ................................ ................... 10

Windrose Data for Tennessee

................................ ................................ ................................ ...................... 11 Tennessee Metropolitan and Micropolitan Statistical Areas and Population Data

................................ ..... 12 Tennessee County Population Density

................................ ................................ ................................ ......... 13 Monitoring Equipment Evaluation for Tennessee Air Pollution Control Divisio n

................................ ........ 15 The Purpose of Tennessee’s Ambient Air Monitoring Network

................................ ................................ .. 16 Ozone monitoring network requirements

................................ ................................ ................................ .................. 18

PM 2.5 monitori ng network requirements

................................ ................................ ................................ ................. 18 PM 10 monitoring network requirements

................................ ................................ ................................ .................. 19 SO2 monitoring network requirements

................................ ................................ ................................ ..................... 19 NO2 monitoring network requirements

................................ ................................ ................................ ..................... 21 Lead monitoring n etwork requirements

................................ ................................ ................................ ..................... 21 CO monitoring network requirements

................................ ................................ ................................ ....................... 22 Index reporting requirements

................................ ................................ ................................ ................................ ..... 23 NCore monitoring network requirements and PM 10

- 2.5

................................ ................................ ......................... 23



## N Core Monitoring In Tennessee

................................ ................................ ................................ ................... 25

Nashville

- Davidson

-- Murfreesboro, TN MSA Area

................................ ................................ ....................... 39 Memphis, TN

- MS

- AR Area

................................ ................................ ................................ ............................ 45 Knoxville, TN Area

................................ ................................ ................................ ................................ ........ 49 Chattanooga, TN

- GA Area

................................ ................................ ................................ ............................ 57 Kingsport Bristol Johnson City Area

................................ ................................ ................................ ............. 61 Clarksville, TN

- KY Area

................................ ................................ ................................ ................................ .. 65
Morristown, TN Area

................................ ................................ ................................ ................................ .... 69 Jackson, TN Area

................................ ................................ ................................ ................................ ........... 73

Cleveland , TN Area

................................ ................................ ................................ ................................ ....... 77 Monitoring Sites Located In MSA/CBSA Areas In Tennessee

................................ ................................ ....... 81 Monitoring Sites Located In Non

- MSA/CBSA Areas In Tennessee

................................ ............................... 82 Agreement Letters with Agencies Outside of Tennessee

................................ ................................ ............ 90 Appendix 1: MSA Monitoring Agreements Prepared by Kentucky and Tennessee for Ozone and Continuous PM2.5 Monitoring

................................ ................................ ................................ ................................ ..................... 91 Appendix 2: MSA Monitoring Agreements for Memphis and Shelby County Health Department and the states of Arkansas and Mississippi

................................ ................................ ................................ ................................ .......... 94


## List of Attachments

................................ ................................ ................................ ................................ ...... 98 1 Chattanooga AMP

................................ ................................ ................................ ................................ .................... 1

2 Knoxville AMP

................................ ................................ ................................ ................................ ........................ 1

3 Memphis AMP

................................ ................................ ................................ ................................ ......................... 1

4 Nashville AMP

................................ ................................ ................................ ................................ ......................... 1

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# Introduction to the 2011 Ambient Air Monitoring Plan for Tennessee

The State of Tennessee is required to evaluate the ambient air monitoring network each year in accord ance with the requirements specified in 40 CFR Subpart B 58.10. The requirements that must be met in the annual evaluation are

included as follows:

§ 58.10 Annual monitoring network plan and periodic network assessment. (a) (1) Beginning July 1, 2007, t he State, or where applicable local, agency shall adopt and submit to the Regional Administrator an annual monitoring network plan which shall provide for the establishment and maintenance of an air quality surveillance system that consists of a network of SLAMS monitoring stations including FRM, FEM, and ARM monitors that are part of SLAMS, NCore stations, STN stations, State speciation stations, SPM stations, and/or, in serious, severe and extreme ozone nonattainment areas, PAMS stations, and SPM monitori ng stations. The plan shall include a statement of purposes for each monitor and evidence that siting and operation of each monitor meets the requirements of appendices A, C, D, and E of this part, where applicable. The annual monitoring network plan must be made available for public inspection for at least 30 days prior to submission to EPA. (2) Any annual monitoring network plan that proposes SLAMS network modifications including new monitoring sites is subject to the approval of the EPA Regional Administrator, who shall provide opportunity for public comment and shall approve or disapprove t he plan and schedule within 120 days. If the State or local agency has already provided a public comment opportunity on its plan and has made no changes subsequent to that comment opportunity, and has submitted the received comments together with the plan, the Regional Administrator is not required to provide a separate opportunity for comment. (3) The plan for establishing required NCore multipollutant stations shall be submitted to the Administrator not later than July 1, 2009. The plan shall provide for all required stations to be operational by January 1, 2011. (4) A plan for establishing Pb monitoring sites in accordance with the requirements of appendix D to this part shall be submitted to the EPA Regional Administrator no later than July 1, 2009 as part of the annual network plan required in paragraph (a)(1) of this section. The plan shall provide for the required source

oriented Pb monitoring sites to be operational by January 1, 2010, and for all required non

- source

- oriented Pb monitoring sites to be operational by January 1, 2011. Specific site locations for the sites to be operational by January 1, 2011 are not required as part of the July 1, 2009 annual network plan, but shall be included in the annual network plan due to be submitted to the EPA Regional Administrator on July 1, 2010. (5) A plan for establishing NO2 monitoring sites in accordance with the requirements of appendix D to this part shall be submitted to the Administrator by July 1, 2012. The plan shall provide for all required monito ring stations to be operational by January 1, 2013. (6) A plan for establishing SO2 monitoring sites in accordance with the requirements of appendix D to this part shall be submitted to the EPA Regional Administrator by July 1, 2011 as part of the annual network plan required in paragraph (a) (1). The plan shall provide for all required SO2 monitoring sites to be operational by January 1, 2013. (b) The annual monitoring network plan must contain the following information for each existing and proposed sit e: (1) The AQS site identification number. (2) The location, including street address and geographical coordinates. (3) The sampling and analysis method( s) for each measured parameter. (4) The operating schedules for each monitor

. (5) Any proposals to remove or move a monitoring station within a period of 18 months following plan

submittal. (6) The monitoring objective and spatial scale of representativeness for each monitor as defined in appendix D to this part. (7) The identification of any sites that are suitable and sites that are not suitable for comparison against the annual PM2.5 NAAQS as described in § 58.30.

## 4 (8) The MSA, CBSA, CSA or other area represented by the monitor. (9) The designation of any Pb mo nitors as either source

- oriented or non source

- oriented according to Appendix D to 40 CFR part 58. (10) Any source

- oriented monitors for which a waiver has been requested or granted by the EPA Regional Administrator as allowed for under paragraph 4.5(a)( ii) of Appendix D to 40 CFR part 58. (11) Any source

- oriented or non source

- oriented site for which a waiver has been requested or granted by the EPA Regional Administrator for the use of Pb

- PM10 monitoring in lieu of Pb

- TSP monitoring as allowed

for und er paragraph 2.10 of Appendix C to 40 CFR part 58. (12) The identification of required NO2 monitors as either near

- road or area

- wide sites in accordance with appendix D, section 4.3 of this part. (c) The annual monitoring network plan must document how S tates and local agencies provide for the review of changes to a PM2.5 monitoring network that impact the location of a violating PM2.5 monitor or the creation/change to a community monitoring zone, including a description of the proposed use of spatial ave raging for purposes of making comparisons to the annual PM2.5 NAAQS as set forth in appendix N to part 50 of this chapter. The affected State or local agency must document the process for obtaining public comment and include any comments received through t he public notification process within their submitted plan. (d) The State, or where applicable local, agency shall perform and submit to the EPA Regional Administrator an assessment of the air quality surveillance system every 5 years to determine, at a m inimum, if the network meets the monitoring objectives defined in appendix D to this part, whether new sites are needed, whether existing sites are no longer needed and can be terminated, and whether new technologies are appropriate for incorporation into the ambient air monitoring network. The network assessment must consider the ability of existing and proposed sites to support air quality characterization for areas with relatively high populations of susceptible individuals (e.g., children with asthma), and, for any sites that are being proposed for discontinuance, the effect on data users other than the agency itself, such as nearby States and Tribes or health effects studies. For PM2.5, the assessment also must identify needed changes to population

- orie nted sites. The State, or where applicable local, agency must submit a copy of this 5

- year assessment, along with a revised annual network plan, to the Regional Administrator. The first assessment is due July 1, 2010. (e) All proposed additions and disco ntinuations of SLAMS monitors in annual monitoring network plans and periodic network assessments are subject to approval according to § 58.14. [71 FR 61298, Oct. 17, 2006, as amended at 72 FR 32210, June 12, 2007; 73 FR 67059, Nov. 12, 2008; 73 FR 77517, Dec. 19, 2008; 75 FR 6534, Feb. 9, 2010]

The draft plan that is presented in the following pages will address each of the requirements specified in the CFR. An overview of the geography, general climate, wind patterns and population trends are included t o provide background information that will assist the reader in understanding the current air monitoring network and reasons for placement of the existing monitoring sites. The actual regulatory requirements that specify the number and placement of air

mon itoring sites is found in 40 CFR 58. The sections that provide this guidance are also included in the report as a reference to help better understand the actual monitoring needs in a given area.

In many instances, the ―areas‖ for which monitoring is requ ired are based on population criteria in which population must be considered to allow for monitoring in the areas where populations may be affected or exposed to the various criteria pollutants of concern. Additional monitoring sites are needed to address areas where source related emission density may be elevated and also impact communities in the same area. Other considerations must also be addressed when selecting and operating air monitoring sites. The local influences of some types of sources (roadw ay dust or emissions) may be factors that require monitoring site s to be spaced certain distances from those sources or in the

case or near

- road or roadway monitoring activities, the monitors must be located very close to the potential sources of

mobile em issions.

The principal areas in Tennessee with air monitoring sites are depicted with a graphic showing the locations for each of the monitoring sites. The sites are further identified with a site number, an AQSID and the types of pollutants being monito red for at each location. Tables containing the relevant information for each site are also included. The tables are provided in two sections following the location graphic and have been condensed and combined from the

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previous year’s format so that all relevant information can be found within each areas section of the report and relieves the reader from searching tables at the end of the report for information about a given site.

A separate section is provided to discuss the NCORE monitoring requirement s and the two NCORE sites selected to operate in Tennessee.

Each of the four local programs operating air monitoring networks in Tennessee have also provided separate annual reviews which have been included as attachments to this report. Where revisions were noted in the local networks, similar revisions were added to the states overall plan.

The recent changes in the NAAQS (National Ambient Air Quality Standards) have resulted in a need to evaluate additional air monitoring in order to comply with the n ew standards. In some cases (SO2, NO2 and Lead) the revisions to the standard was augmented with revisions to th e monitoring requirements. Some of the necessary changes to the monitoring networks have been completed while others are being planned for imp lementation. Additional changes to the existing ozone monitoring networks are anticipated after EPA finalizes the proposed revisions to the ozone standard (potentially lower than 0.075 ppm 8 hour average). Additional changes to both the number and placem ent of existing and new SO2 and NO2 monitoring sites are under consideration. Additional lead monitoring sites may also be needed to meet the new source related monitoring requirements finalized for lead.

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# Tennessee Geographic Regions and Descriptions

In order to have a more meaningful understanding of its different land patterns and variations, geographers and geologists have divided the State into nine natural regions or physiographic provinces. From west to east (see map of Natural Regions of Tennessee) these are the Mississippi Alluvial Valley, West Tennessee Plain, West Tennessee Uplands, Western Highland Rim, Central Basin, Eastern Highland Rim, Cumberland Plateau, Valley and Ridge, and Unaka Mountains.

MISSISSIPPI ALLUVIAL VALLE Y

The Mississippi Alluvial Valley, situated along the State’s western border, is a relatively narrow strip of land that varies from 5 to 20 miles in width and is oriented in a north to south direction. Covering an area of only 57 square miles, it is the smallest of the State’s natural regions. The western boundary of the region is the Mississippi River; the eastern boundary is the Chickasaw Bluffs of the West Tennessee Plain. Although six counties have some area in the region, only Lake County is found entirely within he Mississippi Alluvial Valley. The average elevation of this floodplain region is 235 feet, although it may be as high as 290 feet in Lake County and as low as 185 feet in Shelby County.

WEST TENNESSEE PLAIN

The West Tennessee Plain has an area of 7731 square miles and is the second largest physiograph province in the State. This plain is 45 to 65 miles wide and is bounded on the west by the Chickasaw Bluffs. The eastern boundary follows the drainage divided between the Mississippi Riv er and the Western Valley of the Tennessee River. Eighteen of the State’s counties are either completely or partially situated in the West Tennessee Plain. The topography of the West Tennessee Plain is a relatively flat terrain that slopes gently westwar d to the Mississippi River floodplain. Elevations of 450 feet are found on West Tennessee Plain’s eastern side and

around 280 feet on the west. Relief in most areas is less than 200 feet.

WEST TENNESSEE UPLANDS

The West Tennessee Uplands, the second s mallest physiographic province in the State, occupies an area of 1928 square miles. The drainage divided between the Mississippi and Tennessee Rivers forms the region’s western boundary, while the eastern boundary is marked by the Tennessee River. The wi dth of this upland region is 15 to 45 miles and covers parts of seven of the State’s counties. Although it is not considered a rugged region, the West Tennessee Uplands has greater relief and contrast than the West Tennessee Plain. Broad expanses of

undu lating plains are found here. The average elevation of this upland province is 700 feet with relief varying

from 100 to 300 feet.

HIGHLAND RIM

The Highland Rim, covering an area of 10,572 square miles, is the largest physiographic province in Tennessee. It extends from the Tennessee River in the west to the western escarpment of the Cumberland Plateau in the east. A large part of the Highland Rim’s center has been eroded out by the Cumberland River, forming the large, oval

- shaped Central Basin. The pr esence of Central basin, as well as the Highland Rim being relatively narrow in the State’s north and south borders, has led to the dividing of the Highland Rim into western and eastern divisions. The Western Highland Rim is the larger of the two, with an area of 6566 square miles. Together, these divisions account for area in 39 of the State’s counties. The Western Highland Rim varies from 25 to 45 miles in width and consists of a rolling terrain heavily dissected by stream erosion. Elevations on the

W estern Highland Rim’s tableland range from 800 to 1000 feet, while relief varies from 100 to 200 feet. The

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Eastern Highland Rim averages 25 miles in width and has an elevation of 900 to 1100 feet. The topography is comprised of an undulating tableland of low relief with widely scattered hills and knobs.

CENTRAL BASIN

The Central Basin, also known as the Nashville basin, is a larger pear

- shaped area occupying much of the geographic center of the State. The area has a total of 5851 square miles, measures 65 miles east to west and 95 miles north to south. With the exception of the valley of the Cumberland River at its northern corners, the central Basin is entirely surrounded by the Highland Rim. Wilson, Rutherford, and Marshall Counties are

situated ent irely within the Basin; parts of 23 other counties are also found there. Differences in typography have caused the Central Basin to sometime be divided into two different regions. Large areas of the region’s geographic center are known as The Inner Basin . This topography is extremely level and has an average

elevation of 650 feet. Relief in most areas is less than 50 feet. Relief in most areas is less than 50 feet. The few hills and knobs that rise above the landscape are commonly less than 100 feet i n height. The Outer Basin includes the rest of the province and is comprised of an undulating, hilly type topography. Numerous hills and ridges mark the landscape and are especially prominent at the outer edge. The average elevation in this part of

the basin is 750 feet, but may vary as much as 250 feet.

CUMBERLAND PLATEAU

Covering an area of 2980 square miles, the Cumberland Plateau is an elevated tableland bounded on the west by the Eastern Highland Rim and on the east by the Valley and Ridge. The g reatest width, 75 miles, is near the Kentucky border. At its most southern point in the State, the Cumberland Plateau is about 35 miles in width. Five of the State’s counties are entirely within the region, while another 17 counties are situated partiall y in this area. The Cumberland Plateau’s topography varies in different parts of the region. In places, the surface has been cut by stream valleys and precipitous gorges that are 200 to 400 feet deep. The tableland part of the

Cumberland Plateau has an average elevation of 1800 feet. The elevations are generally lower in the northern part at 1700 to 1900 feet. Far to the south in Marion and Hamilton Counties, the elevations are somewhat higher, around 2000 to 2100 feet. Relief varies from as little as 100 feet to as much as 400 feet.

VALLEY AND RIDGE

The Valley and Ridge covers 7703 square miles and is situated between the Cumberland Plateau to the west and the Unaka Mountains to the east. The width of the region ranges from as much as 70 miles alon g the Kentucky border to as little as 30 miles near the Georgia State Line. In most places, it averages 45 miles in width. Twenty

- seven counties of Tennessee are either completely or partially found in this Valley and Ridge region. The topography of the Valley and Ridge consists of long linear ridges and parallel lowland valleys that trend in a northeast to southwest direction. The ridges usually have high elevations of 1100 to 1500 feet while the adjacent valley floors vary from 700 feet to 1000 feet. The ridges and valleys generally have high elevations in the northern part of the region; they are slightly less elevated to the south.

UNAKA MOUNTAINS

Covering an area of 2523 square miles, the Unaka Mountains region is the most eastern physiographic province in Tennessee and extended along its entire eastern border adjacent to North Carolina. The width of the region varies from 5 to 25 miles. Although 13 counties have part of their land area within the region, Johnson County is the only on having all of its area completely within the region. The Unaka Mountains region is known for having the highest and most rugged terrain in Tennessee. Lofty mountai nous ridges and peaks, heavily forested and deeply carved by precipitous stream valleys, comprise the topography. The highest point, in both the region and the State, is Clingman’s Dome (6643 ft) in Sevier County. In addition to Clingman’s Dome, there ar e 13 other mountain peaks in the Unakas with heights of over 6000 feet and 33 peaks of more than 5000 feet. A very

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large percentage of those peaks are situated directly on the Tennessee State Line, with the greatest concentration found in Sevier County. Narrow lowland valleys and isolated coves are also a part of the topography of the region. The floors of these topographic features range from 1000 to 2000 feet in elevation.

Excerpt from draft of : Tennessee Division of Geology Bulletin 86, Tennessee Top ography, by David D. Starnes (2009). The section is titled "Physiographic Provinces of Tennessee."

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# Tennessee Geographic Regions

## 10 

# Climate Synopsis for Tennessee

The highly varied topography of Tennessee has a significant im pact on the state's climate. The landscape varies generally from west to east, starting with the gently rolling lowlands (200

- 600' above sea level) in the west, rising to the Highland Rim (600

- 1000') enclosing the Central Basin, and on up to the Cumberland Plateau (~2000') which trends northeast

- southwest across the state in a belt 30

- 50 miles wide. East of the Plateau is the Great Valley of East Tennessee (elevations ranging from 1500' in the north down to 700' in the south) containing a series of northeas t

- southwest ridges. The eastern border of the state is dominated by the Great Smoky Mountains, with numerous peaks rising 4000' to 6000' above sea level.

Average annual temperature across the state range from around 55F to a bit over 60F. Winter mean
temp eratures are near 35F over most of the state, while summer temperatures average between 75F and 80F. Of course, these general patterns are affected by topography: the higher mountain areas tend to have milder summers as well as colder, more blustery winter s. The length of the growing season is also linked to topography: most of the state has a growing season between 180 and 220 days, but this stretches to over 235 days in the lowlands around Memphis and drops to near 130 days in the highest mountains to the east.

The principal source of moisture for the state is the Gulf of Mexico to the south, which results in a gradual decrease of precipitation from south to north. This gradient is largely obscured, however, by orographic effects. In West Tennessee, annua l precipitation amounts range from 46 inches to 54 inches, increasing from the Mississippi bottomlands to the slight hills farther east. In Middle Tennessee, the variation is from around 45

inches in the Central Basin to 50

- 55 inches • in the surrounding Hi ghland Rim. The Cumberland Plateau also averages 50

- 55 inches • per year. In the Great Valley of Eastern Tennessee, annual precipitation rises from a

minimum of 40 inches • in the north (the driest part of the state due to the rain shadow effect of the Great Smoky Mountains and the Cumberland Plateau) to over 50 inches in the south. The mountainous eastern border of the state is the wettest part, with annual totals of up to 80 inches in the higher, well

- exposed peaks.

Over most of the state, the greatest pre cipitation occurs in winter and early spring owing to the more frequent passage of large

- scale (frontal) storms over the region. A secondary maximum of precipitation occurs in midsummer in response to shower and thunderstorm activity, especially in July in the mountains of the east. Fall tends to be the dry season for the state, due to the higher frequency of slow

- moving high pressure areas during this season. Average annual snowfall ranges from 4

- 6 inches in the south and west to over 10 inches in

the east . Due to the relatively mild winter conditions over most of the state, snow cover rarely persists for more than a few days. Severe storms are relatively infrequent in the state, being east of the center of tornado activity, south of most

blizzard condition s, and too far inland to be often affected by hurricanes. An average of 11 tornadoes are observed in the state each year, mostly confined to areas west of the Cumberland Plateau. Hailstorms at a given location are observed 2 or 3 times a year, and damaging glaze storms occur in the state every 5 or 6 years. Thunderstorms are frequent in the warm season, and severe thunderstorms with damaging winds are experienced at scattered locations throughout the state each year.

Adapted from: Climatography of the Unit ed States, No. 60, National Climatic Center

## 11 

# Windrose Data for Tennessee

## 12 Tennessee Metropolitan and Micropolitan Statistical Areas and Population Data

(2000 Census and Estimates to 200 9 by US Census Bureau)

2010 OMB Standards for Delineating Metropolitan and Micropolitan Statistical Areas [PDF] (Note: the new delineations based on the 2010 standards will be announced by OMB in 2013.)

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# Tennessee County Population Density

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# Monitoring Equipment Evaluation for Tennessee Air Pollution Control

Division

The Division has evaluated the operating condition of all air monitors and auxiliary support equipment in its inventory and determined the following major pieces of equipment will be needed for replacement purposes this

year.

Item Quantity Ozone Analyzer 2

PM

- 2.5 Speciation Monitor 1

PM

- 2.5 Continuous Monitor 2

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# The Purpose of Tennessee’s Ambient Air Monitoring Network

There are several criteria that are used for determining the need for ambient air quality monitoring. Some of the criteria are as follows:

EPA National Ambient Air Quality Standards (NAAQS) Criteria pollutant monitoring network requirements for the NCore (National Core) formally NAMS (National Air Monitoring Site), SLAMS (State and Local Air Monitoring Site) and SPM (Special Purpose Monitoring) monitoring networks.

The Code of Federal Regulations (CFR) sets forth as regulations the requirements for air quality monitoring to be implemented by the states and EPA. These requirements are primarily organized around population and emission density in a given area with the number of required monitors and the distribution of the monitors within the networks specified by

these re gulations. Additionally 40CFR, Part 58, Appendix D specifies criteria that must be followed in designing the NCore and SLAMS networks. The EPA must approve design

and/or modifications to these networks.

Additional federal regulations also specify requir ements for Prevention of Significant Deterioration (PSD) monitoring networks

. This monitoring is addressed at new facilities to be constructed in a given area or around certain types of existing industry such as large coal fired power plants or facilities that release toxic heavy metals such as lead to the

environment.

Air quality monitoring is required to be conducted to alert citizens in given areas to elevated levels of air pollutants in cities or communities of designated population levels that are

re quired to provide Air Quality Index (AQI) reports to the general public.

Air quality monitoring is conducted to address the need for background air quality data and to provide needed air quality data that is used in industrial recruitment efforts with the monitoring areas periodically rotated to new locations throughout the state on a routine basis.

Special air quality monitoring studies are conducted based on identified needs for monitoring data in a given area.

Citizen complaints and enforcement invest igations related to air quality are other reasons for air quality monitoring usually in or around a specific area related to the complaint or investigation.

Requests from citizens for special air monitoring studies are also a reason for air monitoring

act ivities.

## 17

The federal regulations also specify the frequency, method, location requirements, equipment, quality assurance procedures and reporting of data collected from the ambient air monitoring networks.

## 18 

# Ozone monitoring network requiremen ts

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 20 10

TABLE D

– 2 OF APPENDIX D TO PART 58.

— SLAMS MINIMUM O3 MONITORING REQUIREMENTS

MSA population 1, 2 

### Most recent 3

- year design value
concentrations ≥85% of any O3 NAAQS 3 

### Most recent 3

- year design value
concentrations <85% of any O3 NAAQS 3,4



### >10 million 4 2

4

– 10 million 3 1
350,000

– <4 million 2 1
50,000

– <350,000 5 

### 1 0

1 Minimum monitoring requirements apply to the Metropolitan statistical area (MSA). 2 Population based on latest available census figures. 3 The ozone (O3) National Ambient Air Quality Standards (NAAQS) levels and forms are defined in 40 CFR part 50. 4 These minimum monitoring requirements apply in the absence of a design value. 5 Metropolitan statistical areas (MSA) must contain an urbanized area of 50,000 or more population.

Note: The NAAQS for ozone was revised by EPA March 12, 2008 to 0.075 PPM. There were no regulatory changes made to the network monitoring requirements at that time.

On January 6, 2010 EPA proposed strengthening the 8

- hour “primary” ozone standard, to a level within the range of 0.060

- 0.070 parts per million (ppm). EPA also proposed to establish a distinct cumulative, seasonal “secondary” standard w ithin the range of 7

- 15 ppm

- hours. EPA pr oposed in July 2009 to modify the ozone air quality monitoring network design requirements for urban areas with populations between 50,000 and 350,000 people operate at least one ozone monitor and that states be required to operate at least three ozone mon itors in

non

- urban areas. However, these regulations have not yet been finalized by the EPA. When the rules become final Tennessee will redesign its ozone monitoring network in accordance with the regulations.



