AMBIENT AIR MONITORING NETWORK PLAN

2014

STATE OF NEVADA

DIVISION OF ENVIRONMENTAL PROTECTION

BUREAU OF AIR QUALITY PLANNING

Contact: Daren Winkelman

Ambient Monitoring Program

Bureau of Air Quality Planning

901 S. Stewart Street, Suite 4001

Carson City, Nevada89701

(775) 687-9342 or (775) 687-6396 fax

Email: dwinkelman@ndep.nv.gov
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Table of Contents

List of Figures and Tables.................................................................. iii

Acronyms and Abbreviations............................................................ iv

Overview..................................................................................... 1

Goals........................................................................................... 1

Background.................................................................................. 2

Network Design....................................................................................................... 3

Minimum Monitoring Requirements................................................... 6

Changes in Monitoring Network......................................................... 8

Purpose of Monitors........................................................................ 8

Overview of Monitored Parameters.................................................... 9

Site Information.................................................................................................... 12

Appendix A: Ozone Seasonality Approval Letter........................................ 42

Appendix B: Manse PM10 Monitor Relocation Approval............................43

Appendix C: 5

th Street Relocation Approval...........................................44

Appendix D: Comment Submittal Information.......................................46
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List of Figures

Figure 1 – Site Map......................................................................... 11

Figure 2 – Elko Grammar School #2, 1055 7th Street, Elko, NV.................. 14

Figure 3 – West End Elementary School, 280 S. Russell Street, Fallon, NV ... 17

Figure 4 – Fernley Intermediate School, 320 Hardie Lane Fernley, NV............20

Figure 5 – Carson City Armory, 2601 S. Carson Street, Carson City, NV...... 23

Figure 6 – Church Site, 781 E. Gamebird Pahrump, NV ........................... 26

Figure 7 – Manse Elementary, 1020 E. Wilson Road Pahrump, NV ............ 29

Figure 8 – 145 Glen Oaks St., Pahrump, NV ........................................ 32

Figure 9 – 8825 N. Linda Pahrump, NV .............................................. 35

Figure 10 – Ranchos Aspen Park, 820 Lyell Way Gardnerville, NV............ 38

Figure 11 – Mahoney Forest Service IMPROVE Station, Jarbidge, NV ...... 41

List of Tables

Table 1 – NDEP’s Ambient Air Monitoring Network............................... 5

Table 2- NDEP’s Minimum Monitoring Requirements by Pollutant............ 7
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Acronyms and Abbreviations

AADT: Annual Average Daily Traffic

AQS: Air Quality System

BAQP: Bureau of Air Quality Planning

BAM: Beta Attenuation Monitor

CFR: Code of Federal Regulations

CO: Carbon Monoxide

DCNR: Department of Conservation and Natural Resources

FEM: Federal Equivalent Method

FRM: Federal Reference Method

IMPROVE: Interagency Monitoring of Protected Visual Environments

MOU: Memorandum of Understanding

MSA: Metropolitan Statistical Area

NAAQS: National Ambient Air Quality Standard

NAC: Nevada Administrative Code

NDEP: Nevada Division of Environmental Protection

O3: Ozone

PM: Particulate Matter (2.5 or 10 microns)

POC: Pollutant Occurrence Code

QAPP: Quality Assurance Project Plan

QMP: Quality Management Plan

SLAMS: State and Local Air Monitoring Station

SPMS: Special Purpose Monitoring Station

USEPA: United States Environmental Protection Agency
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Overview

The monitoring program of the Nevada Division of Environmental Protection Bureau of Air 

Quality Planning (NDEP-BAQP) operates an ambient air quality monitoring network of gaseous 

and particulate pollutant monitors. The monitors are located in small communities throughout 

rural Nevada. In the metropolitan areas of Reno and Las