# PM 2.5 monitoring network requirements

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 20 10

TABLE D

– 5 OF APPENDIX D TO PART 58. PM2.5 MINIMUM MONITORING REQUIREMENTS

MSA population 1, 2 

### Most recent 3

-

year design value

concentrations ≥85% of any PM 2.5 

### NAAQS 3 

### Most recent 3

-

year des ign value

concentrations <85% of any

PM 2.5 

### NAAQS 3,4 

### Continuous

PM 2.5 Monitoring PM2.5

Background and Transport Sites PM2.5

Chemical Speciation

Sites

>1,000,000 3 2 1

- 2 One site each per state for background and transport. Existing

STN Required Site(s) 500,000

– 1,000,000 2 1 1
50,000

– <500,000 5 

### 1 0 0

- 1

1 Minimum monitoring requirements apply to the Metropolitan statistical area (MSA). 2 Population based on latest available census figures. 3 The PM2.5 National Ambient Air Quality Standards (NAAQS) levels and forms are defined in 40 CFR part 50. 4 These minimum monitoring requirements apply in the absence of a design value. 5 Metropolitan statistical areas (MSA) must contain an urbanized area of 50,000 or more population.

4.7.2 Requirement for Cont inuous PM2.5 Monitoring. The State, or where appropriate, local agencies must operate continuous PM2.5 analyzers equal to at least one

- half (round up) the minimum required sites listed in Table D

- 5 of this

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appendix. At least one required continuous analyz er in each MSA must be collocated with one of the required FRM/FEM/ARM monitors, unless at least one of the required FRM/FEM/ARM monitors is itself a continuous FEM or ARM monitor in which case no collocation requirement applies. State and local air monito ring agencies must use methodologies and quality assurance/quality control (QA/QC) procedures approved by the EPA Regional Administrator for these required continuous analyzers.

4.7.3 Requirement for PM2.5 Background and Transport Sites. Each State shall install and operate at least one PM2.5 site to monitor for regional background and at least one PM2.5 site to monitor regional transport.

4.7.4 PM2.5 Chemical Speciation Site Requirements. Each State shall continue to conduct chemical speciation

monitori ng and analyses at sites designated to be part of the PM2.5 Speciation Trends Network (STN). The selection and modification of these STN sites must be approved by the Administrator.



# PM 10 monitoring network requirements

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 20 10

TABLE D

– 4 OF APPENDIX D TO PART 58. PM10 MINIMUM MONITORING REQUIREMENTS (NUMBER OF STATIONS PER MSA) 1

1 Selection of urban areas and actual numbers of stations per area within the ranges shown in this table will be jointly determined by EPA and the State Agency. 2 High concentration areas are those for which ambient PM10 data show ambient concentrations exceeding the PM10 NAAQS by 20 percent or more.

3 Medium concentration areas are those for which ambient PM 10 data show ambient concentrations exceeding 80 percent of the PM10 NAAQS. 4 Low concentration areas are those for which ambient PM10 data show ambient concentrations less than 80 percent of the PM10 NAAQS. 5 These minimum monitoring requirements apply in the absence of a design value.



# SO2 monitoring network requirements

Federal Register / Vol. 75, No. 119 / Tuesday, June 22, 2010 / Rules and Regulations
Appendix D to Part 58

— Network Design Criteria for Ambient Air Quality Monitoring

## 20

4.4 Sulfur Dioxide (SO2) Design Criteria.

4.4.1 General Requirements. (a) State and, where appropriate, local agencies must operate a minimum number of required SO2 monitoring sites as described below.

4.4.2 Requirement for Monitoring by the Population Weighted Emi ssions Index. (a) The population weighted emissions

index (PWEI) shall be calculated by States for each core based statistical area (CBSA) they contain or share with another

State or States for use in the implementation of or adjustment to the SO2 monitori ng network. The PWEI shall be calculated by multiplying the population of each CBSA, using the most current census data or estimates, and the total amount of SO2 in tons per year emitted within the CBSA area, using an aggregate of the most recent county l evel

emissions data available in the National Emissions Inventory for each county in each CBSA. The resulting product shall be divided by one million, providing a PWEI value, the units of which are million persons

- tons per year. For any CBSA

with a calcula ted PWEI value equal to or greater than 1,000,000, a minimum of three SO2 monitors are required within

that CBSA. For any CBSA with a calculated PWEI value equal to or greater than 100,000, but less than 1,000,000, a

minimum of two SO2 monitors are require d within that CBSA. For any CBSA with a calculated PWEI value equal to or greater than 5,000, but less than 100,000, a minimum of one SO2 monitor is required within that CBSA. (1) The SO2 monitoring site(s) required as a result of the calculated PWEI in each CBSA shall satisfy minimum monitoring requirements if the monitor is sited within the boundaries of the parent CBSA and is one of the following site types (as defined in section 1.1.1 of this appendix): population exposure, highest concentration, sour ce impacts, general background, or regional transport. SO2 monitors at NCore stations may satisfy minimum monitoring requirements if that

monitor is located within a CBSA with minimally required monitors under this part. Any monitor that is sited outside o f a CBSA with minimum monitoring requirements to assess the highest concentration resulting from the impact of significant sources or source categories existing within that CBSA shall be allowed to count towards minimum monitoring requirements for that CBS A.

4.4.3 Regional Administrator Required Monitoring. (a) The Regional Administrator may require additional SO2 monitoring stations above the minimum number

of monitors required in 4.4.2 of this part, where the minimum monitoring requirements are not suffi cient to meet monitoring objectives. The Regional Administrator may require, at his/her discretion, additional monitors in situations where an area has the potential to have concentrations that may violate or contribute to the violation of the NAAQS, in

ar eas impacted by sources which are not conducive to modeling, or in locations with susceptible and vulnerable populations, which are not monitored under the minimum monitoring provisions described above. The Regional Administrator and the responsible State or local air monitoring agency shall work together to design and/or maintain the most appropriate SO2 network to provide sufficient data to meet monitoring objectives

4.4.5 NCore Monitoring

.

## 21

(a) SO2 measurementare included within the NCore multipollutant site requirements as described in paragraph (3)(b) of this appendix. NCorebased SO2 measurements are primarily used to characterize SO2 trends and assist in understanding SO2 transport across representative areas in urban or rural locations and are also used for comparison with the SO2 NAAQS. SO2 monitors at NCore sites that exist in CBSAs with minimum monitoring requirements per section 4.4.2

above shall be allowed to count towards those minimum monitoring requirements.

On June 2, 2010, EP A strengthened the primary National Ambient Air Quality Standard (NAAQS) for sulfur dioxide (SO2). EPA is revising the primary SO2 standard by establishing a new 1

- hour standard at a level of 75 parts per billion (ppb). The Agency is revoking the two exi sting primary standards of 140 ppb evaluated over 24

- hours, and 30 ppb evaluated over an entire year because they will not add additional public health protection given a 1

- hour standard at 75 ppb. EPA is also revising the ambient air monitoring requireme nts for SO2. States will need to make adjustments to the existing monitoring network in order to ensure that monitors meeting the network design regulations for the new 1

- hour SO2 standard are sited and operational by January 1, 2013. EPA plans to use ref

ined dispersion modeling to determine if areas with sources that have the potential to cause or contribute to a violation of the new SO2 standard can comply with the standard.

The final monitoring regulations require monitors to be placed in Core Based S tatistical Areas (CBSAs) based on a population weighted emissions index for the area. The final rule requires:

3 monitors in CBSAs with index values of 1,000,000 or more; 2 monitors in CBSAs with index values less than 1,000,000 but greater than 100,000; a nd 1 monitor in CBSAs with index values greater than 5,000.



# NO2 monitoring network requirements

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 20 10

4.3 .2 Requirement for Near

- road NO2 Monitors (a) Within the NO2 network, there must be one microscale near

- road NO2 monitoring station in each CBSA with a population of 500,000 or more persons to monitor a location of expected maximum hourly concentrations sited near a major road with high AADT counts as specified in paragraph 4.3.2(a)(1) of this appendix. An additional near

- road NO2 monitoring station is required for any CBSA with a population of 2,500,000 persons or more, or in any CBSA with a population of 500,000 or more persons that has one or more roadway segments with 250,000 or gre ater AADT counts to monitor a second location of expected maximum hourly concentrations. CBSA populations shall be based on the latest available census figures.

4.3.3 Requirement for Area

- wide NO2 Monitoring (a) Within the NO2 network, there must be one monitoring

station in each CBSA with a population of 1,000,000 or more persons to monitor a location of expected highest

NO2 concentrations representing the neighborhood or larger spatial scales. PAMS sites collecting NO2 data that

are situated in an area of expected high NO2 concentrations at the neighborhood or larger spatial scale may be used to satisfy this minimum monitoring requirement when the NO2 monitor is operated year round. Emission inventories and meteorological analysis should be used to identify the appropriate locations within a CBSA for locating required area

- wide NO2 monitoring stations. CBSA populations shall be based on the latest available census figures.

EPA announced on January 22, 2010 the final revisions to the NO2 NAAQS. EPA added a new Primary1

- hour NO2 standard at 100 ppb (parts per billion). EPA chose to retain the current Primary and Secondary standards and to revise the AQI for NO2 to incorporate the new 1

- hou r standard. Additional monitors will also be required to be placed in areas with vulnerable populations susceptible to NO2 health related effects. These additional monitors would be required to be operational before January 1, 2013 if the EPA proposal is adopted in

its current form.



# Lead monitoring network requi rements

## 22

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 2010

4.5 Lead (Pb) Design Criteria. Lead (Pb) Design Criteria.

(a) State and, where appropriate, local agencies are required to conduct ambient air Pb monitoring taking into

accou nt Pb sources which are expected to or have been shown to contribute to a maximum Pb concentration in ambient air in excess of the NAAQS, the potential for population exposure, and logistics. At a minimum, there

must be one source

- oriented SLAMS site locat ed to measure the maximum Pb concentration in ambient air resulting from each Pb source which emits 0.5 or more tons per year based on either the most recent National

Emission Inventory ( http://www.epa.gov/ttn/chief/ eiinformation.html ) or other scientifically justifiable methods and data (such as improved emissions factors or site

- specific data) taking into account logistics and the potential for population exposure. (i) One monitor may be used to meet the requirement in paragraph 4.5(a) for all sources involved when

the location of the maximum Pb concentration due to one Pb source is expected to also be impacted by

Pb emissions from a nearby source (or multiple sources). This monitor must be sited, taking into account logistics and the potential for population exposure, where the Pb concentration from all

sources combined is expected to be at its maximum. (ii) The Regional Administrator may waive the requirement in paragraph 4.5(a) for monitoring near Pb sources if the State or, where appropriat e, local agency can demonstrate the Pb source will not

contribute to a maximum Pb concentration in ambient air in excess of 50% of the NAAQS (based on historical monitoring data, modeling, or other means). The waiver must be renewed once every 5 years

as p art of the network assessment required under 58.10(d). (b) State and, where appropriate, local agencies are required to conduct Pb monitoring in each CBSA with a population equal to or greater than 500,000 people as determined by the latest available cens us figures. At a minimum, there must be one non

- source

- oriented SLAMS site located to measure neighborhood scale Pb concentrations in urban areas impacted by re

- entrained dust from roadways, closed industrial sources which previously were significant sources of Pb, hazardous waste sites, construction and demolition projects, or other fugitive dust sources of Pb.

On December 14, 2010, the Environmental Protection Agency (EPA) revised the ambient monitoring requirements for measuring lead (Pb) in the air. These amendments expand the nation’s lead monitoring network to better assess compliance with the revised Nation al Ambient Air Quality Standards (NAAQS) for lead issued in 2008. EPA is changing the emission threshold that state monitoring agencies must use to determine if an air quality monitor should be placed near an industrial facility that emits lead. The new e mission threshold is 0.5 tons per year (tpy), reduced from the previous threshold of 1.0 tpy. Any new monitors located near an emissions source must be operational no later than one year after this rule is published in the Federal Register. EPA is

maintai ning a 1.0 tpy lead emission threshold for airports. EPA is also requiring lead monitoring in large urban areas (Core Based Statistical Areas, or CBSAs, with a population of 500,000 people or more). Monitors will be located along with multi

- pollutant ambi ent monitoring sites (known as the “NCore network”). Lead monitoring at these sites will begin January 1, 2012. The NCore network will consist of approximately 80 monitoring sites, of which 63 will be in large urban areas. The requirement to add these mon itors replaces an existing requirement to place lead monitors in each CBSA with a population of 500,000 or more people.

Tennessee has already identified an area not meeting the new standard and has implemented monitoring at the

source. Additional evalua tions are underway to identify all 0.5 ton sources for potential monitoring.



# CO monitoring network requirements

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 20 10

4.2 Carbon Monoxide (CO) Design Criteria. (a) There are no minimum requirem ents for the number of CO monitoring sites. Continued operation of existing SLAMS CO sites using FRM or FEM is required until discontinuation is approved by the EPA Regional Administrator. Where SLAMS CO monitoring is ongoing, at least one site must be a m aximum concentration site for that area under investigation.

## 23

On January 28, 2011, EPA proposed to retain the existing National Ambient Air Quality Standards (NAAQS) for carbon monoxide (CO). EPA is proposing changes to the ambient air monitoring requirem ents for CO. EPA is proposing to require co

- location of these CO monitors with a subset of nitrogen dioxide (NO2), monitors that are required, as part of the January, 2010 revision to the NAAQS for NO2. Specifically, EPA is proposing to require

the coloc ation with “near

- road” NO2 monitors in urban areas having populations of 1 million or more. EPA is proposing that the required CO monitors would be operating by January 1, 2013. EPA is also proposing that EPA Regional Administrators would have the author ity to require additional monitoring in case

- by

- case circumstances, such as in areas impacted by major stationary CO sources, in urban downtown areas or urban street canyons, or in areas adversely impacted by meteorological and/or topographical influences.



# Index reporting requirements

40 CFR 58 Subpart F, 58.50 Revised as of July 1, 20 10

§ 58.50 Index reporting.

(a) The State or where applicable, local agency shall report to the general public on a daily basis through prominent notice an air quality ind ex that complies with the requirements of appendix G to this part. (b) Reporting is required for all individual MSA with a population exceeding 350,000. (c) The population of a MSA for purposes of index reporting is the most recent decennial U.S. census population.

Geographic area 2000

Census 2010

Census Required to Have

AQI Reporting Daily AQI/Air Quality Forecasts

Provided Chattanooga, TN

- GA 476,531 Yes Yes
Clarksville, TN

- KY 232,000 No Yes
Cleveland, TN 104,015 No No
Jackson, TN 107,377 No No Johnson City, TN 181,607 No Yes Based on the combined population

of both areas. Kingsport

- Bristol

- Bristol, TN

- VA 298,484 No

Knoxville, TN 616,079 Yes Yes In addition, the GSMNP has a separate AQI/Forecast provided. Memphis, TN

- MS

- AR 1,205,204 Yes Yes
Morristown, TN 123,081 No No

Nashville

- Davidson

-- Murfreesboro, TN 1,311,789 Yes Yes



# NCore monitoring network requirements and PM 10

- 2.5

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 20 10

3. Design Criteria for NCore Sites (a) Each State (i.e. the fifty States, District of Columbia, Puerto Rico, and the Virgin Islands) is required to operate at least one NCore site. States may delegate this requirement to a local agency. States with many MSAs often also have multiple air sheds with unique characteristics and, often, elevated air pollution. These States include, at a minimum, California, Florida, Illinois, Michigan, New York, North Carolina, Ohio, Pennsylvania, and Texas. These States are required to identify one to two additiona l NCore sites in order to account for their unique situations. These additional sites shall be located to avoid proximity to large emission sources. Any State or local agency can propose additional candidate NCore sites or modifications to these requiremen ts for approval by the Administrator. The Ncore locations should be leveraged with other multipollutant air monitoring sites including PAMS sites, National Air Toxics Trends Stations (NATTS) sites, CASTNET sites, and STN sites. Site leveraging includes usi ng the same monitoring platform and equipment to meet the objectives of the variety of programs where possible and advantageous.

## 24

(b) The NCore sites must measure, at a minimum, PM2.5 particle mass using continuous and integrated/filter

- based samplers, spec iated PM2.5, PM10

– 2.5 particle mass, speciated PM10

– 2.5, O3, SO2, CO, NO/NOy, wind speed, wind direction, relative humidity, and ambient temperature. (1) Although the measurement of NOy is required in support of a number of monitoring objectives, available commercial instruments may indicate little difference in their measurement of NOy compared to the conventional measurement of NOX, particularly in areas with relatively fresh sources of nitrogen emissions. Therefore, in areas with negligible expected diff erence between NOy and NOX measured concentrations, the Administrator may allow for waivers that permit NOX monitoring to be substituted for the required NOy monitoring at applicable NCore sites. (2) EPA recognizes that, in some cases, the physical locatio n of the NCore site may not be suitable for representative meteorological measurements due to the site’s physical surroundings. It is also possible that nearby meteorological measurements may be able to fulfill this data need. In these cases, the requireme nt for meteorological monitoring can be waived by the Administrator. (c) In addition to the continuous measurements listed above, 10 of the Ncore locations must also measure lead (Pb) either at the same sites or elsewhere within the MSA/CSA boundary. These ten Pb sites are included within the NCore networks because they are intended to be long

- term in operation, and not impacted directly from a single Pb source. These locations for Pb monitoring must be located in the most populated MSA/CSA in each

of the 1 0 EPA Regions. Alternatively, it is also acceptable to use the Pb concentration data provided at urban air toxics sites. In approving any substitutions, the Administrator must consider whether these alternative sites are suitable for collecting long

- term l ead trends data for the broader area.

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 20 10

4.8.1 General Monitoring Requirements. (a) The only required monitors for PM10

- 2.5 are those required at NCore Stations.

4.8.2 PM10

– 2.5 Chemical Spec iation Site Requirements.

PM10

– 2.5 chemical speciation monitoring and analyses is required at NCore sites. The selection and modification of these sites must be approved by the Administrator. Samples must be collected using the monitoring methods and the

s ampling schedules approved by the Administrator.

Tennessee’s primary NCore site will be located in Memphis, Tennessee . See the following pages for details on the proposed location of th e site. In addition to the Memphis NCore site, the EPA has designa ted the Look Rock air monitoring station in the Great Smoky Mountains National Park as an NCore rural

- type site. This site is operated in cooperation with the National Park Service , Tennessee Valley Authority, and the State of Tennessee.

The following pa ges identify the Memphis NCore site and the Look Rock NCore equivalent

- type site

.

## 25 

# NCore Monitoring In Tennessee 

# Ambient Air Monitoring Work Plan

For National Core (NCore) Monitoring Station

Memphis, TN

- MS

- AR MSA

Memphis and Shelby County Health Dept. Air

Pollution Control

814 Jefferson Avenue Memphis, TN 38105

## 26 National Core (NCore) Multi

- pollutant Monitoring Stations

In 2006, the U.S. Environmental Protection Agency (EPA) amended its national air quality monitoring requirements. The changes will help EPA, states, tribes and local air quality agencies improve public health protection and better inform the public about air quality in their communities. EPA and the states will add about 75 multi

- pollutant monitoring

sta tions around the country, as part of a National Core (NCore) network. Memphis and Shelby County has been selected as an NCore site location. With this selection, the Memphis and Shelby County Health Department (MSCHD) is faced with the unique challenge of finding a suitable site, which would meet EPA’s siting criteria.

Under the new requirements, air quality regulators will be able to take advantage of improvements in monitoring technologies. The changes will affect monitoring for six common pollutants kn own as "criteria pollutants" and their precursors. The six pollutants are: ground

- level ozone, carbon monoxide, nitrogen dioxide, sulfur dioxide, particle pollution (also called particulate matter) and lead. EPA’s siting criteria for NCore monitoring netwo rks ensure that monitors are concentrated in areas with air quality problems, where monitoring is most critical. Monitoring multiple pollutants at the same site will help EPA improve air quality management by enhancing the Agency's ability to model

and for ecast air pollution. The sites also will provide real

- time data for some pollutants, including particle pollution and ground

- level ozone.

By requiring that these monitors be co

- located, EPA will have the ability to examine the effects of multiple air po llutants

on health and the environment.

Siting

The NCore sites placement (siting) criteria is extensive, requiring certain distances from interstates and major roadways. It is the opinion of the MSCHD that no existing air monitoring site will meet sit ing requirements. The proposed Haley Road site is located on property owned by Shelby County Government and is located within the Memphis city limits. This location should meet all the criteria established by EPA. The site is located in Shelby Farms, area 10, adjacent to the Shelby County gas station on Haley road.

The coordinates are: 

## Latitude 35.15159 N Longitude 89.85022 W

Elevation 287 ft.

The ―NCore Readiness Self

- Assessment‖ forms along with photographs in 8 cardinal directions have been submitte d to

EPA.



## Official EPA approval was granted on August 26, 2009. Since this will not be an existing site, greater monitoring resources will be needed toward new capital purchases (site preparations, new building, new monitors, etc.) and costs cannot be co vered through divestment

- reinvestments of

resources alone.

Monitoring Objective

Determine compliance with NAAQS; observe pollution trends for national data analysis, provide pollution levels for daily index reporting; and provide data for scientific studies.

## 27 Monitors

Monitor Type Designation Analysis Method Frequency of Sampling

ARM Carbon Monoxide (CO) NCore Automated Reference Method utilizing trace

level non

- dispersive infrared analysis. Continuously

ARM Ozone (O 3 

### ) NCore/AQI Automated Equivalent Method utilizing UV photometry analysis. Continuously

ARM Sulfur Dioxide (SO 2 

### ) NCore Automated Equivalent Method utilizing trace level UV fluorescence analysis Continuously

FRM PM 2.5 

### NCore Manual Reference Method utilizing gravimetric analysi s. 1/3 days

PM 2.5 

### TEOM NCore/AQI Automated Equivalent Method* utilizing

T apered E lement O scillating

M icrobalance/gravimetric analysis Continuously

PM 2.5 

### Speciation NCore Multi

- species manual collection method utilizing thermal optical, ion chromatography, gravimetric, and X

- ray fluorescence analyses. 1/6 days

Total Reactive Nitrogen (NO y 

### ) NCore Automated trace level chemiluminescence analysis. Continuously

Meteorological NCore Air quality measurements approved

instrumentation for wind speed, wind direction, relative humidity, and temperature. Continuously

Lead NCore Manual Reference Method TSP or Manual

Reference Method PM 10 

### 1/6

* Pending

Area of Representativeness

40 CFR Part 58 Appendix D provides design criteria for ambient air monitoring. The monitoring objective for the NCore site is to produce data that represents a fairly large area and therefore the spatial scale of the site is important. The spatial scale defines the physical dimensions of the air parcel nearest to a monit oring site throughout which actual pollutant concentrations are reasonably similar. It is determined by the characteristics of the area surrounding the air monitoring site and the site ’s distance from nearby air pollution sources such as roadways, factori es, etc. In the case of urban NCore the spatial scales to be used are neighborhood and urban. Table 2 shows the area of representativeness for each pollutant for the Haley Road site.

Spatial Scales for Each Pollutant

Pollutant Spatial Scale Comments

Ozone Neighborhood and Urban Scale

NO

x 

### Neighborhood and Urban Scale

Carbon Monoxide Neighborhood Scale There is no Urban scale for CO

SO 2 

### Neighborhood Scale There is no Urban scale for SO 2 

### PM 10 

### /PM 2.5 

### /Lead Urban

## 28

The placement of the NCore site east of the urban core provides the best location for measuring transport and secondary pollutant formation from that area. And, the placement of the Haley Road site downwind of the more industrialized areas compliments the existing network, which is primarily designed to measure maximum concentration on a neighborhood scale.

## 29

As can be seen from the citywide view above, the proposed NCore site is located East of the urban

core and North East of the heavier indust rialized areas of the metro area.

## 30 6388 Haley Road (41

- 157

- 0075)

## 31 

# Wind Rose for Memphis, TN

- MS

- AR MSA

## 32

## 33 

# NCore Look Rock Monitoring Site

Air quality monitoring at the Look Rock monitoring site has a long history dating at least back to about 1980 . Monitoring at this site has been a joint effort of the National Park Service (NPS) Tennessee Valley Authority (TVA) and

the State of Tennessee.

Siting

The coordinates are:

Latitude + 35.6334 N Longitude

- 83.9416 W
Elevation 801 Meters

.

Site is approved by the EPA as a rural NCore site.



### Monitoring Objective

Determine compliance with NAAQS; observe pollution trends for national data analysis, provide pollution levels for daily inde x reporting; and provide data for scientific st udies.

## 34 Current National Park Service Monitoring At Look Rock 

## Updated by Jim Renfro xxxxxxxx 2011

## 35 Current TVA Air Monitoring at Look Rock Updated by Roger L. Tanner, April 11, 2011

POLLUTANT /

INSTRUMENT ANALYSIS

METHOD SAMPLING /

REPORTING FREQ AQS CODE PARA

METER

CODE POC REP ORG

CODE DATE

SAMPLIN G

BEGAN MONITOR SAMPLING

INSTRUMENT NAME

AND DESIGNATION FED AGENCY

Type Comment

Sulfur dioxide (SO 2 

### ) trace

- level Pulsed

fluorescence Continuous/

1 hour 47

- 009

- 0101 42401 2 1029 20070401 Special Purpose Proposed

NCore Thermo SO2 43i

- TLE

EQSA

- 0486

- 060 TVA

Carbon monoxide (CO) trace

- level

NDIR

- GFC Continuous/

1 hour 47

- 009

- 0101 42101 2 1029 20070401 Special Purpose Proposed

NCore Thermo CO

- 48i TLE

RFCA

- 0981

- 054 TVA

1 

### Nitrogen oxide (NO) trace

- level Chemilumine

scence with molybdenum

converter Continuous/

1 hour 47

- 009

- 0101 42601 2 1029 20070401 Special Purpose Proposed

NCore Thermo NO/NO y 

### 42C

TLE RFNA

- 1289

- 074 TVA

1 

### Total reactive nitrogen (NOy )

trace

- level Chemilumine

scence with molybdenum

converter Continuous/

1 hour 47

- 009

- 0101 42603 2 1029 20070401 Special Purpose Proposed

NCore Thermo NO/NO y 

### 42C

TLE RFNA

- 1289

- 074 TVA

1 

### Nitrogen oxide (NO) trace

- level Chemilumine

scence with photolytic

converter Continuous/

1 hour 47

- 009

- 0101 42601 3 1029 20081001 Special Purpose Proposed

NCore Teledyne NO/NO2/NOx

200EU with photolytic

converter TVA

1 

### Nitrogen dioxide (NO 2 

### ) trace

- level Chemilumine

scence with photolytic

converter Continuous/

1 hour 47

- 009

- 0101 42602 3 1029 20081001 Special Purpose Proposed

NCore Teledyne NO/NO2/NOx

200EU with photolytic

converter TVA

1 

### Oxides of Nitrogen (NO

x 

### )

trace

- level Chemilumine

scence with photolytic

converter Continuous/

1 hour 47

- 009

- 0101 42603 3 1029 20081001 Special Purpose Proposed

NCore Teledyne NO/NO2/NOx

200EU with photolytic

converter TVA

1 

### Black carbon

PM 2.5 

### LC Optical

absorption Continuous/

1 hour 47

- 009

- 0101 88313 2 1029 20061001 Special Purpose Proposed

NCore Magee Scientific AE21

Dual beam (BC/UV) TVA

1 

### Sulfate

PM 2.5 

### LC Thermal

reduction/

Pulsed

fluorescence Continuous/

1 hour 47

- 009

- 0101 88403 2 1029 20071106 Special Purpose Proposed

NCore Thermo Model 5020 TVA

1 

### Calibrator NA Daily NA NA NA NA 20070401 NA NA Thermo Model 146C TVA

1 

### Zero Air Supply NA NA NA NA NA NA 20070401 NA NA Thermo 111 TVA

1 

### Telemetry

- Data Logger NA 1 minute/1 hour NA NA NA NA 20070401 NA NA ESC 8832 TVA

## 36

Quality Assurance

All Quality Assurance procedures shall be implemented in accordance with 40 CFR 58, Appendix A.

Area of Representativeness

40 CFR Part 58 Appendix D provides design criteria for ambient air monitoring. In the case of urban NCore the spatial scales to be used are neighborhood and urban. Because the Look Rock site is located in a pristine high elevation area, it is understood that the site is ideally suited for both background and transport related measurements..

Spatial Scales for Each Pollutant

Generally regional scale.

## 37

Looking West Looking North

Looking East

Looking South 2011 View of Look Rock Site

## 38 

# Need For Additional Resources

All parties agree that the collaboration between the National Park Service, TVA and the S tate of Tennessee at the Look Rock sampling site has produced an extraordinarily diverse and in

- depth air quality record and that the bulk of this data set has been validated and reported to the U.S. EPA AQS repository. However, under the present piecemeal funding by the various agencies, there is no assura nce that this will continue at the site for the longer term needed for monitoring compliance with the PM NAAQS and with the regional haze rule (RHR). What is needed is a long

- term commitment by EPA to coordinate the operation of this and other sites to ma intain quality and relevance in the NCore network over the long term. This commitment should commence by the 2011 time frame when NCore sites are expected to become fully operational.

## 39 

# Nashville

- Davidson

-- Murfreesboro, TN MSA Area

## 40 Tennessee’s Interpretation of Ambient Air Monitors Needed to meet the 40CFR, Part 58 Requirements

Census Area Identification and Population Data 14129

Lead 42101
CO 42401
SO2 42602
NO2 44201 Ozone 81102
PM 10 88101 PM 2.5 88502
PM 2.5 Speciation 88101

or 88501
PM 2.5
Cont

CBSA

2003
Code Census

2000
/Est.

2009 CBSA 2003 Title (MS

Areas)

Operating Required Operating Required Operating Required Operating Required Operating 

### 200 8
20 10 8

Hr DV Required Operating Required Operating 

### 200 8
20 10

Annual DV ug/m 200 8

20 10 24

Hr DV ug/m Required Operating Required Operating Required



### 34980 1311789/

1582264 Nashville

- Davidson

Murfreesboro, TN 0 0 1 1 1 1 1 1 7 0.076 3 1 

### 2 5 1 

### 11.2 23 2 1 1 2 1

1 

### Includes collocated monitor.



## Discussions of any proposals to re

- locate monitors in the next 18 months and suitability of PM2.5 sites for use in comparisons to the annual

PM2.5 standard :

The TEOM POC 3 PM2.5 particulate monitors and the speciation POC 5 STN monitors are generally not suited to be used for compa risons to the annual PM2.5 standards.

There are no plans to relocate or shutdown any e xisting monitoring sites in the MSA area described.

The need to establish additional NO2 near road monitors is under consideration. No lead monitors are anticipated to be estab lished as there are no sources emitting 0.5 TPY of

lead. No additional SO2 mo nitors are anticipated to be required to be established. The proposed requirement for CO monitors to be collocated with the near road NO2

monitors has not been finalized. The need for additional monitoring sites may be met by re

- location of existing netw ork sites. Additional monitoring sites will require additional resources for both equipment and operational expenses.

## 41

AQSID County Name Monitor Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd RepOrg RepOrgName

470370002 Davidson SLAMS 81102 PM10 1 7 2010 6 LESTER &

HART STS 34980 +36.143244

- 86.754611 063 0682 Metropolitan

Health Department/Nashv

ille & Davidson County

470370 011 Davidson SLAMS 42401 SO2 1 1 2010 Hourly 1015 TRINITY

LANE 34980 +36.205000

- 86.744722 061 0682 Metropolitan

Health Department/Nashv

ille & Davidson County

470370011 Davidson UNKNO

WN 42602 NO2 1 1 2010 Hourly 1015 TRINITY

LANE 34980 +36.205000

- 86.744722 074 0682 Metropolitan

Health Department/Nashv

ille & Davidson County

470370011 Davidson UNKNO

WN 44201 O3 1 1 2010 Hourly 1015 TRINITY

LANE 34980 +36.205000

- 86.744722 047 0682 Metropolitan

Health Department/Nashv

ille & Davidson County

470370 021 Davidson UNKNO

WN 42101 CO 1 1 2010 Hourly 700

BROADWAY 34980 +36.159671

- 86.781149 054 0682 Metropolitan

Health Department/Nashv

ille & Davidson County

470370023 Davidson SLAMS 88101 PM2.5 1 7 2010 6 105 SOUTH 17TH ST @

LOCKELAND

SCHOOL 34980 +36.176326

- 86.738902 120 0682 Metropolitan

Health Department/Nashv

ille & Davidson County

470370023 Davidson SLAMS 88101 PM2.5 2 7 2010 6 105 SOUTH 17TH ST @

LOCKELAND

SCHOOL 34980 +36.176326

- 86.738902 120 0682 Metropolitan

Health Department/Nashv

ille & Davidson County

470370 023 Davidson INDEX

SITE 88502 PM2.5

Cont 3 1 2010 Hourly 105 SOUTH 17TH ST @

LOCKELAND

SCHOOL 34980 +36.176326

- 86.738902 717 0682 Metropolitan

Health Department/Nashv

ille & Davidson County

470370023 Davidson SUPLMN

TL

SPECIAT

ION 88502 PM Spec

Carbon 5 7 2010 6 105 SOUTH 17TH ST @

LOCKELAND

SCHOOL 34980 +36.176326

- 86.738902 810 0682 Metropolitan

Health Department/Nashv

ille & Davidson County

470370024 Davidson SLAMS 81102 PM10 1 7 2010 6 56TH AVE AND

LOUISIANA ST 34980 +36.162763

- 86.854927 063 0682 Metropolitan

Health Department/Nashv

ille & Davidson County

470370024 Davidson QA

COLLOC 81102 PM10 2 7 2010 6 56TH AVE AND

LOUISIANA ST 34980 +36.162763

- 86.854927 063 0682 Metropolitan

Health

## 42

AQSID County Name Monitor Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd RepOrg RepOrgName

ATED Department/Nashv

ille & Davidson County

470370026 Davidson SLAMS 44201 O3 1 1 2010 Hourly 3711 BELL

ROAD 34980 +36.150742

- 86.623301 047 0682 Metropolitan

Health Department/Nashv

ille & Davidson County

470370036 Davidson SLAMS 88101 PM2.5 1 7 2010 1 400 DAVIDSON

RD 34980 +36.118251

- 86.873547 120 0682 Metropolitan

Health Department/Nashv

ille & Davidson County

471490101 Rutherford SLAMS 44201 O3 1 1 2010 Hourly EAGLEVILLE

PUCKETT'S

FARM 34980 +35.732878

- 86.598872 047 1025 Tennessee
Division Of Air

Pollution Control

471650 007 Sumner UNKNO

WN 44201 O3 1 1 2010 Hourly ROCKLAND

RECREATION

AREA

- OLD

HICKORY

DAM 34980 +36.297778

- 86.652778 047 1025 Tennessee
Division Of Air

Pollution Control

471650 007 Sumner SLAMS 88101 PM2.5 1 7 2010 3 ROCKLAND

RECREATION

AREA

- OLD

HICKORY

DAM 34980 +36.297778

- 86.652778 118 1025 Tennessee
Division Of Air

Pollution Control

471650007 Sumner SLAMS 88101 PM2.5 2 7 2010 6 ROCKLAND

RECREATION

AREA

- OLD

HICKORY

DAM 34980 +36.297778

- 86.652778 118 1025 Tennessee
Division Of Air

Pollution Control

471650 007 Sumner SPECIAL

PURPOS

E 88501 PM2.5

Cont 3 1 2010 Hourly ROCKLAND

RECREATION

AREA

- OLD

HICKORY

DAM 34980 +36.297778

- 86.652778 716 1025 Tennessee
Division Of Air

Pollution Control

471650 101 Sumner SLAMS 44201 O3 1 1 2010 Hourly COTTONTOWN

WRIGHT'S

FARM 34980 +36.453975

- 86.564149 047 1025 Tennessee
Division Of Air

Pollution Control

471870106 Williamson SLAMS 44201 O3 1 1 2010 Hourly FAIRVIEW

MIDDLE

SCHOOL

CROW CUT

ROAD 34980 +35.951944

- 87.137222 047 1025 Tennessee
Division Of Air

Pollution Control

471890103 Wilson SLAMS 44201 O3 1 1 2010 Hourly CEDARS OF

LEBANON

STATE PARK 34980 +36.060372

- 86.286085 047 1025 Tennessee
Division Of Air

Pollution Control

## 43

AQS ID County

Name Monitor

Type Para Para

Name Monitoring

Instrument Analysis Ref

Mtd

ID Monitor Objective Type Domin

ant
Source Measurement

Scale Land Use Type Location Setting Date Site

Established

470370002 Davidson SLAMS 81102 PM10 GMW

Model

1200 GRAVIMETRI

C RFPS

- 1287

- 063 POPULATION

EXPOSURE AREA NEIGHBORH

OOD COMMERCIAL URBAN AND

CENTER

CITY 8/22/1969

470370011 Davidson SLAMS 42401 SO2 DASIBI

4108 ULTRA

VIOLET

FLUORESCEN

CE EQS

A

1086

- 061 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDENTIAL URBAN AND

CENTER

CITY 5/1/1970

470370011 Davidson UNKNO

WN 42602 NO2 THERMO

ENVIRON.

INST.

MODEL 42 CHEMILUMIN

ESCENCE RFN

A

1289

- 074 HIGHEST

CONCENTRA

TION AREA NEIGHBORH

OOD RESIDENTIAL URBAN AND

CENTER

CITY 5/1/1970

470370011 Davidson UNKNO

WN 44201 O3 THERMO

ELECTRO

N 49 ULTRA

VIOLET EQO

A

0880

- 047 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDENTIAL URBAN AND

CENTER

CITY 5/1/1970

470370021 Davidson UNKNO

WN 42101 CO THERMO

ELECTRO N 48, 48C,
48i NONDISPERSI

VE

INFRARED RFC

A

0981

- 054 HIGHEST

CONCENTRA

TION MOBI

LE MICROSCALE COMMERCIAL URBAN AND

CENTER

CITY 4/14/1972

470370023 Davidson SLAMS 88101 PM2.5 Andersen

RAAS2.5

- 300 PM2.5 SEQ GRAVIMETRI

C RFPS

- 0598

- 120 POPULATION

EXPOSURE AREA NEIGHBORH

OOD INDUSTRIAL URBAN AND

CENTER

CITY 1/1/1976

470370023 Davidson SLAMS 88101 PM2.5 Andersen

RAAS2.5

- 300 PM2.5 SEQ GRAVIMETRI

C RFPS

- 0598

- 120 POPULATION

EXPOSURE AREA NEIGHBORH

OOD INDUSTRIAL URBAN AND

CENTER

CITY 1/1/1976

470370023 Davidson INDEX

SITE 88502 PM2.5

Cont TEOM
Gravimetric 50 deg C POPULATION

EXPOSURE AREA NEIGHBORH

OOD INDUSTRIAL URBAN AND

CENTER

CITY 1/1/1976

470370023 Davidson SUPLM

NTL

SPECIA

TION 88502 PM Spec

Carbon MetOne

Super

SASS

URG 3000 GRAVIMETRI

C POPULATION

EXPOSURE NULL NULL INDUSTRIAL URBAN AND

CENTER

CITY 1/1/1976

470370024 Davidson SLAMS 81102 PM10 GMW

Model

1200 GRAVIMETRI

C RFPS

- 1287

- 063 HIGHEST

CONCENTRA

TION AREA NEIGHBORH

OOD RESIDENTIAL SUBURBAN 1/1/1976

470370024 Davidson QA

COLLO

CATED 81102 PM10 GMW

Model

1200 GRAVIMETRI

C RFPS

- 1287

- 063 QUALITY

ASSURANCE NULL NULL RESIDENTIAL SUBURBAN 1/1/1976

470370026 Davidson SLAMS 44201 O3 THERMO

ELECTRO

N 49 ULTRA

VIOLET EQO

A

0880

- 047 HIGHEST

CONCENTRA

TION AREA URBAN

SCALE FOREST RURAL 1/1/1978

470370036 Davidson SLAMS 88101 PM2.5 Andersen

RAAS2.5

- 300 PM2.5 SEQ GRAVIMETRI

C RFPS

- 0598

- 120 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDENTIAL SUBURBAN 12/1/1998

## 44

AQS ID County

Name Monitor

Type Para Para

Name Monitoring

Instrument Analysis Ref

Mtd

ID Monitor Objective Type Domin

ant
Source Measurement

Scale Land Use Type Location Setting Date Site

Established

471490101 Rutherford SLAMS 44201 O3 THERMO

ELECTRO

N 49 ULTRA

VIOLET EQO

A

0880

- 047 POPULATION

EXPOSURE AREA URBAN

SCALE AGRICULTUR

AL RURAL 4/1/1988

471650007 Sumner UNKNO

WN 44201 O3 THERMO

ELECTRO

N 49 ULTRA

VIOLET EQO

A

0880

- 047 HIGHEST

CONCENTRA

TION AREA URBAN

SCALE INDUSTRIAL RURAL 1/1/1973

471650007 Sumner SLAMS 88101 PM2.5 R & P CO

PLUS

MODEL

2025PM SEQ GRAVIMETRI

C RFPS

- 0498

- 118 POPULATION

EXPOSURE AREA URBAN

SCALE INDUSTRIAL RURAL 1/1/1973

471650007 Sumner SLAMS 88101 PM2.5 R & P CO

PLUS

MODEL

2025PM SEQ GRAVIMETRI

C RFPS

- 0498

- 118 UNKNOWN NULL NULL INDUSTRIAL RURAL 1/1/1973

471650007 Sumner SPECIA

L

PURPO

SE 88501 PM2.5

Cont TEOM

Gravimetric 50 deg C POPULATION

EXPOSURE AREA URBAN

SCALE INDUSTRIAL RURAL 1/1/1973

471650101 Sumner SLAMS 44201 O3 THERMO

ELECTRO

N 49 ULTRA

VIOLET EQO

A

0880

- 047 POPULATION

EXPOSURE AREA URBAN

SCALE AGRICULTUR

AL RURAL 4/1/1988

471870106 Williamson SLAMS 44201 O3 THERMO

ELECTRO

N 49 ULTRA

VIOLET EQO

A

0880

- 047 POPULATION

EXPOSURE NULL NULL AGRICULTUR

AL RURAL 4/11/1997

471890103 Wilson SLAMS 44201 O3 THERMO

ELECTRO

N 49 ULTRA

VIOLET EQO

A

0880

- 047 HIGHEST

CONCENTRA

TION AREA URBAN

SCALE FOREST RURAL 5/1/1988

## 45 

# Memphis, TN

- MS

- AR Area

## 46 Tennessee’s Interpretation of Ambient Air Monitors Needed to meet the 40CFR, Part 58 Requirements

Census Area Identification and Population Data 14129

Lead 42101
CO 42401
SO2 42602
NO2 44201 Ozone 81102

PM 10 88101 PM 2.5 88502
PM 2.5 Speciation 88101 or

88501 PM
2.5 Cont

CBSA
2003
Code Census

2000
/Est.

2009 CBSA 2003 Title

(MS Areas)

Operating Required Operating Required Operating Required Operating Required Operating 

### 200 8
20 10
8 Hr

DV Required Operating Required Operating 

### 200 8
20 10
Annual

DV ug/m 200 8
20 10

24 Hr

DV ug/m

Required Operating Required Operating Required



### 32820 1205204/

1304926 Memphis, TN

- MS

AR 1 1 1 1 1 1 1 3 

### 1 2 0.076 2 2 2 

### 2 3 2 

### 10.8 23 2 1 1 1 1

1 

### The Memphis and Shelby County Health Department and the states of Arkansas and Mississippi have implemented a joint MOA that provides for meeting the MSA monitoring requirements for the com bined MSA area. See Appendix 2 for the monitoring agreement. 2 

### Includes collocated monitor. 3 

### Monitor located at Shelby Farms NCore site. There is also an NO2 monitor located in Marion, Arkansas just to the northwest of downtown Memphis.



## Discussion s of any proposals to re

- locate monitors in the next 18 months and suitability of PM2.5 sites for use in comparisons to the annual

PM2.5 standard :

The TEOM POC 3 PM2.5 particulate monitors and the speciation POC 5 STN monitors are generally not suited to be used for comparisons to the annual PM2.5 standards.

One additional ozone monitor was added at the NCORE site to increase the total number of ozone monitors operated to 3. The S harpe School 47

- 157

- 0014 PM2.5 monitor was

relocated to the NCORE site on Feb. 21, 2011 after approval from EPA.

The need to establish additional NO2 near road monitors is under consideration. No lead monitors are anticipated to be estab lished as there are no sources emitting 0.5 TPY of

lead. No additional SO2 monitors are a nticipated to be required to be established at this time. The NCORE site is projected to include a lead monitor. The proposed requirement for CO monitors to be collocated with the near road NO2 monitors has not been finalized. The need for additional mo nitoring sites may be met by re

- location of existing network sites. Additional monitoring sites will require additional resources for both equipment and operational exp enses.

## 47

AQSID County

Name Monitor

Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd Rep Org RepOrgName

471570014 Shelby SLAMS 88101 PM2.5 1 7 2010 1 3431 SHARPE

AVENUE 32820 +35.085833

- 89.949444 118 0673 Memphis

- Shelby County Health Department

471570016 Shelby SLAMS 81102 PM10 1 7 2010 6 GAS SERVICE

CENTER

MEAGHER

STREET 32820 +35.165746

- 89.970897 064 0673 Memphis

- Shelby County Health Department

471570016 Shelby QA

COLLOC

ATED 81102 PM10 2 7 2010 6 GAS SERVICE

CENTER

MEAGHER

STREET 32820 +35.165746

- 89.970897 064 0673 Memphis

- Shelby County Health Department

471570021 Shelby UNKNO

WN 44201 O3 1 1 2010 Hourly 1330 FRAYSER

BLVD 32820 +35.217501

- 90.019707 087 0673 Memphis

- Shelby County Health Department

471570024 Shelby UNKNO

WN 42101 CO 1 1 2010 Hourly 416 ALABAMA

AVENUE 32820 +35.151194

- 90.041559 093 0673 Memphis

- Shelby County Health Department

471570024 Shelby SLAMS 88502 PM2.5

Cont 3 1 2010 Hourly 416 ALABAMA

AVENUE 32820 +35.151194

- 90.041559 701 0673 Memphis

- Shelby County Health Department

471570024 Shelby TRENDS

SPECIAT

ION 88502 PM Spec 5 7 2010 3 416 ALABAMA

AVENUE 32820 +35.151194

- 90.041559 810 0673 Memphis

- Shelby County Health Department

471570046 Shelby SLAMS 42401 SO2 1 1 2010 Hourly 3065 FITE RD 32820 +35.273460

- 89.961217 100 0673 Memphis

- Shelby County Health Department

471570046 Shelby SLAMS 81102 PM10 1 7 2010 6 3065 FITE RD 32820 +35.273460

- 89.961217 064 0673 Memphis

- Shelby County Health Department

471570047 Shelby SLAMS 88101 PM2.5 1 7 2010 1 1064 BREEDLOVE

STREET 32820 +35.168894

- 90.021537 000 0673 Memphis

- Shelby County Health Department

471570047 Shelby QA

COLLOC

ATED 88101 PM2.5 2 7 2010 1 1064 BREEDLOVE

STREET 32820 +35.168894

- 90.021537 000 0673 Memphis

- Shelby County Health Department

471570075 Shelby Ncore Ncore Ncore 2010 HALEY ROAD 32820 +35.15159

- 89.8502 0673 Memphis

- Shelby County Health Department

471571004 Shelby UNKNO

WN 44201 O3 1 1 2010 Hourly 6855 MUDVILLE

RD. EDMUND

ORGILL PARK 32820 +35.378153

- 89.834470 087 0673 Memphis

- Shelby County Health Department

## 48

AQSID County Name Monitor Type Para Para

Name Monitoring

Instrument Analysis Ref Mtd

ID Monitor Objective

Type Dominant

Source Measurement

Scale Land Use

Type Location

Setting Date Site

Established

471570014 Shelby SLAMS 88101 PM2.5 R & P CO

PLUS MODEL 2025PM SEQ GRAVIMETRI

C RFPS

0498

- 118 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURB

AN 1/2/1971

471570016 Shelby SLAMS 81102 PM10 SIERRA

ANDERSEN/G

MW 321

- B GRAVIMETRI

C RFPS

1287

- 064 HIGHEST

CONCENTRATI

ON AREA NEIGHBORH

OOD INDUST

RIAL URBAN

AND

CENTER

CITY 1/1/1972

471570016 Shelby QA

COLLOC

ATED 81102 PM10 SIERRA

ANDERSEN/G

MW 321

- B GRAVIMETRI

C RFPS

1287

- 064 POPULATION

EXPOSURE AREA NEIGHBORH

OOD INDUST

RIAL URBAN

AND

CENTER

CITY 1/1/1972

471570021 Shelby UNKNO

WN 44201 O3 MODEL 400

OZONE

ANALYZER ULTRA

VIOLET

ABSORPTION EQOA

0992

- 087 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURB

AN 9/1/1972

471570024 Shelby UNKNO

WN 42101 CO API MODEL

300 GAS

FILTER GAS FILTER

CORRELATIO

N CO

ANALYZER RFCA

1093

- 093 MAX

PRECURSOR

EMISSIONS

IMPACT MOBILE MICROSCAL

E RESIDEN

TIAL SUBURB

AN 1/1/1973

471570024 Shelby SLAMS 88502 PM2.5

Cont TEOM

Gravimetric 50 deg C POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURB

AN 1/1/1973

471570024 Shelby TRENDS

SPECIAT

ION 88502 PM Spec

Carbon MetOne Super

SASS

URG 3000 Gravimetric POPULATION

EXPOSURE NULL NULL RESIDEN

TIAL SUBURB

AN 1/1/1973

471570046 Shelby SLAMS 42401 SO2 API MODEL

100 A SO2

ANALYZER ULTRAVIOLE

T

FLUORESCEN

CE EQSA

0495

- 100 POPULATION

EXPOSURE MOBILE URBAN

SCALE INDUST

RIAL SUBURB

AN 5/1/1994

471570046 Shelby SLAMS 81102 PM10 SIERRA

ANDERSEN/G

MW 321

- B GRAVIMETRI

C RFPS

1287

- 064 POPULATION

EXPOSURE NULL NEIGHBORH

OOD INDUST

RIAL SUBURB

AN 5/1/1994

471570047 Shelby SLAMS 88101 PM2.5 #N/A #N/A #N/A POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURB

AN 12/1/1998

471570047 Shelby QA

COLLOC

ATED 88101 PM2.5 #N/A #N/A #N/A POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURB

AN 12/1/1998

471570075 Shelby Ncore Ncore Ncore

471571004 Shelby UNKNO

WN 44201 O3 MODEL 400

OZONE

ANALYZER ULTRA

VIOLET

ABSORPTION EQOA

0992

- 087 HIGHEST

CONCENTRATI

ON MOBILE URBAN

SCALE AGRICU

LTURAL RURAL 1/1/1980

## 49 

# Knoxville, TN Area

## 50 Tennessee’s Interpretation of Ambient Air Monitors Needed to meet the 40CFR, Part 58 Requirements

Census Area Identification and Population Data 14129

Lead 42101

CO 42401
SO2 42602
NO2 44201 Ozone 81102

PM 10 88101 PM 2.5 88502 PM 2.5 Speciation 88101 or

88501 PM
2.5 Cont

CBSA
2003
Code Census

2000
/Est.

2009 CBSA 2003 Title

(MS Areas)

Operating Required Operating Required Operating Required Operating Required Operating 

### 200 8
20 10
8 Hr

DV Required Operating Required Operating 

### 200 8
20 10

Annual DV ug/m 200 8

20 10

24 Hr

DV ug/m Required Operating Required Operating Required



### 28940 616079/

699247 Knoxville, TN 4 1 

### 2 1 0 0 1 0 0 6 0.077 2 5 1 

### 2 7 1 

### 13. 1 26 1 1 1 3 1

1 

### Includes collocated monitor.



## Discussions of any proposals to re

- locate monitors in the next 18 months and suitability of PM2.5 sites for use in comparisons to the annual

PM2.5 standard :

The TEOM POC 3 PM2.5 particulate monitors and the speciation POC 5 STN monitors are generally not suited to be used for compa risons to the annual PM2.5 standards.

The collocated PM2.5 monitor at site 47

- 093

- 1017 was relocated to site 47

- 093

- 0028 on Apri l 11, 2011 with EPA’s approval. This collocated sampler will operate on a 6

- day

schedule.

Due to new developments the lead monitor located near Ameristeel is no longer positioned to measure maximum lead concentratio ns at the fence line of the source. Ag ency is working with EPA Region 4 to identify an acceptable monitoring site. The need to establish additional NO2 near road monitors and t he proposed requirement for CO monitors

to be collocated with the near road NO2 monitors has not been finalized. An SO2 monitoring site is need ed to be established to meet the PWEI requirements. Although an

SO2 monitor is operating at the NCORE site, it may not meet the PWEI requirements. If not, a new monitoring site will be established to meet the January 1, 2013 mo nitoring

deadline.

The need for additional monitoring sites may be met by re

- location of existing network sites. Additional monitoring sites will require additional resources for both equipment and operational expenses.

## 51

AQSID County

Name Monitor Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd 

### RepOrg RepOrgName

470930021 Knox SLAMS 44201 O3 1 1 2010 Hourly 9315 RUTLEDGE

PIKE MASCOT

TN 37806 28940 +36.085508

- 83.764806 047 

### 0581 Knox County Department Of

Air Pollution

Control

470930027 Knox SLAMS 14129 Pb 1 7 2010 6 2522 BURNSIDE

ST KNOXVILLE

TN 37921 28940 +35.983056

- 83.952253 107 

### 0581 Knox County Department Of

Air Pollution

Control

470930027 Knox SLAMS 14129 Pb 2 7 2010 6 2522 BURNSIDE

ST KNOXVILLE

TN 37921 28940 +35.983056

- 83.952253 107 

### 0581 Knox County Department Of

Air Pollution

Control

470930028 Knox SLAMS 88101 PM2.5 1 7 2010 1 1000 FRANCIS

ROAD 28940 +35.944601

- 84.035980 118 

### 0581 Knox County Department Of

Air Pollution

Control

470930028 Knox SLAMS 88101 PM2.5 2 7 2010 1 1000 FRANCIS

ROAD 28940 +35.944601

- 84.035980 118 

### 0581 Knox County Department Of

Air Pollution

Control

470931013 Knox SLAMS 81102 PM10 1 7 2010 6 1403 DAVANNA

STREET Knoxville, Tn

37917 28940 +35.980421

- 83.932814 064 

### 0581 Knox County Department Of

Air Pollution

Control

470931013 Knox SPECIAL

PURPOSE 81102 PM10 2 7 2010 6 1403 DAVANNA

STREET Knoxville, Tn

37917 28940 +35.980421

- 83.932814 064 

### 0581 Knox County Department Of

Air Pollution

Control

470931013 Knox SPECIAL

PURPOSE 88101 PM2.5 1 7 2010 6 1403 DAVANNA

STREET Knoxville, Tn

37917 28940 +35.980421

- 83.932814 118 

### 0581 Knox County Department Of

Air Pollution

Control

470931013 Knox SPECIAL

PURPOSE 88501 PM2.5

Cont 3 1 2010 Hourly 1403 DAVANNA

STREET Knoxville, Tn

37917 28940 +35.980421

- 83.932814 702 

### 0581 Knox County Department Of

Air Pollution

Control

470931017 Knox SLAMS 14129 Pb 1 7 2010 6 1613 VERMONT

AVENUE 28940 +35.978074

- 83.950666 107 

### 0581 Knox County Department Of

Air Pollution

Control

## 52

AQSID County

Name Monitor Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd 

### RepOrg RepOrgName

470931017 Knox SLAMS 88101 PM2.5 1 7 2010 1 1613 VERMONT

AVENUE 28940 +35.978074

- 83.950666 118 

### 0581 Knox County Department Of

Air Pollution

Control

470931020 Knox SLAMS 44201 O3 1 1 2010 Hourly 4625 MILDRED

DRIVE 28940 +36.019186

- 83.873810 047 

### 0581 Knox County Department Of

Air Pollution

Control

470931020 Knox SLAMS 88101 PM2.5 1 7 2010 1 4625 MILDRED

DRIVE 28940 +36.019186

- 83.873810 118 

### 0581 Knox County Department Of

Air Pollution

Control

470931020 Knox SUPLMNTL

SPECIATION 88502 PM Spec
Carbon 5 7 2010 6 4625 MILDRED

DRIVE 28940 +36.019186

- 83.873810 810 

### 0581 Knox County Department Of

Air Pollution

Control

47093STBD Knox SLAMS 14129 Pb 1 7 201 1 6 1584 ELY

AVENUE 28940 +35.98049

- 83.95422 107 0581 

### Knox County Department Of

Air Pollution

Control

470090101 Blount OTHER 44201 O3 1 1 2010 Hourly GREAT SMOKY

MOUNTAINS NP

LOOK ROCK 28940 +35.631490

- 83.943512 047 

### 0745 National Park

Service

470010101 Anderson OTHER 44201 O3 1 1 2010 Hourly FREELS BEND_STUDY

AREA MELTON

LAKE 28940 +35.963273

- 84.223234 087 

### 1025 Tennessee
Division Of Air

Pollution Control

470090011 Blount SPECIAL

PURPOSE 88101 PM2.5 1 7 2010 3 2007 SEQUOYAH

AVENUE 28940 +35.768431

- 83.942123 118 

### 1025 Tennessee
Division Of Air

Pollution Control

470090011 Blount SPECIAL

PURPOSE 88501 PM2.5

Cont 3 1 2010 Hourly 2007 SEQUOYAH

AVENUE 28940 +35.768431

- 83.942123 716 

### 1025 Tennessee
Division Of Air

Pollution Control

470090101 Blount SPECIAL

PURPOSE 88501 PM2.5

Cont 3 1 2010 Hourly GREAT SMOKY

MOUNTAINS NP

LOOK ROCK 28940 +35.631490

- 83.943512 703 

### 1025 Tennessee
Division Of Air

Pollution Control

470090102 Blount NON

- EPA

FEDERAL 44201 O3 1 1 2010 Hourly GREAT SMOKY

MOUNTAINS NP

- CADES COVE 28940 +35.603056

- 83.783611 053 

### 1025 Tennessee
Division Of Air

Pollution Control

471050108 Loudon SPECIAL

PURPOSE 88101 PM2.5 1 7 2010 3 130 WEBB

DRIVE 28940 +35.744799

- 84.317313 118 

### 1025 Tennessee
Division Of Air

Pollution Control

471050109 Loudon SPECIAL 44201 O3 1 1 2010 Hourly 1703 ROBERTS 28940 +35.720932

- 84.341581 087 

### 1025 Tennessee

## 53

AQSID County

Name Monitor Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd 

### RepOrg RepOrgName

PURPOSE RD 

### Division Of Air

Pollution Control

471730107 Union OTHER 81102 PM10

Cont 1 1 2010 Hourly DONAHUE

PROPERTY ON

DONAHUE

ROAD 28940 +36.224167

- 83.714444 079 

### 1025 Tennessee
Division Of Air

Pollution Control

471730105 Union OTHER 81102 PM10 1 7 2010 6 LUTTRELL

SMITH HOUSE

DONAHEW RD. 28940 +36.228145

- 83.709615 063 

### 1027 Tennessee Luttrell

Lime

471730105 Union OTHER 81102 PM10 2 7 2010 6 LUTTRELL

SMITH HOUSE

DONAHEW RD. 28940 +36.228145

- 83.709615 063 

### 1027 Tennessee Luttrell

Lime

470090101 Blount SPECIAL

PURPOSE 42101 CO 2 1 2010 Hourly GREAT SMOKY

MOUNTAINS NP

LOOK ROCK 28940 +35.631490

- 83.943512 055 

### 1029 Tennessee Valley Authority

470090101 Blount SPECIAL

PURPOSE 42401 SO2 2 1 2010 Hourly GREAT SMOKY

MOUNTAINS NP

LOOK ROCK 28940 +35.631490

- 83.943512 560 

### 1029 Tennessee Valley Authority

470090101 Blount SPECIAL

PURPOSE 42602 NO2 3 1 2010 Hourly GREAT SMOKY

MOUNTAINS NP

LOOK ROCK 28940 +35.631490

- 83.943512 599 

### 1029 Tennessee Valley Authority

## 54

AQSID County

Name Monitor

Type Para Para

Name Monitoring

Instrument Analysis Ref Mtd

ID Monitor Objective

Type Dominant

Source Measurement

Scale Land Use

Type Location

Setting Date Site

Established

470930021 Knox SLAMS 44201 O3 THERMO

ELECTRON 49 ULTRA

VIOLET EQOA

0880

- 047 HIGHEST

CONCENTRATI

ON NULL URBAN

SCALE AGRICU

LTURAL RURAL 6/1/1981

470930027 Knox SLAMS 14129 Pb PB

TSP/FLAMELESS

AA Flameless

Atomic absorption (GFAA); 3M
HNO3 Boil 30

min EQL

0895

- 107 SOURCE

ORIENTED POINT NEIGHBORH

OOD INDUST

RIAL URBAN

AND

CENTER

CITY 12/4/1994

470930027 Knox SLAMS 14129 Pb PB

TSP/FLAMELESS

AA Flameless

Atomic absorption (GFAA); 3M

HNO3 Boil 30

min EQL

0895

- 107 SOURCE

ORIENTED POINT NEIGHBORH

OOD INDUST

RIAL URBAN

AND

CENTER

CITY 12/4/1994

470930028 Knox SLAMS 88101 PM2.5 R & P CO PLUS

MODEL 2025PM SEQ GRAVIMETRI

C RFPS

0498

- 118 POPULATION

EXPOSURE MOBILE NEIGHBORH

OOD MOBILE SUBURBA

N 1/1/1999

470930028 Knox SLAMS 88101 PM2.5 R & P CO PLUS

MODEL 2025PM SEQ GRAVIMETRI

C RFPS

0498

- 118 POPULATION

EXPOSURE MOBILE NEIGHBORH

OOD MOBILE SUBURBA

N 1/1/1999

470931013 Knox SLAMS 81102 PM10 SIERRA

ANDERSEN/GMW

321

- B GRAVIMETRI

C RFPS

1287

- 064 POPULATION

EXPOSURE MOBILE NEIGHBORH

OOD MOBILE URBAN

AND

CENTER

CITY 1/1/1975

470931013 Knox SPECIAL

PURPOS

E 81102 PM10 SIERRA

ANDERSEN/GMW

321

- B GRAVIMETRI

C RFPS

1287

- 064 POPULATION

EXPOSURE MOBILE NEIGHBORH

OOD MOBILE URBAN

AND

CENTER

CITY 1/1/1975

470931013 Knox SPECIAL

PURPOS

E 88101 PM2.5 R & P CO PLUS

MODEL 2025PM SEQ GRAVIMETRI

C RFPS

0498

- 118 POPULATION

EXPOSURE MOBILE MIDDLE

SCALE MOBILE URBAN

AND

CENTER

CITY 1/1/1975

470931013 Knox SPECIAL

PURPOS

E 88501 PM2.5

Cont TEOM
Gravimetric 50 deg C POPULATION

EXPOSURE MOBILE MIDDLE

SCALE MOBILE URBAN

AND

CENTER

CITY 1/1/1975

470931017 Knox SLAMS 14129 Pb PB

TSP/FLAMELESS

AA Flameless

Atomic absorption (GFAA); 3M

HNO3 Boil 30

min EQL

0895

- 107 POPULATION

EXPOSURE NULL NULL RESIDEN

TIAL URBAN

AND

CENTER

CITY 4/1/1978

470931017 Knox SLAMS 88101 PM2.5 R & P CO PLUS

MODEL 2025PM SEQ GRAVIMETRI

C RFPS

0498

- 118 POPULATION

EXPOSURE MOBILE NEIGHBORH

OOD RESIDEN

TIAL URBAN

AND

CENTER

CITY 4/1/1978

470931020 Knox SLAMS 44201 O3 THERMO

ELECTRON 49 ULTRA

VIOLET EQOA

0880

- 047 POPULATION

EXPOSURE AREA NEIGHBORH

OOD MOBILE SUBURBA

N 1/1/1981

470931020 Knox SLAMS 88101 PM2.5 R & P CO PLUS

MODEL 2025PM GRAVIMETRI

C RFPS

0498

- POPULATION

EXPOSURE MOBILE NEIGHBORH

OOD MOBILE SUBURBA

N 1/1/1981

## 55

AQSID County

Name Monitor

Type Para Para

Name Monitoring

Instrument Analysis Ref Mtd

ID Monitor Objective

Type Dominant

Source Measurement

Scale Land Use

Type Location

Setting Date Site

Established SEQ 118

470931020 Knox SUPLMN

TL

SPECIAT

ION 88502 PM Spec

Carbon MetOne Super SASS

URG 3000 Gravimetric POPULATION

EXPOSURE NULL NULL MOBILE SUBURBA

N 1/1/1981

47093STB

D Knox SLAMS 14129 Pb PB

TSP/FLAMELESS

AA Flameless

Atomic absorption (GFAA); 3M

HNO3 Boil 30

min EQL

0895

- 107 POPULATION

EXPOSURE POINT NULL RESIDEN

TIAL URBAN

AND

CENTER

CITY 4/1/1978

470090101 Blount OTHER 44201 O3 THERMO

ELECTRON 49 ULTRA

VIOLET EQOA

0880

- 047 UNKNOWN AREA NEIGHBORH

OOD FOREST RURAL 1/1/1980

470010101 Anderso

n OTHER 44201 O3 MODEL 400

OZONE

ANALYZER ULTRA

VIOLET

ABSORPTION EQOA

0992

- 087 POPULATION

EXPOSURE AREA URBAN

SCALE FOREST RURAL 4/1/1992

470090011 Blount SPECIAL

PURPOS

E 88101 PM2.5 R & P CO PLUS

MODEL 2025PM SEQ GRAVIMETRI

C RFPS

0498

- 118 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 5/1/2000

470090011 Blount SPECIAL

PURPOS

E 88501 PM2.5

Cont TEOM

Gravimetric 50 deg C POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 5/1/2000

470090101 Blount SPECIAL

PURPOS

E 88501 PM2.5

Cont TEOM

Gravimetric 30 deg C REGIONAL

TRANSPORT AREA REGIONAL

SCALE FOREST RURAL 1/1/1980

470090102 Blount NON

EPA

FEDERA

L 44201 O3 MONITOR LABS

8810 ULTRA

VIOLET EQOA

0881

- 053 HIGHEST

CONCENTRATI

ON NULL REGIONAL

SCALE FOREST RURAL 5/1/1994

471050108 Loudon SPECIAL

PURPOS

E 88101 PM2.5 R & P CO PLUS

MODEL 2025PM SEQ GRAVIMETRI

C RFPS

0498

- 118 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 8/1/2003

471050109 Loudon SPECIAL

PURPOS

E 44201 O3 MODEL 400

OZONE

ANALYZER ULTRA

VIOLET

ABSORPTION EQOA

0992

- 087 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 2/1/2006

471730107 Union OTHER 81102 PM10

Cont RUPRCHT&PATSH

NCK TEOM SER

1400 TEOM

GRAVIMETRI

C EQPM

1090

- 079 UNKNOWN NULL NULL AGRICU

LTURAL RURAL 10/25/1996

471730105 Union OTHER 81102 PM10 GMW Model 1200 GRAVIMETRI

C RFPS

1287

- 063 UNKNOWN POINT NULL AGRICU

LTURAL RURAL 3/1/1984

471730105 Union OTHER 81102 PM10 GMW Model 1200 GRAVIMETRI

C RFPS

1287

- 063 UNKNOWN POINT NULL AGRICU

LTURAL RURAL 3/1/1984

470090101 Blount SPECIAL

PURPOS

E 42101 CO Gas Filter

Correlation

Thermo

Electron 48C

TL UNKNOWN NULL NULL FOREST RURAL 1/1/1980

470090101 Blount SPECIAL

PURPOS

E 42401 SO2 Thermo Electron

43c

- TLE/43i

- TLE Pulsed

Fluorescent

43C

- TLE/43i

EQSA

0486

- 060 UNKNOWN NULL NULL FOREST RURAL 1/1/1980

## 56

AQSID County

Name Monitor

Type Para Para

Name Monitoring

Instrument Analysis Ref Mtd

ID Monitor Objective

Type Dominant

Source Measurement

Scale Land Use

Type Location

Setting Date Site

Established

TLE

470090101 Blount SPECIAL

PURPOS

E 42602 NO2 Chemiluminesc ence Teledyne

API 200 EU/501w/photo lytic converter GENERAL/BAC

KGROUND NULL NULL FOREST RURAL 1/1/1980

## 57 

# Chattanooga, TN

- GA Area

## 58 Tennessee’s Interpretation of Ambient Air Monitors Needed to meet the 40CFR, Part 58 Requirements

Census Area Identification and Population Data 14129

Lead 42101

CO 42401
SO2 42602
NO2 44201 Ozone 81102 PM 10 88101 PM 2.5 88502
PM 2.5 Speciatio

n 88101 or
88501 PM
2.5 Cont

CBSA

2003
Code Census
2000
/Est.

2009 CBSA 2003 Title

(MS Areas)

Operating Required Operating Required Operating Required Operating Required Operating 

### 200 8
20 10
8 Hr

DV Required Operating Required Operating 

### 200 8
20 10

Annual DV ug/m 200 8

20 10 24

Hr DV ug/m Required Operating Required Operating Required



### 16860 476531/
524303 Chattanooga, TN

GA 0 0 0 0 0 0 0 0 2 0.075 1 2 1 

### 0 5 1 

### 11.6 25 1 1 1 1 1

1 

### Includes collocated monitor.



## Discussions of any proposals to re

- locate monitors in the next 18 months and suitability of PM2.5 sites for use in comparisons to the annual

PM2.5 standard :

T he TEOM POC 3 PM2.5 particulate monitors and the speciation POC 5 STN monitors are generally not suited to be used for compar isons to the annual PM2.5 standards.

There are plans to relocate the Eastside Utility District 47

- 065

- 4003 ozone monitoring site t o a new location preferably within a 1 mile radius of the existing site before the start of the 2012 ozone monitoring season. This is due to continued difficulty in access to the site because of security gates

.

The POC 2 PM2.5 sampler was shut down at si te 47

- 065

- 0031 in Jan. 2010.

No lead or SO2 monitors are anticipated to be required to be established. The need to establish additional NO2 near road monitors is under consideration. The proposed requirement for CO monitors to be collocated with the near road NO2 monitors has not been finalized. The need for additional monitoring sites may be met by re

- location of existing network sites. Additional monitoring sites will require additional resources for both equipment and operational exp enses.

## 59

AQS ID County

Name Monitor Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd 

### RepOrg RepOrgName

470650006 Hamilton SLAMS 81102 PM10 1 7 2010 6 3300 SOUTH

BROAD

STREET. 33RD AND BROAD, 16860 +35.017139

- 85.322056 064 0170 Chattanooga

- Hamilton County Air Pollution

Control

470650006 Hamilton SLAMS 81102 PM10 2 7 2010 6 3300 SOUTH

BROAD

STREET. 33RD AND BROAD, 16860 +35.017139

- 85.322056 064 0170 Chattanooga

- Hamilton County Air Pollution

Control

470650031 Hamilton SPECIAL

PURPOSE 88101 PM2.5 1 7 2010 3 1517 TOMBRAS AVENUE, EAST

RIDGE 16860 +34.994555

- 85.242872 118 0170 Chattanooga

- Hamilton County Air Pollution

Control

470651011 Hamilton UNKNOWN 44201 O3 1 1 2010 Hourly SODDY DAISY

H.S. 006 18 SEQUOYAH RD 16860 +35.233527

- 85.181806 000 0170 Chattanooga

- Hamilton County Air Pollution

Control

470651011 Hamilton SPECIAL

PURPOSE 88101 PM2.5 1 7 2010 6 SODDY DAISY

H.S. 006 18 SEQUOYAH RD 16860 +35.233527

- 85.181806 118 0170 Chattanooga

- Hamilton County Air Pollution

Control

470654002 Hamilton SLAMS 88101 PM2.5 1 7 2010 3 RIVERSIDE

SUBSTATION

911 SISKIN DR 16860 +35.050928

- 85.292975 118 0170 Chattanooga

- Hamilton County Air Pollution

Control

470654002 Hamilton SLAMS 88101 PM2.5 2 7 2010 3 RIVERSIDE

SUBSTATION

911 SISKIN DR 16860 +35.050928

- 85.292975 118 0170 Chattanooga

- Hamilton County Air Pollution

Control

470654002 Hamilton IMPROVE 88501 PM2.5

Cont 3 1 2010 Hourly RIVERSIDE

SUBSTATION

911 SISKIN DR 16860 +35.050928

- 85.292975 715 0170 Chattanooga

- Hamilton County Air Pollution

Control

470654002 Hamilton SU PLMNTL

SPECIATION 88502 PM Spec

Carbon 5 7 2010 6 RIVERSIDE

SUBSTATION

911 SISKIN DR 16860 +35.050928

- 85.292975 810 0170 Chattanooga

- Hamilton County Air Pollution

Control

470654003 Hamilton SLAMS 44201 O3 1 1 2010 Hourly 6200 BONNY

OAKS DRIVE

EASTSIDE

UTILITY F 16860 +35.102638

- 85.162194 047 0170 Chattanooga

- Hamilton County Air Pollution

Control

## 60

AQSID County

Name Monitor

Type Para Para

Name Monitoring

Instrument Analysis Ref Mtd

ID Monitor Objective

Type Dominant

Source Measurement

Scale Land Use

Type Location

Setting Date Site

Established

470650006 Hamilton SLAMS 8110 2 PM10 SIERRA

ANDERSEN/GMW

321

- B GRAVIMETRI

C RFPS

1287

- 064 UNKNOWN AREA URBAN

SCALE INDUST

RIAL URBAN

AND

CENTER

CITY 1/1/1965

470650006 Hamilton SLAMS 81102 PM10 SIERRA

ANDERSEN/GMW

321

- B GRAVIMETRI

C RFPS

1287

- 064 UNKNOWN AREA URBAN

SCALE INDUST

RIAL URBAN

AND

CENTER

CITY 1/1/1965

470650031 Hamilton SPECIA

L

PURPO

SE 88101 PM2.5 R & P CO PLUS

MODEL 2025PM SEQ GRAVIMETRI

C RFPS

0498

- 118 REGIONAL

TRANSPORT AREA NEIGHBORH

OOD COMME

RCIAL URBAN

AND

CENTER

CITY 5/6/1999

470651011 Hamilton UNKNO

WN 44201 O3 #N/A #N/A #N/A HIGHEST

CONCENTRATI

ON AREA REGIONAL

SCALE AGRICU

LTURAL RURAL 8/1/1978

470651011 Hamilton SPECIA

L

PURPO

SE 88101 PM2.5 R & P CO PLUS

MODEL 2025PM SEQ GRAVIMETRI

C RFPS

0498

- 118 REGIONAL

TRANSPORT NULL REGIONAL

SCALE AGRICU

LTURAL RURAL 8/1/1978

470654002 Hamilton SLAMS 88101 PM2.5 R & P CO PLUS

MODEL 2025PM SEQ GRAVIMETRI

C RFPS

0498

- 118 POPULATION

EXPOSURE NULL URBAN

SCALE COMME

RCIAL URBAN

AND

CENTER

CITY 1/1/1999

470654002 Hamilton SLAMS 88101 PM2.5 R & P CO PLUS

MODEL 2025PM SEQ GRAVIMETRI

C RFPS

0498

- 118 POPULATION

EXPOSURE NULL URBAN

SCALE COMME

RCIAL URBAN

AND

CENTER

CITY 1/1/1999

470654002 Hamilton IMPRO

VE 88501 PM2.5

Cont TEOM

Gravimetric 30 deg C POPULATION

EXPOSURE AREA URBAN

SCALE COMME

RCIAL URBAN

AND

CENTER

CITY 1/1/1999

470654002 Hamilton SUPLM

NTL

SPECIA

TION 88502 PM Spec

Carbon MetOne Super SASS

URG 3000 Gravimetric POPULATION

EXPOSURE NULL NULL COMME

RCIAL URBAN

AND

CENTER

CITY 1/1/1999

470654003 Hamilton SLAMS 44201 O3 THERMO

ELECTRON 49 ULTRA

VIOLET EQOA

0880

- 047 POPULATION

EXPOSURE MOBILE NEIGHBORH

OOD INDUST

RIAL RURAL 3/1/2004

## 61 

# Kingsport Bristol Johnson City Area

## 62 Tennessee’s Interpretation of Ambient Air Monitors Needed to meet the 40CFR, Part 58 Requirements

Census Area Identification and Population Data 14129

Lead 42101

CO 42401
SO2 42602
NO2 44201 Ozone 81102 PM
10 88101 PM 2.5 88502 PM
2.5 Speciation 88101 or

88501 PM 2.5
Cont

CBSA
2003
Code Census
2000
/Est.

2009 CBSA 2003 Title

(MS Areas)

Operating Required Operating Required Operating Required Operating Required Operating 

### 200 8
20 10
8 Hr

DV Required Operating Required Operating 

### 200 8
20 10
Annual

DV ug/m 200 8
20 10

24 Hr

DV ug/m Required Operating Required Operating Required



### 27740 181607/

197381 Johnson City, TN 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

Census Area Identification and Population Data 14129
Lead 42101

CO 42401
SO2 42602
NO2 44201 Ozone 81102 PM
10 88101 PM 2.5 88502 PM
2.5 Speciation 88101 or

88501 PM 2.5
Cont

CBSA

2003
Code Census

2000
/Est.

2009 CBSA 2003 Title

(MS Areas)

Operating Required Operating Required Operating Required Operating Required Operating 

### 200 8
20 10
8 Hr

DV Required Operating Required Operating 

### 200 8
20 10

Annual

DV ug/m 200 8
20 10

24 Hr

DV ug/m Required Operating Required Operating Required



### 28700 298484/

305629 Kingsport

- Bristol

Bristol, TN

- VA 5 4 

### 1 1 0 1 1 1 0 2 0.071 1 0 0 1 11.0 23 1 0 0 1 1

1 

### The two ozone sites in the Kingsport

- Bristol MSA should be sufficient to assess ozone levels in the Johnson City MSA. 2 

### Historical PM10 data does not reflect a need for PM10 monitoring in this area. 3 

### PM2.5 monitoring in the Kingsport

- Bristol MSA should be sufficient to assess PM 2.5 levels in the Johnson City MSA. 4 

### Includes collocated

monitor.



## Discussions of any proposals to re

- locate monitors in the next 18 months and suitability of PM2.5 sites for use in comparisons to the annual

PM2.5 standard :

The TEOM POC 3 PM2.5 particulate monitors and the speciation POC 5 STN monitors are generally not suited to be used for compa risons to the annual PM2.5 standards.

There are no plans to relocate or shutdown a ny existing monitoring sites in the MSA area described.

The need to establish additional NO2 near road monitors, PWEI required SO2 monitors and Lead monitoring sites at sources emit ting 0.5 TPY of lead is under consideration. The proposed requirement f or CO monitors to be collocated with the near road NO2 monitors has not been finalized. The need for additional monitoring s ites may be met by

re

- location of existing network sites. Additional monitoring sites will require additional resources for both e quipment and operational expenses.

## 63

AQSID County

Name Monitor Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd 

### RepOrg RepOrgName

471633001 Sullivan INDUSTRIAL 14129 Pb 1 7 2010 3 364 EXIDE DR. 28700 +36.525556

- 82.273333 107 0375 Exide Corporation

471633002 Sullivan INDUSTRIAL 14129 Pb 1 7 2010 3 364 EXIDE DR.

ON EXIDE

PROPERTY 28700 +36.524722

- 82.268056 107 0375 Exide Corporation

471633002 Sullivan INDUSTRIAL 14129 Pb 2 7 2010 3 364 EXIDE DR.

ON EXIDE

PROPERTY 28700 +36.524722

- 82.268056 107 0375 Exide Corporation

471633003 Sullivan INDUSTRIAL 14129 Pb 1 7 2010 3 364 EXIDE DR. 28700 +36.528056

- 82.268333 107 0375 Exide Corporation

471630007 Sullivan OTHER 42101 CO 1 1 2010 Hourly EASTMAN ROSS

N.ROBINSON 28700 +36.534804

- 82.517078 041 1026 Tennessee Eastman Company

471630007 Sullivan OTHER 42401 SO2 1 1 2010 Hourly EASTMAN ROSS

N.ROBINSON 28700 +36.534804

- 82.517078 039 1026 Tennessee Eastman Company

471630007 Sullivan OTHER 42602 NO2 1 1 2010 Hourly EASTMAN ROSS

N.ROBINSON 28700 +36.534804

- 82.517078 042 1026 Tennessee Eastman Company

471631007 Sullivan SLAMS 88101 PM2.5 1 7 2010 3 1649 D STREET 28700 +36.540654

- 82.521667 118 1025 Tennessee Division

Of Air Pollution

Control

471631007 Sullivan SPECIAL

PURPOSE 88501 PM2.5

Cont 3 1 2010 Hourly 1649 D STREET 28700 +36.540654

- 82.521667 716 1025 Tennessee Division

Of Air Pollution

Control

471632002 Sullivan UNKNOWN 44201 O3 1 1 2010 Hourly HILL ROAD 28700 +36.541193

- 82.425964 053 1025 Tennessee Division

Of Air Pollution

Control

471632003 Sullivan SLAMS 44201 O3 1 1 2010 Hourly KETRON

MIDDLE

SCHOOL ON

BLOOMINGDALE

RD. 28700 +36.582222

- 82.485833 053 1025 Tennessee Division

Of Air Pollution

Control

471633004 Sullivan SLAMS 14129 Pb 1 7 2010 6 364 Exide Dr 28700 +36.525556

- 82.273333 000 1025 Tennessee Division

Of Air Pollution

Control

471633004 Sullivan SLAMS 14129 Pb 2 7 2010 6 364 Exide Dr 28700 +36.525556

- 82.273333 000 1025 Tennessee Division

Of Air Pollution

Control

## 64

AQSID County

Name Monitor

Type Para Para

Name Monitoring

Instrument Analysis Ref Mtd

ID Monitor Objective

Type Dominant

Source Measurement

Scale Land Use

Type Location

Setting Date Site

Established

471633001 Sullivan INDUST

RIAL 14129 Pb PB

TSP/FLAMEL

ESS AA Flameless Atomic

absorption (GFAA);

3M HNO3 Boil 30

min EQL

0895

- 107 SOURCE

ORIENTED NULL NULL INDUST

RIAL SUBURBA

N 7/1/1994

471633002 Sullivan INDUST

RIAL 14129 Pb PB

TSP/FLAMEL

ESS AA Flameless Atomic

absorption (GFAA);

3M HNO3 Boil 30

min EQL

0895

- 107 SOURCE

ORIENTED NULL NULL INDUST

RIAL SUBURBA

N 7/1/1994

471633002 Sullivan INDUST

RIAL 14129 Pb PB

TSP/FLAMEL

ESS AA Flameless Atomic

absorption (GFAA);

3M HNO3 Boil 30

min EQL

0895

- 107 SOURCE

ORIENTED NULL NULL INDUST

RIAL SUBURBA

N 7/1/1994

471633003 Sullivan INDUST

RIAL 14129 Pb PB

TSP/FLAMEL

ESS AA Flameless Atomic

absorption (GFAA);

3M HNO3 Boil 30

min EQL

0895

- 107 UPWIND

BACKGROUND NULL NULL INDUST

RIAL SUBURBA

N 7/1/1994

471630007 Sullivan OTHER 42101 CO MONITOR

LABS 8310 NONDISPERSIVE

INFRARED RFCA

0979

- 041 HIGHEST

CONCENTRATI

ON POINT MIDDLE

SCALE RESIDEN

TIAL SUBURBA

N 1/1/1974

471630007 Sullivan OTHER 42401 SO2 MONITOR

LABS 8850 ULTRA VIOLET

STIMULATED

FLUORESCNC EQSA

0779

- 039 HIGHEST

CONCENTRATI

ON POINT NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 1/1/1974

471630007 Sullivan OTHER 42602 NO2 MONITOR

LABS 8840 CHEMILUMINESC

ENCE RFNA

0280

- 042 HIGHEST

CONCENTRATI

ON POINT NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 1/1/1974

471631007 Sullivan SLAMS 88101 PM2.5 R & P CO

PLUS MODEL 2025PM SEQ GRAVIMETRIC RFPS

0498

- 118 POPULATION

EXPOSURE NULL NULL RESIDEN

TIAL SUBURBA

N 10/1/1998

471631007 Sullivan SPECIA

L

PURPO

SE 88501 PM2.5

Cont TEOM Gravimetric 50 deg C UPWIND

BACKGROUND AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 10/1/1998

471632002 Sullivan UNKNO

WN 44201 O3 MONITOR

LABS 8810 ULTRA VIOLET EQOA

0881

- 053 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL RURAL 1/1/1980

471632003 Sullivan SLAMS 44201 O3 MONITOR

LABS 8810 ULTRA VIOLET EQOA

0881

- 053 POPULATION

EXPOSURE NULL NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 4/1/1995

471633004 Sullivan SLAMS 14129 Pb #N/A #N/A #N/A SOURCE

ORIENTED POINT URBAN

SCALE INDUST

RIAL URBAN

AND

CENTER

CITY 1/1/2010

471633004 Sullivan SLAMS 14129 Pb #N/A #N/A #N/A SOURCE

ORIENTED POINT URBAN

SCALE INDUST

RIAL URBAN

AND

CENTER

CITY 1/1/2010

## 65 

# Clarksville, TN

- KY Area

## 66 Tennessee’s Interpretation of Ambient Air Monitors Needed to meet the 40CFR, Part 58 Requirements

Census Area Identification and Population Data 14129

Lead 42101

CO 42401
SO2 42602
NO2 44201 Ozone 81102 PM
10 88101 PM 2.5 88502
PM 2.5 Speciation 88101 or

88501 PM 2.5
Cont

CBSA

2003
Code Census

2000
/Est.

2009 CBSA 2003 Title

(MS Areas)

Operating Required Operating Required Operating Required Operating Required Operating 

### 200 8
20 10
8 Hr

DV Required Operating Required Operating 

### 200 8
20 10

Annual

DV ug/m 200 8
20 10 24

Hr DV ug/m

Required Operating Required Operating Required



### 17300 232000/

268546 Clarksville, TN

- KY 0 0 0 0 2 1 0 0 0 0.070 1 2 3 

### 1 1 10.7 24 1 1 0 1 1

1 

### State of Kentucky operates an ozone site in Christian County, Kentucky. See Appendix 1 for MSA monitoring agreement prepared by Kentucky for ozone monitoring. 2 

### State of Tennessee operate s a continuous PM 2 .5 

### monitor in Clarksville, Montgomery County, Tennessee. See Appendix 1 for MSA monitoring agreement prepared by Tennessee for

continuous PM 2.5 

### monitoring. 3 

### Includes collocated monitor.



## Discussions of any proposals to re

- locate monitors in the next 18 months and suitability of PM2.5 sites for use in comparisons to the annual

PM2.5 standard :

The TEOM POC 3 PM2.5 particulate monitors and the speciation POC 5 STN monitors are generally not suited to be used for compa risons to the annual PM2.5 standard s.

There are no plans to relocate or shutdown any existing monitoring sites in the MSA area described.

An additional SO2 monitor may need to be operated in this area based on the PWEI index. The need for additional SO2 monitoring sites may be met by r e

- location of existing

network sites or by approval of existing industrial sites for use . Additional monitoring sites will require additional resources for both equipment and operational expenses.

## 67

AQSID County

Name Monitor Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd 

### RepOrg RepOrgName

471250006 Montgomery OTHER 81102 PM10 1 7 2010 6 MEEK'S

PROPERTY 17300 +36.520298

- 87.395500 063 0953 Savage Zinc Incinc Company

471250006 Montgomery OTHER 81102 PM10 2 7 2010 6 MEEK'S

PROPERTY 17300 +36.520298

- 87.395500 063 0953 Savage Zinc Incinc Company

471250006 Montgomery OTHER 42401 SO2 1 1 2010 Hourly MEEK'S

PROPERTY 17300 +36.520298

- 87.395500 039 1025 Tennessee Division

Of Air Pollution

Control

471250106 Montgomery OTHER 42401 SO2 1 1 2010 Hourly CUMBERLAND

HEIGHTS

ELEMENTARY

SCHOOL 17300 +36.505185

- 87.397708 039 1025 Tennessee Division

Of Air Pollution

Control

471251009 Montgomery SLAMS 88101 PM2.5 1 7 2010 1 1514 GOLF CLUB

LANE 17300 +36.514444

- 87.327778 118 1025 Tennessee Division

Of Air Pollution

Control

471251009 Montgomery SPECIAL

PURPOSE 88501 PM2.5

Cont 3 1 2010 Hourly 1514 GOLF CLUB

LANE 17300 +36.514444

- 87.327778 716 1025 Tennessee Division

Of Air Pollution

Control

471251009 Montgomery SUPLMNTL

SPECIATION 88502 PM Spec

Carbon 5 7 2010 6 1514 GOLF CLUB

LANE 17300 +36.514444

- 87.327778 810 1025 Tennessee Division

Of Air Pollution

Control

## 68

AQSID County

Name Monitor

Type Para Para

Name Monitoring

Instrument Analysis Ref Mtd

ID Monitor Objective

Type Dominant

Source Measurement

Scale Land Use

Type Location

Setting Date Site

Established

471250006 Montgomery OTHER 81102 PM 10 GMW Model

1200 GRAVIMETRIC RFPS

1287

- 063 UNKNOWN NULL NULL INDUST

RIAL RURAL 8/1/1978

471250006 Montgomery OTHER 81102 PM10 GMW Model

1200 GRAVIMETRIC RFPS

1287

- 063 UNKNOWN NULL NULL INDUST

RIAL RURAL 8/1/1978

471250006 Montgomery OTHER 42401 SO2 MONITOR

LABS 8850 ULTRA VIOLET

STIMULATED

FLUORESCNC EQSA

0779

- 039 UNKNOWN POINT NEIGHBORH

OOD INDUST

RIAL RURAL 8/1/1978

471250106 Montgomery OTHER 42401 SO2 MONITOR

LABS 8850 ULTRA VIOLET

STIMULATED

FLUORESCNC EQSA

0779

- 039 HIGHEST

CONCENTRATI

ON POINT MIDDLE

SCALE RESIDEN

TIAL RURAL 1/1/1982

471251009 Montgomery SLAMS 88101 PM2.

5 R & P CO

PLUS MODEL 2025PM SEQ GRAVIMETRIC RFPS

0498

- 118 POPULATION

EXPOSURE NULL NULL RESIDEN

TIAL SUBURBA

N 5/4/1997

471251009 Montgomery SPECIA

L

PURPO

SE 88501 PM2.

5

Cont TEOM Gravimetric 50 deg C POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 5/4/1997

471251009 Montgomery SUPLM

NTL

SPECIA

TION 88502 PM

Spec

Carbo

n MetOne Super

SASS

URG 3000 Gravimetric POPULATION

EXPOSURE NULL NULL RESIDEN

TIAL SUBURBA

N 5/4/1997

## 69 

# Morristown, TN Area

## 70 Tennessee’s Interpretation of Ambient Air Monitors Needed to meet the 40CFR, Part 58 Requirements

Census Area Identification and Population Data 14129

Lead 42101

CO 42401
SO2 42602
NO2 44201 Ozone 81102 PM
10 88101 PM 2.5 88502
PM 2.5 Speciation 88101 or

88501 PM
2.5 Cont

CBSA
2003
Code Census

2000
/Est.

2009 CBSA 2003 Title

(MS Areas)

Operating Required Operating Required Operating Required Operating Required Operating 

### 200 8
20 10
8 Hr

DV Required Operating Required Operating 

### 200 8
20 10

Annual DV ug/m 200 8

20 10 24

Hr DV ug/m

Required Operating Required Operating Required



### 34100 123081/

137612 Morristown, TN 0 0 0 0 0 0 0 0 1 0.074 1 0 0 0 0 0 0 0 0

1 

### Historical PM10 data does not reflect a need for PM10 monitoring in this area. 2 

### PM 2.5 monitoring in the adjacent MSA’s should be sufficient to assess PM 2.5 levels in this

MSA.



## Discussions of any proposals to re

- locate monitors in the next 18 months and suitability of PM2.5 sites for use in comparisons to the annual

PM2.5 standard :

The TEOM POC 3 PM2.5 particulate monitors and the speciation POC 5 STN monitors are generally not suited to be used for comparisons to the annual PM2.5 standards.

There are no plans to relocate or shutdown any existing monitoring sites in the MSA area described.

The need to establish additional NO2 near road monitors, PWEI required SO2 monitors and Lead monitoring s ites at sources emitting 0.5 TPY of lead is under consideration. The proposed requirement for CO monitors to be collocated with the near road NO2 monitors has not been finalized. The need f or additional monitoring sites may be met by

re

- location of exist ing network sites. Additional monitoring sites will require additional resources for both equipment and operational expenses

.

## 71

AQSID County

Name Monitor Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd 

### RepOrg RepOrgName

470890002 Jefferson OTHER 44201 O3 1 1 2010 Hourly 2393 FORESTER

RD 34100 +36.1 06

- 83.60 2 087 1025 Tennessee Division

Of Air Pollution

Control

## 72

AQSID County

Name Monitor

Type Para Para

Name Monitoring

Instrument Analysis Ref Mtd

ID Monitor Objective

Type Dominant

Source Measurement

Scale Land Use

Type Location

Setting Date Site

Established

470890002 Jefferson OTHER 44201 O3 MODEL 400

OZONE

ANALYZER ULTRA VIOLET

ABSORPTION EQOA

0992

- 087 UNKNOWN NULL NULL AGRICU

LTURAL RURAL 2 /1/ 2010

## 73 

# Jackson, TN Area

## 74 Tennessee’s Interpretation of Ambient Air Monitors Needed to meet the 40CFR, Part 58 Requirements

Census Area Identification and Population Data 14129

Lead 42101

CO 42401
SO2 42602
NO2 44201 Ozone 81102 PM
10 88101 PM 2.5 88502
PM 2.5 Speciation 88101 or 88501

PM 2.5 Cont

CBSA
2003
Code Census

2000
/Est.

2009 CBSA 2003 Title

(MS Areas)

Operating Required Operating Required Operating Required Operating Required Operating 

### 200 8
20 10
8 Hr

DV Required Operating Required Operating 

### 200 8
20 10

Annual DV ug/m 200 8

20 10

24 Hr

DV ug/m Required Operating Required Operating Required



### 27180 107377/

113629 Jackson, TN 0 0 0 0 0 0 0 0 0 0 1 0 2 1 

### 9.6 22 0 0 0 1 1

1 

### Includes collocated monitor.



## Discussions of any proposals to re

- locate monitors in the next 18 months and suitability of PM2.5 sites for use in comparisons to the annual

PM2.5 standa rd :

The TEOM POC 3 PM2.5 particulate monitors and the speciation POC 5 STN monitors are generally not suited to be used for compa risons to the annual PM2.5 standards.

Trees are encroaching on the PM

- 10 monitoring site. Historical data reveal very low l evels of PM

- 10 particulate at this site. Staff will evaluate the feasibility of continuing site by the end of 2011.

The need to establish additional NO2 near road monitors, PWEI required SO2 monitors and Lead monitoring sites at sources emit ting 0.5 TPY of lead is under consideration. The proposed requirement for CO monitors to be collocated with the near road NO2 monitors has not been finalized. The need f or additional monitoring sites may be met by

re

- location of existing network sites. Additional mo nitoring sites will require additional resources for both equipment and operational expenses.

## 75

AQSID County

Name Monitor Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd 

### RepOrg RepOrgName

471130003 Madison OTHER 81102 PM10 1 7 2010 6 JACKSON

REGIONAL

HEALTH OFFICE

PARKING L 27180 +35.637602

- 88.834496 063 1025 Tennessee Division

Of Air Pollution

Control

471130006 Madison SLAMS 88101 PM2.5 1 7 2010 3 1371

- A NORTH

PARKWAY JACKSON, TN

38301 27180 +35.651541

- 88.809652 118 1025 Tennessee Division

Of Air Pollution

Control

471130006 Madison SLAMS 88101 PM2.5 2 7 2010 3 1371

- A NORTH

PARKWAY JACKSON, TN

38301 27180 +35.651541

- 88.809652 118 1025 Tennessee Division

Of Air Pollution

Control

471130006 Madison SPECIAL

PURPOSE 88501 PM2.5

Cont 3 1 2010 Hourly 1371

- A NORTH

PARKWAY JACKSON, TN

38301 27180 +35.651541

- 88.809652 716 1025 Tennessee Division

Of Air Pollution

Control

## 76

AQSID County

Name Monitor

Type Para Para

Name Monitoring

Instrument Analysis Ref Mtd

ID Monitor Objective

Type Dominant

Source Measurement

Scale Land Use

Type Location

Setting Date Site

Established

471130003 Madison OTHER 81102 PM10 GMW Model

1200 GRAVIMETRIC RFPS

1287

- 063 UNKNOWN NULL NULL COMME

RCIAL SUBURBA

N 1/1/1980

471130006 Madison SLAMS 88101 PM2.

5 R & P CO

PLUS MODEL 2025PM SEQ GRAVIMETRIC RFPS

0498

- 118 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 11/17/2004

471130006 Madison SLAMS 88101 PM2.

5 R & P CO

PLUS MODEL 2025PM SEQ GRAVIMETRIC RFPS

0498

- 118 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 11/17/2004

471130006 Madison SPECIA

L

PURPO

SE 88501 PM2.

5

Cont TEOM Gravimetric 50 deg C POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 11/17/2004

## 77 

# Cleveland, TN Area

## 78 Tennessee’s Interpretation of Ambient Air Monitors Needed to meet the 40CFR, Part 58 Requirements

Census Area Identification and Population Data 14129

Lead 42101

CO 42401
SO2 42602
NO2 44201 Ozone 81102 PM
10 88101 PM 2.5 88502
PM 2.5 Speciation 88101 or 88501

PM 2.5 Cont

CBSA
2003
Code Census
2000
/Est.

2009 CBSA 2003 Title

(MS Areas)

Operating Required Operating Required Operating Required Operating Required Operating 

### 200 8
20 10
8 Hr

DV Required Operating Required Operating 

### 200 8
20 10

Annual DV ug/m 200 8

20 10

24 Hr

DV ug/m Required Operating Required Operating Required



### 17420 104015/

113629 Cleveland, TN 0 0 0 0 2 0 2 0 1 0.072 1 5 2 

### 0 1 11.7 23 0 0 0 1 1

1 

### Tennessee operates an ozone site on the Meigs/Bradley County line. 2 

### Includes collocated monitor.



## Discussions of any proposals to re

- locate monitors in the next 18 months and suitabi lity of PM2.5 sites for use in comparisons to the annual

PM2.5 standard :

The TEOM POC 3 PM2.5 particulate monitors and the speciation POC 5 STN monitors are generally not suited to be used for compa risons to the annual PM2.5 standards.

There are no pla ns to relocate or shutdown any existing monitoring sites in the MSA area described.

The need to establish additional NO2 near road monitors, PWEI required SO2 monitors and Lead monitoring sites at sources emit ting 0.5 TPY of lead is under consideration. The proposed requirement for CO monitors to be collocated with the near road NO2 monitors has not been finalized. The need f or additional monitoring sites may be met by

re

- location of existing network sites. Additional monitoring sites will require add itional resources for both equipment and operational expenses.

## 79

AQSID County

Name Monitor Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd 

### RepOrg RepOrgName

470110103 Bradley OTHER 81102 PM10 1 7 2010 6 BOWATERS VEC

SUB

- STATION

CALHOUN 17420 +35.278164

- 84.753816 064 0112 Bowater Southern Paper Company

471070101 McMinn OTHER 81102 PM10 1 7 2010 6 CALHOUN

BOWATERS NORTH(B

- 1)

LAMOUNTVILLE 11940 +35.297330

- 84.750760 064 0112 Bowater Southern Paper Company

471070101 McMinn OTHER 81102 PM10 2 7 2010 6 CALHOUN

BOWATERS NORTH(B

- 1)

LAMOUNTVILLE 11940 +35.297330

- 84.750760 064 0112 Bowater Southern Paper Company

470110102 Bradley OTHER 42401 SO2 1 1 2010 Hourly CHARLESTON

BOWATERS SOUTH(B

- 2)

WORTH ST. 17420 +35.283164

- 84.759371 009 112 Bowater Southern Paper Company

470110102 Bradley OTHER 42602 NO2 1 1 2010 Hourly CHARLESTON

BOWATERS SOUTH(B

- 2)

WORTH ST. 17420 +35.283164

- 84.759371 035 112 Bowater Southern Paper Company

470111002 Bradley OTHER 81102 PM10 1 7 2010 6 2850 Keith Street

NW 17420 +35.188721

- 84.867152 063 1025 Tennessee Division

Of Air Pollution

Control

470111002 Bradley OTHER 81102 PM10 2 7 2010 6 2850 Keith Street

NW 17420 +35.188721

- 84.867152 063 1025 Tennessee Division

Of Air Pollution

Control

471070101 McMinn OTHER 42401 SO2 1 1 2010 Hourly CALHOUN

BOWATERS NORTH(B

- 1)

LAMOUNTVILLE 11940 +35.297330

- 84.750760 009 1025 Tennessee Division

Of Air Pollution

Control

471070101 McMinn OTHER 42602 NO2 1 1 2010 Hourly CALHOUN

BOWATERS NORTH(B

- 1)

LAMOUNTVILLE 11940 +35.297330

- 84.750760 035 1025 Tennessee Division

Of Air Pollution

Control

471071002 McMinn SPECIAL

PURPOSE 88101 PM2.5 1 7 2010 3 SAINT MARK

AME ZION CHURCH, 707

NORTH JA 11940 +35.451111

- 84.599167 118 1025 Tennessee Division

Of Air Pollution

Control

471071002 McMinn SPECIAL

PURPOSE 88501 PM2.5

Cont 3 1 2010 Hourly SAINT MARK

AME ZION CHURCH, 707

NORTH JA 11940 +35.451111

- 84.599167 716 1025 Tennessee Division

Of Air Pollution

Control

471210104 Meigs OTHER 44201 O3 1 1 2010 Hourly 8401 HIGHWAY

60 +35.288997

- 84.946044 087 1025 Tennessee Division

Of Air Pollution

Control

## 80

AQSID County

Name Monitor

Type Para Para

Name Monitoring

Instrument Analysis Ref Mtd

ID Monitor Objective

Type Dominant

Source Measurement

Scale Land Use

Type Location

Setting Date Site

Established

470110103 Bradley OTHER 81102 PM10 SIERRA

ANDERSEN/G

MW 321

- B GRAVIMETRIC RFPS

1287

- 064 HIGHEST

CONCENTRATI

ON POINT NEIGHBORH

OOD COMME

RCIAL RURAL 7/1/1986

471070101 McMinn OTHER 81102 PM10 SIERRA

ANDERSEN/G

MW 321

- B GRAVIMETRIC RFPS

1287

- 064 HIGHEST

CONCENTRATI

ON POINT NEIGHBORH

OOD AGRICU

LTURAL SUBURBA

N 3/1/1982

471070101 McMinn OTHER 81102 PM10 SIERRA

ANDERSEN/G

MW 321

- B GRAVIMETRIC RFPS

1287

- 064 HIGHEST

CONCENTRATI

ON POINT NEIGHBORH

OOD AGRICU

LTURAL SUBURBA

N 3/1/1982

470110102 Bradley OTHER 42401 SO2 THERMO

ELECTRON 43 PULSED

FLUORESCENT EQSA

0276

- 009 UNKNOWN POINT MIDDLE

SCALE RESIDEN

TIAL URBAN

AND

CENTER

CITY 3/1/1982

470110102 Bradley OTHER 42602 NO2 THERMO

ELECTRON

14B/E CHEMILUMINESC

ENCE RFNA

0179

- 035 UNKNOWN POINT NULL RESIDEN

TIAL URBAN

AND

CENTER

CITY 3/1/1982

470111002 Bradley OTHER 81102 PM10 GMW Model

1200 GRAVIMETRIC RFPS

1287

- 063 UNKNOWN NULL NULL COMME

RCIAL SUBURBA

N 1/1/1972

470111002 Bradley OTHER 81102 PM10 GMW Model

1200 GRAVIMETRIC RFPS

1287

- 063 UNKNOWN NULL NULL COMME

RCIAL SUBURBA

N 1/1/1972

471070101 McMinn OTHER 42401 SO2 THERMO

ELECTRON 43 PULSED

FLUORESCENT EQSA

0276

- 009 HIGHEST

CONCENTRATI

ON POINT NEIGHBORH

OOD AGRICU

LTURAL SUBURBA

N 3/1/1982

471070101 McMinn OTHER 42602 NO2 THERMO

ELECTRON

14B/E CHEMILUMINESC

ENCE RFNA

0179

- 035 POPULATION

EXPOSURE POINT NULL AGRICU

LTURAL SUBURBA

N 3/1/1982

471071002 McMinn SPECIA

L

PURPO

SE 88101 PM2.5 R & P CO

PLUS MODEL 2025PM SEQ GRAVIMETRIC RFPS

0498

- 118 POPULATION

EXPOSURE AREA NEIGHBORH

OOD COMME

RCIAL URBAN

AND

CENTER

CITY 7/1/1986

471071002 McMinn SPECIA

L

PURPO

SE 88501 PM2.5

Cont TEOM Gravimetric 50 deg C POPULATION

EXPOSURE AREA NEIGHBORH

OOD COMME

RCIAL URBAN

AND

CENTER

CITY 7/1/1986

471210104 Meigs OTHER 44201 O3 MODEL 400

OZONE

ANALYZER ULTRA VIOLET

ABSORPTION EQOA

0992

- 087 UNKNOWN NULL NULL RESIDEN

TIAL RURAL 2/29/2000

## 81 

# Monitoring Sites Located In MSA/CBSA Areas In Tennessee

## 82 

# Monitoring Sites Located In Non

- MSA/CBSA Areas In Tennessee

## 83 Discussions of any proposals to re

- locate monitors in the next 18 months and suitability of PM2.5 sites for use in comparisons to the annual

PM2.5 standard :

A number of the monitoring sites identified in the Roane County area are being operated to monitor clean

- up acti vities that are on

- going in and around the Kingston TVA facility. The duration of monitoring and types of monitors may change over time and are not considered to be part of the reg ulatory monitoring network required to be operated for comparisons to the N AAQS.

Additional monitoring sites are operated in areas outside of the CBSA/MSA areas to help establish background air quality leve ls and to help define the air quality for those areas less densely populated outside of the metropolitan areas.

The TEOM PO C 3 PM2.5 particulate monitors and the speciation POC 5 STN monitors are generally not suited to be used for comparisons to t he annual PM2.5 standards.

There are no plans to relocate or shutdown any existing monitoring sites in the areas described.

The n eed to establish additional NO2 near road monitors, PWEI required SO2 monitors and Lead monitoring sites at sources emitting 0.5 TPY of lead is under consideration. The proposed requirement for CO monitors to be collocated with the near road NO2 monitors has not been finalized. The need for additional monitoring sites may be met by

re

- location of existing network sites. Additional monitoring sites will require additional resources for both equipment and ope rational expenses.

## 84

AQSID County

Name Monitor Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd 

### RepOrg RepOrgName

471450103 Roane OTHER 81102 PM10 1 7 2010 6 R.CARBON

CLYMERSVILLE

RD & BALDWIN 25340 +35.868153

- 84.698258 063 0921 Horsehead Corp

471450103 Roane OTHER 81102 PM10 2 7 2010 6 R.CARBON

CLYMERSVILLE

RD & BALDWIN 25340 +35.868153

- 84.698258 063 0921 Horsehead Corp

471450104 Roane OTHER 81102 PM10 1 7 2010 6 R.CARBON

HEWITT AVE.

HIGH SHCOOL 25340 +35.873152

- 84.689646 063 0921 Horsehead Corp

471550101 Sevier NON

- EPA

FEDERAL 42401 SO2 1 1 2010 Hourly GREAT SMOKY

MOUNTAIN NP

COVE

MOUNTAIN 42940 +35.696667

- 83.609722 009 0745 National Park Service

471550101 Sevier NON

- EPA

FEDERAL 44201 O3 1 1 2010 Hourly GREAT SMOKY

MOUNTAIN NP

COVE

MOUNTAIN 42940 +35.696667

- 83.609722 047 0745 National Park Service

471550102 Sevier NON

- EPA

FEDERAL 44201 O3 1 1 2010 Hourly CLINGSMANS DOME, GREAT

SMOKY MTNS.

NP 42940 +35.562778

- 83.498056 047 0745 National Park Service

470450004 Dyer SLAMS 88101 PM2.5 1 7 2010 3 175

- B

GREENWOOD

STREET 20540 +36.052871

- 89.382270 118 1025 Tennessee Division Of

Air Pollution Control

470450004 Dyer SPECIAL

PURPOSE 88501 PM2.5

Cont 3 1 2010 Hourly 175

- B

GREENWOOD

STREET 20540 +36.052871

- 89.382270 716 1025 Tennessee Division Of

Air Pollution Control

470990002 Lawrence SLAMS 88101 PM2.5 1 7 2010 3 BUSBY RD 29980 +35.116223

- 87.470010 118 1025 Tennessee Division Of

Air Pollution Control

470990002 Lawrence SPECIAL

PURPOSE 88501 PM2.5

Cont 3 1 2010 Hourly BUSBY RD 29980 +35.116223

- 87.470010 716 1025 Tennessee Division Of

Air Pollution Control

470990002 Lawrence SUPLMNTL

SPECIATION 88502 PM Spec 5 7 2010 6 BUSBY RD 29980 +35.116223

- 87.470010 810 1025 Tennessee Division Of

Air Pollution Control

471192007 Maury SPECIAL

PURPOSE 88101 PM2.5 1 7 2010 3 1600

NASHVILLE

HWY 17940 +35.651920

- 87.026300 118 1025 Tennessee Division Of

Air Pollution Control

471410005 Putnam SPECIAL

PURPOSE 88101 PM2.5 1 7 2010 3 630 EAST 20TH

STREET 18260 +36.185720

- 85.492200 118 1025 Tennessee Division Of

Air Pollution Control

471450004 Roane SPECIAL

PURPOSE 88101 PM2.5 1 7 2010 3 HARRIMAN

HIGH 1002 N.

ROAN ST

MOVED FRO 25340 +35.938695

- 84.543720 118 1025 Tennessee Division Of

Air Pollution Control

471450004 Roane SPECIAL

PURPOSE 88501 PM2.5

Cont 3 1 2010 Hourly HARRIMAN

HIGH 1002 N.

ROAN ST

MOVED FRO 25340 +35.938695

- 84.543720 716 1025 Tennessee Division Of

Air Pollution Control

471451001 Roane SPECIAL

PURPOSE 14128 Pb 1 7 2010 6 199 Lake Shore Rd, Kingston TN

37763 25340 +35.916795

- 84.503518 089 1025 Tennessee Division Of

Air Pollution Control

## 85

AQSID County

Name Monitor Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd 

### RepOrg RepOrgName

471451001 Roane SPECIAL

PURPOSE 81102 PM10

Cont 1 1 2010 Hourly 199 Lake Shore Rd, Kingston TN

37763 25340 +35.916795

- 84.503518 079 1025 Tennessee Division Of

Air Pollution Control

471451001 Roane NON

REGULATORY 88502 PM Spec 5 7 2010 6 199 Lake Shore Rd, Kingston TN

37763 25340 +35.916795

- 84.503518 810 1025 Tennessee Division Of

Air Pollution Control

471450004 Roane NON

REGULATORY 81102 PM10 2 7 2010 6 HARRIMAN

HIGH 1002 N.

ROAN ST

MOVED FRO 25340 +35.938695

- 84.543720 125 1029 Tennessee Valley Authority

471451001 Roane SPECIAL

PURPOSE 12128 Pb 2 7 2010 6 199 Lake Shore Rd, Kingston TN

37763 25340 +35.916795

- 84.503518 089 1029 Tennessee Valley Authority

471451001 Roane SPECIAL

PURPOSE 12128 Pb 3 7 2010 6 199 Lake Shore Rd, Kingston TN

37763 25340 +35.916795

- 84.503518 089 1029 Tennessee Valley Authority

471451001 Roane NON

REGULATORY 81102 PM10 2 7 2010 3 199 Lake Shore Rd, Kingston TN

37763 25340 +35.916795

- 84.503518 125 1029 Tennessee Valley Authority

471451001 Roane NON

REGULATORY 81102 PM10 4 7 2010 3 199 Lake Shore Rd, Kingston TN

37763 25340 +35.916795

- 84.503518 125 1029 Tennessee Valley Authority

471451001 Roane NON

REGULATORY 88101 PM2.5 2 7 2010 3 199 Lake Shore Rd, Kingston TN

37763 25340 +35.916795

- 84.503518 142 1029 Tennessee Valley Authority

471451001 Roane NON

REGULATORY 88101 PM2.5

Cont 3 1 2010 Hourly 199 Lake Shore Rd, Kingston TN

37763 25340 +35.916795

- 84.503518 170 1029 Tennessee Valley Authority

471451001 Roane NON

REGULATORY 88101 PM2.5 4 7 2010 3 199 Lake Shore Rd, Kingston TN

37763 25340 +35.916795

- 84.503518 142 1029 Tennessee Valley Authority

471451001 Roane NON

REGULATORY 88501 PM2.5

Cont 3 1 2010 Hourly 199 Lake Shore Rd, Kingston TN

37763 25340 +35.916795

- 84.503518 716 1029 Tennessee Valley Authority

471453005 Roane NON

REGULATORY 88101 PM2.5 1 7 2010 6 1025 Swan Pond Road, Harriman,

TN 37748 25340 +35.902566

- 84.524061 142 1029 Tennessee Valley Authority

471453005 Roane NON

REGULATORY 88101 PM2.5

Cont 3 1 2010 Hourly 1025 Swan Pond Road, Harriman,

TN 37748 25340 +35.902566

- 84.524061 170 1029 Tennessee Valley Authority

471453006 Roane NON

REGULATORY 88101 PM2.5 1 7 2010 3 130 Birkshire Road, Harriman,

TN 37748 25340 +35.918102

- 84.511151 142 1029 Tennessee Valley Authority

471453008 Roane NON

REGULAT ORY 88101 PM2.5 1 7 2010 6 540 Emory River Road, Harriman,

TN 37748 25340 +35.907121

- 84.497090 142 1029 Tennessee Valley Authority

471453008 Roane NON

REGULATORY 88101 PM2.5

Cont 3 1 2010 Hourly 540 Emory River Road, Harriman,

TN 37748 25340 +35.907121

- 84.497090 170 1029 Tennessee Valley Authority

471453009 Roane NON

REGULATORY 81102 PM10 1 7 2010 3 304 Windswept Lane, Kingston, 25340 +35.889824

- 84.517130 125 1029 Tennessee Valley Authority

## 86

AQSID County

Name Monitor Type Para Para

Name POC Int Year Collection Frequency Address CBSA Lat Lon Mtd 

### RepOrg RepOrgName

TN 37763

471453009 Roane NON

REGULATORY 81102 PM10

Cont 3 1 2010 Hourly 304 Windswept Lane, Kingston,

TN 37763 25340 +35.889824

- 84.517130 079 1029 Tennessee Valley Authority

471453009 Roane NON

REGULATORY 88101 PM2.5 1 7 2010 3 304 Windswept Lane, Kingston,

TN 37763 25340 +35.889824

- 84.517130 142 1029 Tenne ssee Valley Authority

471453009 Roane NON

REGULATORY 88101 PM2.5

Cont 3 1 2010 Hourly 304 Windswept Lane, Kingston,

TN 37763 25340 +35.889824

- 84.517130 170 1029 Tennessee Valley Authority

471453013 Roane NON

REGULATORY 88101 PM2.5

Cont 3 1 2010 Hourly SWAN POND CIRCLE ROAD; HARRIMAN, TN

3774 25340 +35.925500

- 84.516570 170 1029 Tennessee Valley Authority

471451001 Roane NON

REGULATORY 88501 PM2.5

Cont 3 1 2010 Hourly 199 Lake Shore Rd, Kingston TN

37763 25340 +35.916795

- 84.503518 716 1029 Tennessee Valley Authority

## 87

AQSID County

Name Monitor

Type Para Para

Name Monitoring

Instrument Analysis Ref Mtd

ID Monitor Objective

Type Dominant

Source Measurement

Scale Land Use

Type Location

Setting Date Site

Established

471450103 Roane OTHER 81102 PM10 GMW Model

1200 GRAVIMETRIC RFPS

1287

- 063 HIGHEST

CONCENTRATI

ON POINT NEIGHBORH

OOD INDUST

RIAL SUBURBA

N 1/1/1986

471450103 Roane OTHER 81102 PM10 GMW Model

1200 GRAVIMETRIC RFPS

1287

- 063 UNKNOWN POINT NULL INDUST

RIAL SUBURBA

N 1/1/1986

471450104 Roane OTHER 81102 PM10 GMW Model

1200 GRAVIMETRIC RFPS

1287

- 063 HIGHEST

CONCENTRATI

ON POINT NEIGHBORH

OOD INDUST

RIAL SUBURBA

N 1/1/1986

471550101 Sevier NON

EPA

FEDER

AL 42401 SO2 THERMO

ELECTRON 43 PULSED

FLUORESCENT EQSA

0276

- 009 GENERAL/BAC

KGROUND AREA NEIGHBORH

OOD FOREST RURAL 7/1/1988

471550101 Sevier NON

EPA

FEDER

AL 44201 O3 THERMO

ELECTRON 49 ULTRA VIOLET EQOA

0880

- 047 UNKNOWN AREA NEIGHBORH

OOD FOREST RURAL 7/1/1988

471550102 Sevier NON

EPA

FEDER

AL 44201 O3 THERMO

ELECTRON 49 ULTRA VIOLET EQOA

0880

- 047 HIGHEST

CONCENTRATI

ON NULL REGIONAL

SCALE FOREST RURAL 4/1/1993

470450004 Dyer SLAMS 88101 PM2.5 R & P CO

PLUS MODEL 2025PM SEQ GRAVIMETRIC RFPS

0498

- 118 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 8/22/1999

470450004 Dyer SPECIA

L

PURPO

SE 88501 PM2.5

Cont TEOM Gravimetric 50 deg C POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 8/22/1999

470990002 Lawrence SLAMS 88101 PM2.5 R & P CO

PLUS MODEL 2025PM SEQ GRAVIMETRIC RFPS

0498

- 118 UPWIND

BACKGROUND NULL NULL AGRICU

LTURAL RURAL 4/1/1997

470990002 Lawrence SPECIA

L

PURPO

SE 88501 PM2.5

Cont TEOM Gravimetric 50 deg C MAX OZONE

CONCENTRATI

ON NULL NULL AGRICU

LTURAL RURAL 4/1/1997

470990002 Lawrence SUPLM

NTL

SPECIA

TION 88502 PM

Spec Gravimetric UPWIND

BACKGROUND AREA URBAN

SCALE AGRICU

LTURAL RURAL 4/1/1997

471192007 Maury SPECIA

L

PURPO

SE 88101 PM2.5 R & P CO

PLUS MODEL 2025PM SEQ GRAVIMETRIC RFPS

0498

- 118 POPULATION

EXPOSURE AREA MIDDLE

SCALE COMME

RCIAL URBAN

AND

CENTER

CITY 12/25/1998

471410005 Putnam SPECIA

L

PURPO

SE 88101 PM2.5 R & P CO

PLUS MODEL 2025PM SEQ GRAVIMETRIC RFPS

0498

- 118 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL SUBURBA

N 8/15/2006

471450004 Roane SPECIA

L

PURPO

SE 88101 PM2.5 R & P CO

PLUS MODEL 2025PM SEQ GRAVIMETRIC RFPS

0498

- 118 POPULATION

EXPOSURE NULL URBAN

SCALE INDUST

RIAL SUBURBA

N 1/1/1980

471450004 Roane SPECIA 88501 PM2.5 TEOM Gravimetric POPULATION AREA URBAN INDUST SUBURBA 1/1/1980

## 88

AQSID County

Name Monitor

Type Para Para

Name Monitoring

Instrument Analysis Ref Mtd

ID Monitor Objective

Type Dominant

Source Measurement

Scale Land Use

Type Location

Setting Date Site

Established

L

PURPO

SE Cont 50 deg C EXPOSURE SCALE RIAL N

471451001 Roane SPECIA

L

PURPO

SE 14128 Pb ICP/MS W/QUARTZ

FILTER SOURCE

ORIENTED POINT MICROSCAL

E AGRICU

LTURAL RURAL 1/1/1958

471451001 Roane SPECIA

L

PURPO

SE 81102 PM10

Cont RUPRCHT&P

ATSHNCK

TEOM SER

1400 TEOM

GRAVIMETRIC EQPM

1090

- 079 SOURCE

ORIENTED POINT MICROSCAL

E AGRICU

LTURAL RURAL 1/1/1958

471451001 Roane NON

REGUL

ATORY 88502 PM

Spec Gravimetric POPULATION

EXPOSURE NULL NULL AGRICU

LTURAL RURAL 1/1/1958

471450004 Roane NON

REGUL

ATORY 81102 PM10 BGI Model PQ200 PM10 Gravimetric RFPS

1298

- 125 GENERAL/BAC

KGROUND AREA URBAN

SCALE INDUST

RIAL SUBURBA

N 1/1/1980

471451001 Roane SPECIA

L

PURPO

SE 12128 Pb ICP/MS W/QUARTZ

FILTER SOURCE

ORIENTED POINT MICROSCAL

E AGRICU

LTURAL RURAL 1/1/1958

471451001 Roane SPECIA

L

PURPO

SE 12128 Pb ICP/MS W/QUARTZ

FILTER SOURCE

ORIENTED POINT MICROSCAL

E AGRICU

LTURAL RURAL 1/1/1958

471451001 Roane NON

REGUL

ATORY 81102 PM10 BGI Model PQ200 PM10 Gravimetric RFPS

1298

- 125 SOURCE

ORIENTED POINT MICROSCAL

E AGRICU

LTURAL RURAL 1/1/1958

471451001 Roane NON

REGUL

ATORY 81102 PM10 BGI Model PQ200 PM10 Gravimetric RFPS

1298

- 125 SOURCE

ORIENTED POINT MICROSCAL

E AGRICU

LTURAL RURAL 1/1/1958

471451001 Roane NON

REGUL

ATORY 88101 PM2.5 BGI Models PQ200

- VSCC or PQ200A

VSCC Gravimetric EQPM

0202

- 142

or RFPS

0498

- 116 SOURCE

ORIENTED POINT MICROSCAL

E AGRICU

LTURAL RURAL 1/1/1958

471451001 Roane NON

REGUL

ATORY 88101 PM2.5

Cont Met One BAM

1020 PM2.5

VSCC FEM Beta Attenuation EQPM

0308

- 170 POPULATION

EXPOSURE AREA NEIGHBORH

OOD AGRICU

LTURAL RURAL 1/1/1958

471451001 Roane NON

REGUL

ATORY 88101 PM2.5 BGI Models PQ200

- VSCC

or PQ200A

VSCC Gravimetric EQPM

0202

- 142

or RFPS

0498

- 116 SOURCE

ORIENTED POINT MICROSCAL

E AGRICU

LTURAL RURAL 1/1/1958

471451001 Roane NON

REGUL

ATORY 88501 PM2.5

Cont TEOM Gravimetric 50 deg C SOURCE

ORIENTED POINT MICROSCAL

E AGRICU

LTURAL RURAL 1/1/1958

471453005 Roane NON

REGUL

ATORY 88101 PM2.5 BGI Models PQ200

- VSCC or PQ200A

VSCC Gravimetric EQPM

0202

- 142

or RFPS

0498

- 116 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL RURAL 1/1/2009

471453005 Roane NON

REGUL

ATORY 88101 PM2.5

Cont Met One BAM

1020 PM2.5

VSCC FEM Beta Attenuation EQPM

0308

- 170 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL RURAL 1/1/2009

## 89

AQSID County

Name Monitor

Type Para Para

Name Monitoring

Instrument Analysis Ref Mtd

ID Monitor Objective

Type Dominant

Source Measurement

Scale Land Use

Type Location

Setting Date Site

Established

471453006 Roane NON

REGUL

ATORY 88101 PM2.5 BGI Models PQ200

- VSCC or PQ200A

VSCC Gravimetric EQPM

0202

- 142

or RFPS

0498

- 116 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL RURAL 1/1/2009

471453008 Roane NON

REGUL

ATORY 88101 PM2.5 BGI Models PQ200

- VSCC or PQ200A

VSCC Gravimetric EQPM

0202

- 142

or RFPS

0498

- 116 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL RURAL 1/1/2009

471453008 Roane NON

REGUL

ATORY 88101 PM2.5

Cont Met One BAM

1020 PM2.5

VSCC FEM Beta Attenuation EQPM

0308

- 170 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL RURAL 1/1/2009

471453009 Roane NON

REGUL

ATORY 81102 PM10 BGI Model PQ200 PM10 Gravimetric RFPS

1298

- 125 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL RURAL 1/1/2009

471453009 Roane NON

REGUL

ATORY 81102 PM10

Cont RUPRCHT&P

ATSHNCK

TEOM SER

1400 TEOM

GRAVIMETRIC EQPM

1090

- 079 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL RURAL 1/1/2009

471453009 Roane NON

REGUL

ATORY 88101 PM2.5 BGI Models PQ200

- VSCC or PQ200A

VSCC Gravimetric EQPM

0202

- 142

or RFPS

0498

- 116 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL RURAL 1/1/2009

471453009 Roane NON

REGUL

ATORY 88101 PM2.5

Cont Met One BAM

1020 PM2.5

VSCC FEM Beta Attenuation EQPM

0308

- 170 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL RURAL 1/1/2009

471453013 Roane NON

REGUL

ATORY 88101 PM2.5

Cont Met One BAM

1020 PM2.5

VSCC FEM Beta Attenuation EQPM

0308

- 170 POPULATION

EXPOSURE AREA NEIGHBORH

OOD RESIDEN

TIAL RURAL 4/26/2010

## 90 

# Agreement Letters w ith Agencies Outside of Tennessee

Appendix 1: MSA Monitoring Agreements Prepared by Kentucky and Tennessee for Ozone and Continuous PM2.5 Monitoring

Appendix 2: MSA Monitoring Agreements for Memphis and Shelby County Health Department and the states of Arkansas and Mississippi

## 91 

# Appendix 1: MSA Monitoring Agreements Prepared by Kentucky and Tennessee for

Ozone and Continuous PM2.5 Monitoring

Tennessee Agreement Letter (page 1 o f 2 pages)

## 92 Tennessee Agreement Letter (page 2 of 2 pages)

## 93 Kentucky Agreement Letter (page 1 of 1 pages)

## 94 

# Appendix 2: MSA Monitoring Agreements for Memphis and Shelby County Health

Department and the states of Arkansas and Mississippi

Shelby County Agreement Letter (page 1 of 4 pages)

## 95 Shelby County Agreement Letter (page 2 of 4 pages)

## 96 Shelby County Agreement Letter (page 3 of 4 pages)

## 97 Shelby County Agreement Letter (page 4 of 4 pages)

# List of Attachments

Local Program Submittals of Ambient Monitoring Plans

1 Chattanooga AMP

2 Knoxville AMP

3 Memphis AMP

4 Nashville AMP

These documents are provided as submitted by the respective monitoring agency for use by the state in updating the overall ambient monitoring plan document.Chattanooga

- Hamilton County Air Pollution Control Bureau

Network Review 2011 

## 1 

# 1 Chattanooga AMP



# Chattanooga

- Hamilton County Air Pollution Control Bureau

Network Review

2011

East Ridge Site Collocated for 2009

The Chattanooga

- Hamilton County Air Pollution Control Bureau’s East Ridge PM 2.5 

## monitoring site (470650031) located at the U.S. Post Office, 1510 Maxwell Road, was moved to a temporary site on November 20, 2007, at 1517 Tombras Avenue behind East

Rid ge City Hall. The site was moved to a more desirable permanent site January 1, 2009, at the same address. Both the temporary and the permanent monitors were operated as daily collocated monitors about 110 feet apart from January 1, 2009, through January 17, 2010, for a comparison demonstration between the two data sets. After the complete 2009 collocated daily data set indicated excellent correlation, EPA recognized the temporary site data as being representative of the area in a letter dated February 2 5, 2010.



# East Ridge Monitoring Schedule Change

Daily monitoring changed to three

- day monitoring at the Tombras Avenue site (470650031) on January 17, 2010, with EPA concurrence. Daily monitoring is no longer required because Hamilton County is in attainment for the daily PM 2.5 

## standard, and the data is not

within 5% of the standard.



# Soddy Daisy PM 2.5 

# /Ozone Module Moved

The Bureau was informed by the Hamilton County School System in March, 2009, that the Soddy Daisy High School PM 2.5 

## /ozone module (470651011), located in a field behind the school, must be moved. At that time the Hamilton County Department of Education anticipated starting work immediately on a new softball field, and the location of the module interfered with the proposed lo cation of the field. The school system offered a new location approximately 100 feet from the original site. The move occurred on May 20, 2009, and it was coordinated so that there was minimal ozone data loss due to power interruptions. The

constructio n project began about May 6, 2010, and continued through the end of 2010 into

2011. PM 2.5 

## data for October 17, 2010, was extremely high (66.5 μg/m 3) 

## , due to extensive grading, heavy equipment use, and parking lot and road building next to the site. The d ata was dramatically higher than any location that monitors with a Federal Reference Monitor (FRM) in the United States for that day. An exceptional event concurrent flag was requested

from EPA in a letter to the Region 4 Administrator, Ms. Gwen Keyes Fle ming, dated April 15, 2011. Ozone was also affected by the project on September 1, 2010. Both dates are flagged in AQS for the respective pollutants.Chattanooga

- Hamilton County Air Pollution Control Bureau

Network Review 2011 

## 2 

# Carbon Monitor Added

As part of the third phase of EPA’s carbon monitoring program, a URG 3000 carb on monitor was added to the 911 Siskin Drive site (470654002) October 1, 2009, to monitor in conjunction with the Met One SuperSASS PM 2.5 

## speciation monitor.



# Attainment

Hamilton County PM 2.5 

## sites’ data are indicating attainment for the three

- year period s of

2006

- 2008, 2007

- 2009, and 2008

- 2010. PM 2.5 

## levels were extremely low for 2008, 2009, and 2010 across the region. Local pollution reduction measures have been aggressive since 2005. Also, sulfate scrubbers were activated in 2008 by Georgia Power’s n earby Bowen and

Hammond Plants.



# Active Sites

Chattanooga

- Hamilton County

Active Sites Pollutant Monitor AQS #

3300 South Broad Street/

WDEF PM 10 

## Collocated (6

- day) Sierra Anderson

321B 470650006

911 Siskin Drive formerly University of

Tennessee at Chattanooga (UTC) PM 2.5 

## Collocated ( 3

- day)

PM 2.5 

## Speciation (6

- day) Carbon (6

- day)

PM 2.5 

## Continuous TEOM R & P 2025 Seq. Met 1 SuperSASS

URG 3000

TEOM 1400A 470654002

CORE PM 2.5



## 1517 Tombras Avenue/ formerly 1510 Maxwell Rd PM 2.5 

## (Collocation from

1/1/2009

- 1/17/2010)

3

- day monitoring began 1/20/2010) R & P 2025 Seq. 470650031

618 Sequoyah Access Road at Soddy

- Daisy High School PM 2.5 

## (6

- day)

Ozone Continuous

Ozone Calibrator R & P 2025 Seq.

TECO 49C

TECO 49CPS 470651011

6200 Bonny Oaks Drive Eastside Utility District Ozone Continuous

Ozone Calibrator TECO 49C

TECO 49CPS 470654003



# Site Changes for 2011

No lead or SO 2 

## monitoring will be required in Hamilton County for the recently promulgated

lead and SO 2 

## regulations. Hamilton County anticipates, at some point in the future, participating in the Core

- Based Statistical Area near

- road monitoring for NO 2 

## in conjunction with the recently promulgated NO 2 

## regulations.

The Eastside Utility ozone monitor 47065 4003 on the Volunteer Army Ammunition Property has become more and more difficult to access as security has tightened at that site. The water utility has an electronic gate access for which our agency originally was given an accessChattanooga

- Hamilton County Air Pollution Control Bureau

Network Review 2011 

## 3 code. Our agency no lo nger has an access code, and we must rely on personnel of the water utility to let us in electronically. The utility is expanding significantly at that location, and it seems a prudent time to plan to move the site. Scouting is being done to try to find a desirable location within a mile radius, and we anticipate moving the site before the 2012

ozone season. If a suitable location within a mile radius is not found, we may seek an alternate location or request to discontinue the monitoring site.

# 2 Knoxville AMP

## 2 Knoxville, TN Area

## 3 Tennessee’s Interpretation of Ambient Air Monitors Needed to meet the 40CFR, Part 58 Requirements

## 4 Local programs air monitoring report criteria summary

## 5 Local Program Monitors Criteria Data Tables

## 6

Tennessee’s Ambient Air Monitoring Network Additional Criteria Data Tables (All state and local monitors including collocated monitors)

## 7

## 8

## 1 

# 3 Memphis AMP

## 2

## 3

## 4 Memphis, TN

- MS

- AR Area

Memphis, TN

- MS

- AR Area

Airs Name REPORGC

ODE Latitude Longitude StreetAddress CBSA2003Title

471570016 PM10, PM10 Colloc. 0673 +35.164444

- 89.970833 GAS SERVICE CENTER MEAGHER STREET Memphis, TN

- MS

- AR

471570021 Ozone 0673 +35.217500

- 90.019444 1330 FRAYSER BLVD Memphis, TN

- MS

- AR

471570024 CO, PM2.5 Cont, PM2.5

Spec 0673 +35.150833

- 90.041389 416 ALABAMA AVENUE Memphis, TN

- MS

- AR

471570046 SO2, PM10 0673 +35.272778

- 89.961389 3065 FITE RD Memphis, TN

- MS

- AR

471570047 PM2.5, PM2.5 Colloc. 0673 +35.168950

- 90.021567 1064 BREEDLOVE STREET Memphis, TN

- MS

- AR

471571004 Ozone 0673 +35.377222

- 89.832222 6855 MUDVILLE RD. EDMUND ORGILL PARK Memphis, TN

- MS

- AR

471570075 NCore: CO (trace), SO2

(trace), NOY, O3, PM2.5, PM2.5 Cont, PM2.5 Spec 0673 +35.15159

- 89.85022 6388 Haley Road (Shelby Farms) Memphis, TN

- MS

- AR

## 5 Tennessee’s Interpretation of Ambient Air Monitors Needed to meet the 40CFR, Part 58 Requirements

Census Area Identification and Population Data 14129

Lead 42101
CO 42401
SO2 42602
NO2 44201 Ozone 81102

PM 10 88101 PM 2.5 88502
PM 2.5 Speciation 88101 or

88501 PM
2.5 Cont

CBSA

2003
Code Census

2000
/Est.

2009 CBSA 2003 Title

(MS Areas)

Operating Required Operating Required Operating Required Operating Required Operating 

### 2007
2009
8 Hr

DV Required Operating Required Operating 

### 2007
2009

Annual

DV 2007
2009

24 Hr

DV Required Operating Required Operating Required



### 32820 1205204/

1304926 Memphis, TN

- MS

AR 0 0 2 3 

### 0 2 3 

### 0 0 0 3 0.078 2 3 2 

### 2

- 4 2 1,2 

### 11.7 28 3 2 2 2 2

1 

### The Memphis and Shelby County Health Department and the states of Arkansas and Mississippi have implemented a joint MOA that provides for meeting the MSA monitoring requirements fo r the combined MSA area. See Appendix 2 for the monitoring agreement.

2 

### Includes collocated monitor.

3 

### Includes trace level analyzer.

## 6 Local programs air monitoring report criteria summary

(1) The AQS site
identificati

on number. Parameter POC
Identifier Reporting

Org. (2) The

location, including

street
address and geographical
coordinates. (3) The

sampling
and analysis method(s)
for each

measured parameter. (4) The

operating
schedules for

each monitor. (5) Any

proposals to

remove or

move a monitoring
station within a period of 18
months following plan

submittal. (6) The

monitoring objective and spatial scale of representative
ness for each

monitor as
defined in appendix D to this part. (7) The

identification of any sites that are

su itable and sites
that are not
suitable for comparison against the
annual PM2.5 NAAQS as described in §
58.30. (8) The MSA,

CBSA, CSA

or other area represented by the
monitor.

471570016 81102 1 0673 See table. See table. 1 in 6 No See table. DNA See table.

471570016 81102 2 0673 See table. See table. 1 in 6 No See table. DNA See table.

471570021 44201 1 0673 See table. See table. Continuous No See table. DNA See table.

471570024 88501 3 0673 See table. See table. Continuous No See table. Not suitable See table.

471570024 88502 5 0673 See table. See table. 1 in 6 No See table. suitable See table.

471570024 42101 1 0673 See table. See table. Continuous No See table. DNA See table.

471570046 81102 1 0673 See table. See table. 1 in 6 No See table. DNA See table.

471570046 42401 1 0673 See table. See table. Continuous No See table. DNA See table.

471570047 88101 1 0673 See table. See table. 1 in 1 No See table. Suitable See table.

471570047 88101 2 0673 See table. See table. 1 in 6 No See table. Suitable See table.

471570075 42101 1 0673 See table. See table. Continuous No See table. DNA See table.

471570075 42401 1 0673 See table. See table. Continuous No See table. DNA See table.

471570075 42600 1 0673 See table. See table. Continuous No See table. DNA See table.

471570075 44201 1 0673 See table. See table. Continuous No See table. DNA See table.

471570075 88101 1 0673 See table. See table. Continuous No See table. Suitable See table.

471570075 88101 3 0673 See table. See table. Continuous No See table. DNA See table.

471570075 88502 5 0673 See table. See table. 1 in 3 No See table. DNA See table.

471570075 86101 1 0673 See table. See table. 1 in 3 No See table. Suitable See table.

471571004 44201 1 0673 See table. See table. Continuous No See table. DNA See table.

## 7 Local Program Monitors Criteria Data Tables

Airs

Parameter POC REP
ORG
CODE Date

Sampling Began CBSA

2003 Title

Population of CBSA 2009 Est Population of CBSA 2000 Census

Land Use Location Setting

Dominant Source Measurement

Scale Monitor

Objective MONITOR

TYPE Sampling

Instrument
Name and Designation

471570016 81102 1 0673 19860101 Memphis,

TN

- MS

- AR 1,304,926 1,205,204 INDUSTRIAL URBAN AND
CENTER
CITY AREA NEIGHBORHOOD HIGHEST
CONCENTRATI
ON SLAMS Sierra

- A
ndersen/GMW
321

- B RFPS

1287

- 064 064

471570016 81102 2 0673 19860101 Memphis,

TN

- MS

- AR 1,304,926 1,205,204 INDUSTRIAL URBAN AND
CENTER
CITY AREA NEIGHBORHOOD HIGHEST
CONCENTRATI
ON SPECIAL

PURPOSE Sierra

- A

ndersen/GMW
321

- B RFPS

1287

- 064 064

471570021 44201 1 0673 19720901 Memphis,

TN

- MS

- AR 1,304,926 1,205,204 RESIDENTIAL SUBURBAN AREA NEIGHBORHOOD POPULATION
EXPOSURE SLAMS Advanced
Pollution Instr.
400/400A/400E
EQOA

- 0992

- 087
087

471570024 42101 1 0673 20060401 Memphis,
TN

- MS

- AR 1,304,926 1,205,204 RESIDENTIAL SUBURBAN MOBILE MICROSCALE HIGHEST
CONCENTRATI
ON SLAMS Teledyne
Advanced
Pollution Instr.
300 or 300E
RFCA

- 1093

- 093
093

471570024 88501 3 0673 20060101 Memphis,

TN

- MS

- AR 1,304,926 1,205,204 RESIDENTIAL SUBURBAN AREA NEIGHBORHOOD POPULATION
EXPOSURE SLAMS R & P TEOM
Gravimetric 50 deg C PM2.5 SSI
w/No Correction
Factor 711

471570024 88502 5 0673 20060514 Memphis,

TN

- MS

- AR 1,304,926 1,205,204 RESIDENTIAL SUBURBAN AREA NEIGHBORHOOD POPULATION
EXPOSURE TRENDS

SPECIATIO

N Met One SASS

810

## 8

Airs

Parameter POC REP
ORG
CODE Date

Sampling Began CBSA

2003 Title

Population of CBSA 2009 Est Population of CBSA 2000 Census

Land Use Location Setting

Dominant Source Measurement

Scale Monitor

Objective MONITOR

TYPE Sampling

Instrument
Name and Designation

471570046 42401 1 0673 19940501 Memphis,

TN

- MS

- AR 1,304,926 1,205,204 INDUSTRIAL SUBURBAN MOBILE URBAN SCALE MAX
PRECURSOR
EMISSIONS
IMPACT SLAMS Advanced
Pollution Instr.
100A/100AS
EQSA

- 0495

- 100
100

471570046 81102 1 0673 19940501 Memphis,
TN

- MS

- AR 1,304,926 1,205,204 INDUSTRIAL SUBURBAN AREA NEIGHBORHOOD MAX
PRECURSOR
EMISSIONS
IMPACT SLAMS Sierra

- A
ndersen/GMW

321

- B RFPS

1287

- 064 064

471570047 88101 1 0673 19981201 Memphis,

TN

- MS

- AR 1,304,926 1,205,204 RESIDENTIAL SUBURBAN AREA NEIGHBORHOOD POPULATION
EXPOSURE SLAMS R & P Partisol

FRM 2000 PM

- 2.5 RFPS

- 0498

- 117 117

471570047 88101 2 0673 19981201 Memphis,

TN

- MS

- AR 1,304,926 1,205,204 RESIDENTIAL SUBURBAN AREA NEIGHBORHOOD POPULATION
EXPOSURE SPECIAL

PURPOSE R & P Partisol

FRM 2000 PM

- 2.5 RFPS

- 0498

- 117 117

471571004 44201 1 0673 19800201 Memphis,

TN

- MS

- AR 1,304,926 1,205,204 AGRICULTURAL RURAL MOBILE URBAN SCALE HIGHEST
CONCENTRATI
ON SLAMS Advanced
Pollution Instr.
400/400A/400E
EQOA

- 0992

- 087
087

471570075 42101 1 0673 20110401 Memphis,
TN

- MS

- AR 1,260,905 1,205,204 INDUSTRIAL URBAN AREA Neighborhood and
Urban Scale MAX

PRECURSOR
EMISSIONS
IMPACT NCore Teledyne
Advanced
Pollution Instr.
300EU
RFCA

- 1093

- 093

471570075 42401 1 0673 20110401 Memphis,

TN

- MS

- AR 1,260,905 1,205,204 INDUSTRIAL URBAN AREA Neighborhood MAX
PRECURSOR
EMISSIONS
IMPACT NCore Teledyne
Advanced
Pollution Instr.
100EU
EQSA

- 0495

- 100

471570075 42600 1 0673 20110401 Memphis,
TN

- MS

- AR 1,260,905 1,205,204 INDUSTRIAL URBAN AREA Neighborhood MAX
PRECURSOR
EMISSIONS
IMPACT NCore Teledyne
Advanced
Pollution Instr.
200EU

RFNA

- 1194

- 099

## 9

Airs

Parameter POC REP
ORG
CODE Date

Sampling Began CBSA

2003 Title

Population of CBSA 2009 Est Population of CBSA 2000 Census

Land Use Location Setting

Dominant Source Measurement

Scale Monitor

Objective MONITOR

TYPE Sampling

Instrument
Name and Designation

471570075 44201 1 0673 20110301 Memphis,

TN

- MS

- AR 1,260,905 1,205,204 INDUSTRIAL URBAN AREA Neighborhood and
Urban Scale HIGHEST

CONCENTRATI
ON NCore Teledyne
Advanced
Pollution Instr.
400E/400/400A
EQOA

- 0992

- 087

471570075 88101 1 0673 20110223 Memphis,
TN

- MS

- AR 1,260,905 1,205,204 INDUSTRIAL URBAN AREA URBAN SCALE HIGHEST
CONCENTRATI
ON NCore R & P Pa rtisol

FRM 2025 PM

- 2.5
RFPS

- 0498

- 118

471570075 88101 3 0673 20110311 Memphis,

TN

- MS

- AR 1,260,905 1,205,204 INDUSTRIAL URBAN AREA URBAN SCALE HIGHEST
CONCENTRATI
ON NCore R & P TEOM
Gravimetric 50 deg C PM2.5 SSI
w/No Correction
Factor 711

471570075 88502 5 0673 20110208 Memphis,
TN

- MS

- AR 1,260,905 1,205,204 INDUSTRIAL URBAN AREA URBAN SCALE HIGHEST
CONCENTRATI
ON TRENDS

SPECIATIO

N Met One SASS

810

471570075 86101 1 0673 PENDING Memphis,

TN

- MS

- AR 1,260,905 1,205,204 INDUSTRIAL URBAN AREA URBAN SCALE HIGHEST
CONCENTRATI
ON NCore Thermo Scientific

Dichotmous
Partisol

- Plus
Model 2025D
EQPS

- 0509

- 179

## 10

Tennessee’s Ambient Air Monitoring Network Additional Criteria Data Tables (All state and local monitors including collocated monitors)

Airs Co

FIPS Parameter POC Operating
Schedule REP ORG

CODE SLI Latitude Longitude Street Address CBSA_2003_Code CBSA_2003_Title

471570016 157 81102 1 1 in 6 0673 L +35.164444

- 89.970833 GAS SERVICE CENTER
MEAGHER STREET 32820 Memphis, TN

MS

- AR

471570016 157 81102 2 1 in 6 0673 L +35.164444

- 89.970833 GAS SERVICE CENTER
MEAGHER STREET 32820 Memphis, TN

MS

- AR

471570021 157 44201 1 Continuous 0673 L +35.217500

- 90.019444 1330 FRAYSER BLVD 32820 Memphis, TN

MS

- AR

471570024 157 42101 1 Continuous 0673 L +35.150833

- 90.041389 416 ALABAMA AVENUE 32820 Memphis, TN

MS

- AR

471570024 157 88101 3 Continuous 0673 L +35.150833

- 90.041389 416 ALABAMA AVENUE 32820 Memphis, TN

MS

- AR

471570024 157 88502 5 1 in 6 0673 L +35.150833

- 90.041389 416 ALABAMA AVENUE 32820 Memphis, TN

MS

- AR

471570046 157 42401 1 Continuous 0673 L +35.272778

- 89.961389 3065 FITE RD 32820 Memphis, TN

MS

- AR

471570046 157 81102 1 1 in 6 0673 L +35.272778

- 89.961389 3065 FITE RD 32820 Memphis, TN

MS

- AR

471570047 157 88101 1 1 in 1 0673 L +35.168950

- 90.021567 1064 BREEDLOVE
STREET 32820 Memphis, TN

MS

- AR

471570047 157 88101 2 1 in 6 0673 L +35.168950

- 90.021567 1064 BREEDLOVE
STREET 32820 Memphis, TN

MS

- AR

471571004 157 44201 1 Continuous 0673 L +35.377222

- 89.832222 6855 MUDVILLE RD.
EDMUND ORGILL PARK 32820 Memphis, TN

MS

- AR

471570075 157 42101 1 Continuous 0673 L +35.15159

- 89.85022 6388 Haley Road 32820 Memphis, TN

MS

- AR

471570075 157 42401 1 Continuous 0673 L +35.15159

- 89.85022 6388 Haley Road 32820 Memphis, TN

MS

- AR

471570075 157 42600 1 Continuous 0673 L +35.15159

- 89.85022 6388 Haley Road 32820 Memphis, TN

MS

- AR

471570075 157 44201 1 Continuous 0673 L +35.15159

- 89.85022 6388 Haley Road 32820 Memphis, TN

MS

- AR

471570075 157 88101 1 1 in 3 0673 L +35.15159

- 89.85022 6388 Haley Road 32820 Memphis, TN

MS

- AR

471570075 157 88101 3 Continuous 0673 L +35.15159

- 89.85022 6388 Haley Road 32820 Memphis, TN

MS

- AR

471570075 157 88502 5 1 in 3 0673 L +35.15159

- 89.85022 6388 Haley Road 32820 Memphis, TN

MS

- AR

471570075 157 86101 1 1 in 3 0673 L +35.15159

- 89.85022 6388 Haley Road 32820 Memphis, TN

MS

- AR

# 4 Nashville AMP



# Ambient Air Monitoring Plan

2011

Metro Public Health Department

Pollution Control Division

Nashville, Tennessee

Draft Plan 

# March 22, 2011

## 1 1. The Purpose of the Nashville/Davidson County Ambient Air Monitoring Network

There are several criteria that are used for determining the need for ambient air quality monitoring. Some of the criteria ar e as follows:

The Code of Federal Regulations (CFR) sets forth as regulations the requirements for air quality monitoring to be i mplemented by the states and EPA. These requirements are primarily organized around population and emission density in a given area with the number of required monitors and the distribution of the monitors within the networks specified by these regulatio ns

. The EPA must approve design and/or modifications to these networks. The federal regulations also specify the frequency, method, location requirements, equipment, quality assurance procedures and reporting of data collected from the ambient air monitoring networks.

Air quality monitoring is required to be conducted to alert citizens of possible elevated levels of air pollutants in cities or communities of desig nated population levels and to provide Air Quality Index (AQI) reports of the current air qual ity to the general public. Air quality monitoring is conducted to address the need for background air quality data and to provide needed air quality data that is used in evaluating healthy environmental conditions in Nashville and Davidson County.

Speci al air quality monitoring studies are conducted based on identified needs for m onitoring data in a given area. Citizen complaints and enforcement investigations related to air quality are other reasons for air quality monitoring usually in or around a spec ific area related to the complaint or investigation. Requests from citizens for special air monitoring studies are also a reason for air monitoring activities.

The Metropolitan Public Health Department, Pollution Control Division (MPHDPCD) Nashville, Tenn essee evaluates its monitoring network annually to account for any necessary changes which may involve the addition, discontinuation, revision, or modificat ion of a monitoring site within the network. We have examined each air monitoring site and have eval uated each accordingly to the requirements and provisions of the new regulations in CFR 40, Parts 50, 53, and 58. We have concluded that the number and loc ation of the air monitors in our network contribute by the best means, to provide sufficient air qual ity data and reliable information to the public.



## 2. Monitoring Network Requirements

2 .1 Ozone Monitoring Network Requirements:

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 2009



## Table 1 SLAMS MINIMUM O3 MONITORING REQUIREMENTS

MSA Population 1,2 

### Most recent 3

- year design value concentrations ≥85% of any O3
NAAQS 3 

### Most recent 3

- year design value concentrations <85% of any O3
NAAQS 3,4



### >10 million 4 2

4

- 10 million 3 1

350,000

- < 4 million 2 1

50,000

- <350,000 5 

### 1 0

(1) Minimum monitoring requirements apply to the Metropolitan statistical area (MSA). (2) Population based on latest available census figures. (3) The ozone (O3) National Ambient Air Quality Standards (NAAQS) levels and forms are defined in 40 CFR part 50. (4) These minimum monitoring requirements apply in the absence of a design value. (5) Metropolitan statistical areas (MSA) must contain an urbanized area of 50,000 or more population



### Note: The NAAQS for ozone was revi sed by EPA March 12, 2008 to 0.075 PPM. There were no regulatory changes made to the network monitoring requirements at that time. On January 6, 2010 EPA proposed strengthening the 8

- hour “primary” ozone standard, to a level within the range of 0.060

- 0.070 parts per million (ppm). EPA also proposed to establish a distinct cumulative, seasonal “secondary” standard within the range of 7

- 15 ppm

- hours. EPA proposed in July 2009 to modify the ozone air quality monitoring network design requirements for urban are as with populations between 50,000 and 350,000 people , to operate at least one ozone monitor and that states will be required to operate at least three ozone monitors in non

urban areas. However, these regulations have not yet been finalized by the EPA. When the rules become final, Nashville will
review its ozone monitoring network in accordance with the regulations.

## 2 2 .2 PM 2.5 Monitoring Network Requirements:

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 2009



## Table 2 PM2.5 MINIMUM MONITORING REQUIREMENTS

MSA Population 1, 2 

### Most recent 3

-

year design
value

concentrations ≥85% of any

PM2.5
NAAQS 3 

### Most recent 3

-

year design
value

concentrations <85% of any

PM2.5
NAAQS 3,4 

### Continuous

PM2.5 Monitoring PM2.5

Background

and Transport
Sites PM2.5

Chemical Speciation
Sites

>1,000,000 3 2 2

- 1 One site each per state for background and transport Existing STN

Required Site(s) 500,000

- 1,000,000 2 1 1

50,000

– <500,000 5 

### 1 0 0

- 1

(1) Minimum monitoring requirements apply to the Metropolitan statistical area (MSA). (2) Population based on latest available census figures. (3) The PM2.5 National Ambient Air Quality Standards (NAAQS) levels and forms are defined in 40 CFR part 50. (4) These minimum monitoring requirements apply in the absence of a design value. (5) Metropolitan statistical areas (MSA) must contain an urbanized area of 50,000 or more population.



### Requirement for Continuous PM2.5 Monitoring ; The State, or where appropriate, local agencies must operate continuous PM2.5 analyzers equal to at least one

- half (round up) the minimum required sites listed in Table D

- 5 of this appendix. At least one required continuous analyzer in each MSA must be collocated with one of the required FRM/FEM/ARM monitors, unless at least one of the required FRM/FEM/ARM monitors is itself a continuous FEM or ARM monitor in which case no collocation requirement applies. State and local air monitoring agencies must use methodologies and quality assurance/quality control (QA/QC) procedures approved by the EPA Regional Administrator for these required continuous analyzers.

Requirement for PM2.5 Background and Transport Sites ; Each State shall install and operate at least one PM2.5 site to monitor for regional background and at least one PM2.5 site to monitor regional transport.

PM2.5 Chemical Speciation Site Requirements ; Each State shall continue to conduct chemical speciation monitoring and analyses at sites designated to be part of the PM2.5 Speciation Trends Network (STN). The selection and modification of these STN sites m ust be approved by the Administrator.



## 2 .3 PM 10 Monitoring Network Requirements:

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 2009



## Table 3 PM10 MINIMUM MONITORING REQUIREMENTS (NUMBER OF STATIONS PER MSA) 1



### Population Category 1 

### High Concentration 2 

### Medium Concentration 3 

### Low Concentration 4,5



### >1,000,000 6

- 10 4

- 8 2

- 4

500,000

- 1,000,000 4

- 8 2

- 4 1

- 2

250,000

- 500,000 3

- 4 1

- 2 0

- 1

100,000

- 250,000 1

- 2 0

- 1 0

(1) Selection of urban areas and actual numbers of stations per area within the ranges shown in this tabl e will be jointly determined by EPA and the State Agency. (2) High concentration areas are those for which ambient PM10 data show ambient concentrations exceeding the PM10 NAAQS by 20 percent or more. (3) Medium concentration areas are those for which ambient PM10 data show ambient concentrations exceeding 80 percent of the PM10 NAAQS. (4) Low concentration areas are those for which ambient PM10 data show ambient concentration s less than 80 percent of the PM10 NAAQS. (5) These minimum monitoring requirements apply in the absence of a design value.

## 3 2 .4 SO2 Monitoring Network Requirements:

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 2009

Sulfur Dioxide (SO2) Design Criteria:

(a) There are no minimum requirements for the number of SO2 monitoring sites. Continued operation of existing SLAMS SO2 sites using FRM or FEM is required until discontinuation is approved by the EPA Regional Administrator. Where SLAMS SO2 monitoring is ongoing, at least one of the SLAMS SO2 sites must be a maximum concentration site for that specific area.

EPA announced on 11/16/2009 proposals to revise the annual and 24 hour primary NAAQS and replace both with a new 1

- hour SO2 standard. The existing secondary standard is under review. Additional SO2 monitoring sites are expected to be added to existing monitoring network s to increase the number of monitors in the Core Based Statistical Areas. Increased monitoring would also be required in states based on their contribution to national SO2 emissions and additional monitoring may be required in areas where gaps exist in net work coverage. The new monitors would be required to be operational by 2013 if the EPA proposal i s 

### adopted in its current form

.

SO2 monitoring that is required under the population

- weighted emission index (PWEI) calculations requires MPHDPCD to operate o ne (1) SO2 monitor. MPHDPCD currently operates one SO2 monitor which has been approved by EPA to meet the SO2 monitoring requirement.



## 2 .5 NO2 Monitoring Network Requirements:

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 2009

Nitroge n Dioxide (NO2) Design Criteria:

a) There are no minimum requirements for the number of NO2 monitoring sites. Continued operation of existing SLAMS NO2 sites using FRM or FEM is required until discontinuation is approved by the EPA Regional Administrato r. Where SLAMS NO2 monitoring is ongoing, at least one NO2 site in the area must be located to measure the maximum concentration of NO2.

EPA announced on January 22, 2010 the final revisions to the NO2 NAAQS. EPA added a new Primary1

- hour NO2 standard at 100 ppb (parts per billion). EPA chose to retain the current Primary and Secondary standards and to revise the AQI for NO2 to incorporate the new 1

- hour standard. EPA also revised the monitoring requirements and will now require monitoring near
roads in a reas with populations greater than 500,000. Additional monitors will be required in urban areas near major roads with populations greater than or equal to 1,000,000 to assess community wide concentrations and an additional monitor for areas with population s greater than or equal to 2,500,000 also near roads or having road segments with annual average vehicle daily traffic counts greater than or equal to 250,000 vehicles. Additional monitors will also be required to be place d in areas with vulnerable populat ions susceptible to NO2 health related effects. These additional monitors would be required to be operational before January 1, 2013 if the EPA proposal is adopted in its current form.



## 2 .6 Lead (Pb ++ 

## ) Monitoring Network Requirements:

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 2009

Lead (Pb) Design Criteria:

(a) State and, where appropriate, local agencies are required to conduct ambient air Pb mo nitoring taking into account Pb sources which are expected to or have been shown to contribute to a maximum Pb concentration in ambient air in excess of the NAAQS, the potential for population exposure, and logistics. At a minimum, there must be one source

- oriented SLAMS site located to

measure the maximum Pb concentration in ambient a ir resulting from each Pb source which emits 1.0 or more tons per year based on either the most recent National Emission Inventory ( http://www.epa.gov/ttn/chief/ eiinformation.html ) or other scientifically justifiable methods and data (such as improved emi ssions factors or site

- specific data) taking into account logistics and the potential for population exposure.

(i) One monitor may be used to meet the requirement in paragraph 4.5(a) for all sources involved when the location of the

maximum P b concentration due to one Pb source is expected to also be impacted by Pb emissions from a nearby source (or multiple sources). This monitor must be sited, taking into account logistics and the potential for population exposure, where the
Pb concentration from all sources combined is expected to be at its maximum. (ii) The Regional Administrator may waive the requirement in paragraph 4.5(a) for monitoring near Pb sources if the State or, where appropriate, local agency can demonstrate the Pb sour ce will not contribute to a maximum Pb concentration in ambient air in excess of 50% of the NAAQS (based on historical monitoring data, modeling, or other means). The waiver must be renewed once every 5 years as part of the network asse ssment required unde r 58.10(d)

## 4 (b) State and, where appropriate, local agencies are required to conduct Pb monitoring in each CBSA with a population equal t o or greater than 500,000 people as determined by the latest available census figures. At a minimum, there must be one non

- source

oriented SLAMS site located to measure neighborhood scale Pb concentrations in urban areas impacted by re

- entrained dust from roadways, closed industrial sources which previously were significant sources of Pb, hazardous waste sites, constructi on and demolition projects, or other fugitive dust sources of Pb.

EPA announced on October 15, 2008 the final revisions to the Lead NAAQS. EPA added a new Primary standard of 0.15 ug/m3 as a running 3 month average. The initial number of lead monitors to be added to the network was to be based on source emissions of 1 or more tons of lead. EPA is reconsidering the initial 1 ton threshold and instead is considering areas with sources emitting 0.5 tons as triggering the source oriented monitoring requirement s

. Because Nashville/Davidson County has no sources that generate lead emissions of 0.5 ton/year, and in accordance to the provisions designated in the EPA CFR, November 12, 2008 Final Rule for Lead, the MPHDPCD is not required and therefore will not parti cipate in any source

- oriented lead monitoring for FY2010



## 2 .7 CO Monitoring Network Requirements:

40 CFR 58 Subpart G, Appendix D to Part 58 Revised as of July 1, 2009

Carbon Monoxide (CO) Design Criteria:

(a) There are no minimum requirements for the number of CO monitoring sites. Continued operation of existing SLAMS CO sites u sing FRM or FEM is required until discontinuation is approved by the EPA Regional Administrator. Where SLAMS CO monitoring is ongoi ng, at least one site must be a maximum concentration site for that area under investigation.



## 2 .8 Air Quality Index (AQI) Reporting Requirements:

40 CFR 58 Subpart F, 58.50 Revised as of July 1, 2009

Index Reporting Criteria:

(a) The State or where applicable, local agency shall report to the general public on a daily ba sis through prominent notice a air quality index that complies with the requirements of appendix G to this part. (b) Reporting is required for all individual MSA with a popul ation exceeding 350,000. (c) The population of a MSA for purposes of index reporting is the most recent decennial U.S. census population.



## Table 4 Air Qu ality Index Minimum Reporting Requirements

Geographic Area 2000 Census Required to Have AQI Reporting Daily AQI/Air Quality

Forecasts Provided

Nashville

- Davidson, TN 1,311,789 Yes Yes



## 2 .9 Nashville’s Interpretation of Compliance to Ambient Air Monitor Requirements:

The monitoring network is evaluated annually to account for any necessary changes which may involve the addition, discontinuation, revision, or modification of a monitoring site within the network. We have examined each air monitoring site and have evaluated each accordingly to the requirements and provisions of the new regulations in CFR 40, Parts 50, 53, and 58. We have concluded that the number and location of the a ir monitors in our network contribute by the best

means , t o provide sufficient air quality data and reliable information to the public.

The following tables and maps represent the current monitor network description for Nashville/Davidson County and the Nashville Core
Based Statistical Area (CBSA ).Table 5 represents the number of monitors required by 40 CFR part 58 and the number currently operated within the Nashville CBSA. Table 7 represents the most current evaluation of MPHPCD’s ambient air monitoring network

. F 

### rom this information we have concluded tha t the number of monitoring sites

, the designated monitoring methods, and the prima ry monitoring objectives sufficiently comply with the regulations and guidance as set by EPA.

## 5

Table 5 Is Nashville’s interpretation of ambient air monitors needed to me et 40 CFR, Part 58 requirements:



## Table 5 Nashville’s Compliance to Ambient Air Monitors Requirements

Census Area Identification and Population Data 12128

Lead 42101

CO 42401

SO2 42602

NO2 44201 Ozone 81102 PM 10 88101 PM 2.5 88101

PM 2.5 Speciation 88501 or

88502

PM 2.5

Continuous

CBS

2003

Code Census

2000/

Est. 2009 CBSA

Title (MS Areas)

Operating Required Operating Required Operating Required Operating Required Operating 2007

- 2009

8 Hr

DV

Required Operating 2009 24

Hr Max

150 ug/m3 2009

Annual 50 ug/m3

Required Operating 2007

- 2009
Annual

DV 2007

-

2009

24 Hr

DV
35/65 ug/m3

Required Operating Required Operating Required

34980 1311789/1

582264 Nashville/

Davidson 0 0 1 0 1 0 1 0 7 0.078 2 2 37 18.4 2

- 4 3 11.8 26 3 1 1 2 2



### Figure 1 displays the monitoring sites locations within the Nashville CBSA: 

## Figure I

## 6 Table 6 is the locations of the monitoring sites within the Nashville CBSA:



## Table 6
Nashville

- Davidson

-- Murfreesboro, TN CBSA Area

AQ S Site

Number Name REPO G

CODE Latitude Longitude Street Address CBSA2003Title

471490101 Ozone 1025 +35.732778

- 86.598889 EAGLEVILLE PUCKETT'S FARM Nashville

- Davidson

-- Murfreesboro, TN

471650007 Ozone, PM2.5 POC1, PM2.5 POC2,

PM2.5 Cont POC3 1025 +36.297778

- 86.652778 ROCKLAND RECREATION AREA

OLD HICKORY DAM Nashville

- Davidson

-- Murfreesboro, TN

471650101 Ozone 1025 +36.453889

- 86.564167 COTTONTOWN WRIGHT'S FARM Nashville

- Davidson

-- Murfreesboro, TN

471870106 Ozone 1025 +35.951944

- 87.137222 FAIRVIEW MIDDLE SCHOOL CROW

CUT ROAD Nashville

- Davidson

-- Murfreesboro, TN

471890103 Ozone 1025 +36.060278

- 86.286111 CEDARS OF LEBANON STATE PARK Nashville

- Davidson

-- Murfreesboro, TN

470370002 PM10 0682 +36.143244

- 86.754611 333 MURFREESBORO RD Nashville

- Davidson

-- Murfreesboro, TN

470370011 SO2, NO2, Ozone 0682 +36.205000

- 86.744722 1015 EAST TRINITY LANE Nashville

- Davidson

-- Murfreesboro, TN

470370021 CO 0682 +36.159167

- 86.781667 700 BRO A DWAY Nashville

- Davidson

-- Murfreesboro, TN

470370023 PM2.5 POC1, PM2.5 POC2, PM2.5

Cont POC3, PM2.5 Spec POC5 0682 +36.176326

- 86.738902 105 SOUTH 17TH ST at LOCKELAND

SCHOOL Nashville

- Davidson

-- Murfreesboro, TN

470370024 PM10 POC1, PM10 POC2 0682 +36.162763

- 86.854927 56TH AVE AND LOUISIANA ST Nashville

- Davidson

-- Murfreesboro, TN

470370026 Ozone 0682 +36.150556

- 86.621111 PERCY PRIEST Nashville

- Davidson

-- Murfreesboro, TN

470370036 1 PM2.5 0682 +36.118251

- 86.873547 400 DAVIDSON RD Nashville

- Davidson

-- Murfreesboro, TN

Figure 2 is the map locations of the monitoring sites: 

## Figure 2

## 7 Figure 3 indicates the current locations of the ambient air monitoring sites in Nashville and Davidson County:



## Figure 3

Percy Priest Dam

470370026

Ozone 44201

- 047 East Health Center

470370011

Ozone 44201

- 047

NO2 42602

- 074

SO2 42401

- 061

Lockeland School

470370023

PM2.5 POC1 88101

- 120

PM2.5 POC2 88101

- 120

PM2.5 POC3 88502

- 717

McCann School

470370024

PM10 POC1 81102

- 063

PM10 POC2 81102

- 063

Hillwood School

470370036

PM2.5 POC1 88101

- 120

Trevecca College

470370002

PM10 81 102 POC1

- 063 Hume Fogg School

470370021

CO 42101

- 054

Lentz Public Health Dept PM10 API only

No Site ID

## 8 The following is the most current Nashville/Davidson Air Monitoring Network Review



### .



## Table 7
2011 Annual Ambient Monitoring Network Evaluation Date Reviewed: March 11, 2011

AIRS Site

Number Street Address

Pollutant Method

Code Specific Monitoring

Objective Spatial Scale Meet Monitoring Objective? NAMS Hard

Copy

Information

Form and

Photos

Available? Sampling

Frequency AQI

Site? Emergency

Episode

Site? Comments

470370002 Trevecca College

333 Murfreesboro

Road PM 10, 063 Population oriented

surveillance Neighborhood Yes Yes Every 6 th day  SLAMS

470370011 East Health Center

1015 E. Trinity Lane  O 3 ;

 SO 2 ;

 NO 2 ;  047

 061

 074 High, population

oriented surveillance Neighborhood Yes Yes  Continuous

 Continuous

 Continuous  O 3 ;

 SO 2

 NO 2  O 3 ;

 SO 2 ;

 NO 2  O 3 : NAMS

 SO 2 : NAMS;

 NO 2 : SLAMS

470370021 Hume Fogg School

700 Broadway CO 054 High, mobile oriented

surveillance Micro Yes Yes Continuous CO CO  NAMS

470370023 Lockeland School

105 South 17 th Street  PM 2.5 , POC1;

 PM 2.5 , POC2;

 PM 2.5 , POC3 TEOM;

 PM 2.5 , POC5 Speciation

 120

 120

 717

 810 Population oriented

surveillance Neighborhood Yes Yes  Daily

 Every 6 th day

 Continuous

 Every 6 th
day PM 2.5  SLAMS;

 SLAMS;

 SLAMS;

 URG 3000N
Carbon

Monitor

installed

2/10/09. Sampling began 4/1/09

470370024 McCann School

1300 56 th Ave. North  PM 10, POC1;

 PM 10, POC2 063 High, source oriented

surveillance Middle Yes Yes Every 6 th day PM 10  NAMS;

 SLAMS

470370026 Percy Priest Lake

Stewart’s Ferry Pike O 3 047 High, background

surveillance Urban Yes Yes Continuous O 3  SLAMS

470370036 Hillwood High

School

400 Davidson Road PM 2.5 120 High population

oriented surveillance Neighborhood Yes Yes Daily  SLAMS

PM10 AQI only. No Id # Lentz Health Center

311 23rd Ave. North PM 2.5 063 Yes Daily PM 10 PM 10 Used for AQI only

## 9

## 10

## 11 Nashville Air Monitoring Report Criteria Summary

(1) The AQS site
identificati

on number. Parameter POC
Identifier Reporting

Org. (2) The

location, including

street
address and geographical
coordinates. (3) The

sampling
and analysis method(s)
for each

measured parameter. (4) The

operating
schedules for

each monitor. (5) Any

proposals to

remove or

move a monitoring
station within a period of 18
months following plan

submittal. (6) The

monitoring objective and spatial scale of representative
ness for each

monitor as
defined in appendix D to this part. (7) The

identification of any sites that are
suitable and sites
that are not
suitable for

compa rison against the
annual PM2.5 NAAQS as described in §

58.30. (8) The MSA,

CBSA, CSA

or other area represented by the
monitor.

470370021 42101 1 0682 See table. See table. Continuous No See table. DNA See table.

470370011 42401 1 0682 See table. See table. Continuous No See table. DNA See table.

470370011 42602 1 0682 See table. See table. Continuous No See table. DNA See table.

470370011 44201 1 0682 See table. See table. Continuous No See table. DNA See table.

470370026 44201 1 0682 See table. See table. Continuous No See table. DNA See table.

470370002 81102 1 0682 See table. See table. 1 in 6 No See table. DNA See table.

470370024 81102 1 0682 See table. See table. 1 in 6 No See table. DNA See table.

470370024 81102 2 0682 See table. See table. 1 in 6 No See table. DNA See table.

470370023 88101 1 0682 See table. See table. Every Day No See table. Suitable See table.

470370023 88101 2 0682 See table. See table. 1 in 6 No See table. Suitable See table.

470370023 88502 3 0682 See table. See table. Continuous No See table. Does Not Apply See table.

470370036 88101 1 0682 See table. See table. Every Day No See table. Suitable See table.

470370023 88502 5 0682 See table. See table. 1 in 6 No See table. Not suitable See table.

## 12 Nashville’s Monitors Criteria Data Tables

Airs

Parameter POC REP
ORG
CODE Date

Sampling Began CBSA

2003 Title

Population of CBSA 2006 Est Population of CBSA 2000 Census

Land Use Location Setting

Dominant Source Measurement

Scale Monitor

Objective MONITOR

TYPE Sampling

Instrument Name and Designation

470370002 81102 1 0682 19900101 Nashville

Davidson

-- Murfreesbo ro, TN 1,422,544 1,311,789 COMMERCIAL URBAN AND
CENTER
CITY AREA NEIGHBORHOOD POPULATION
EXPOSURE SLAMS Sierra

Andersen/GMW
1200 RFPS

- 1287

- 063 063

470370011 42401 1 0682 19740301 Nashville

Davidson

-- Murfreesbo ro, TN 1,422,544 1,311,789 RESIDENTIAL URBAN AND
CENTER
CITY AREA NEIGHBORHOOD POPULATION
EXPOSURE SLAMS Dasibi 4108
EQSA

- 1086

- 061
061

470370011 42602 1 0682 19750106 Nashville

Davidson

-- Murfreesbo ro, TN 1,422,544 1,311,789 RESIDENTIAL URBAN AND
CENTER
CITY AREA NEIGHBORHOOD HIGHEST
CONCENTRATI
ON SLAMS Thermo
Environmental
Instruments 42C

RFNA

- 1289

- 074
074

470370011 44201 1 0682 19720101 Nashville

Davidson

-- Murfreesbo ro, TN 1,422,544 1,311,789 RESIDENTIAL URBAN AND
CENTER
CITY AREA NEIGHBORHOOD POPULATION
EXPOSURE SLAMS Thermo
Environmental
Instruments 49C
EQOA

- 0880

- 047
047

470370021 42101 1 0682 19720414 Nashville

Davidson

-- Murfreesbo

ro, TN 1,422,544 1,311,789 COMMERCIAL URBAN AND
CENTER
CITY MOBILE MICROSCALE HIGHEST
CONCENTRATI
ON SLAMS Thermo
Environmental
Instruments 48C
RFCA

- 0981

- 054
054

470370023 88101 1 0682 19990101 Nashville

Davidson

-- Murfreesbo ro, TN 1,422,544 1,311,789 RESIDENTIAL URBAN AND
CENTER
CITY AREA NEIGHBORHOOD POPULATION
EXPOSURE SLAMS

Core Graseby Andersen

RAAS2.5

- 300
RFPS

- 0598

- 120
120

470370023 88101 2 0682 19990101 Nashville

Davidson

-- Murfreesbo ro, TN 1,422,544 1,311,789 RESIDENTIAL URBAN AND
CENTER
CITY AREA NEIGHBORHOOD POPULATION
EXPOSURE SLAMS Graseby Andersen
RAAS2.5

- 300
RFPS

- 0598

- 120
120

## 13

Airs

Parameter POC REP
ORG
CODE Date

Sampling Began CBSA

2003 Title

Population of CBSA 2006 Est Population of CBSA 2000 Census

Land Use Location Setting

Dominant Source Measurement

Scale Monitor

Objective MONITOR

TYPE Sampling

Instrument Name and Designation

470370023 8850 1 3 0682 20010301 Nashville

Davidson

-- Murfreesbo ro, TN 1,422,544 1,311,789 RESIDENTIAL URBAN AND
CENTER
CITY AREA NEIGHBORHOOD POPULATION
EXPOSURE SLAMS

Approved AQI (Non

regulatory) R & P TEOM

Gravimetric 50 deg C PM2.5
VSCC
w/Correction
Factor

717

470370023 88502 5 0682 20020213 Nashville

Davidson

-- Murfreesbo ro, TN 1,422,544 1,311,789 RESIDENTIAL URBAN AND
CENTER
CITY AREA NEIGHBORHOOD POPULATION
EXPOSURE SLAMS

Speciation (Non

r e gulatory) Met One Super

SASS and URG
3000N Carbon
810

470370024 81102 1 0682 19900101 Nashville

Davidson

-- Murfreesbo ro, TN 1,422,544 1,311,789 RESIDENTIAL SUBURBAN AREA MIDDLE SCALE HIGHEST
CONCENTRATI
ON SLAMS Sierra

Andersen/GMW
1200 RFPS

- 1287

- 063
063

470370024 81102 2 0682 20000501 Nashville

Davidson

-- Murfreesbo ro, TN 1,422,544 1,311,789 RESIDENTIAL SUBURBAN AREA MIDDLE SCALE HIGHEST
CONCENTRATI
ON SLAMS Sierra

Andersen/GMW
1200 RFPS

- 1287

- 063
063

470370026 44201 1 0682 19780101 Nashville

Davidson

-- Murfreesbo ro, TN 1,422,544 1,311,789 FOREST RURAL AREA URBAN SCALE HIGHEST
CONCENTRATI
ON SLAMS Thermo
Environmental
Instruments 49C
EQOA

- 0880

- 047
047

470370036 88101 1 0682 19990101 Nashville

Davidson

-- Murfreesbo ro, TN 1,422,544 1,311,789 RESIDENTIAL SUBURBAN AREA NEIGHBORHOOD POPULATION
EXPOSURE SLAMS

Core Graseby Andersen

RAAS2.5

- 300
RFPS

- 0598

- 120
120

## 14 Nashville’s Ambient Air Monitoring Network Additional Criteria Data Tables (including collocated monitors)

Airs Co

FIPS Parameter POC Operating
Schedule REP

ORG
CODE SLI Latitude Longitude Street Address CBSA_2003_Code CBSA_2003_Title

470370002 037 81102 1 1 in 6 0682 L +36.143244

- 86.754611 LESTER & HART STS 34980 Nashville

- Davidson

-- Murfreesboro, TN

470370011 037 42401 1 Continuous 0682 L +36.205000

- 86.744722 1015 TRINITY LANE 34980 Nashville

- Davidson

-- Murfreesboro, TN

470370011 037 42602 1 Continuous 0682 L +36.205000

- 86.744722 1015 TRINITY LANE 34980 Nashville

- Davidson

-- Murfreesboro, TN

470370011 037 44201 1 Continuous 0682 L +36.205000

- 86.744722 1015 TRINITY LANE 34980 Nashville

- Davidson

-- Murfreesboro, TN

470370021 037 42101 1 Continuous 0682 L +36.159167

- 86.781667 810 BRODWAY 34980 Nashville

- Davidson

-- Murfreesboro, TN

470370023 037 88101 1 Every Day 0682 L +36.176326

- 86.738902 105 SOUTH 17TH ST @
LOCKELAND SCHOOL 34980 Nashville

- Davidson

-- Murfreesboro, TN

470370023 037 88101 2 1 in 6 0682 L +36.176326

- 86.738902 105 SOUTH 17TH ST @
LOCKELAND SCHOOL 34980 Nashville

- Davidson

-- Murfreesboro, TN

470370023 037 88502 3 Continuous 0682 L +36.176326

- 86.738902 105 SOUTH 17TH ST @
LOCKELAND SCHOOL 34980 Nashville

- Davidson

-- Murfreesboro, TN

470370023 037 88502 5 1 in 6 0682 L +36.176326

- 86.738902 105 SOUTH 17TH ST @
LOCKELAND SCHOOL 34980 Nashville

- Davidson

-- Murfreesboro, TN

470370024 037 81102 1 1 in 6 0682 L +36.162763

- 86.854927 56TH AVE AND LOUISIANA ST 34980 Nashville

- Davidson

-- Murfreesboro, TN

470370024 037 81102 2 1 in 6 0682 L +36.162763

- 86.854927 56TH AVE AND LOUISIANA ST 34980 Nashville

- Davidson

-- Murfreesboro, TN

470370026 037 44201 1 Continuous 0682 L +36.150556

- 86.621111 PERCY PRIEST 34980 Nashville

- Davidson

-- Murfreesboro, TN

470370036 037 88101 1 Every Day 0682 L +36.118251

- 86.873547 400 DAVIDSON RD 34980 Nashville

- Davidson

-- Murfreesboro, TN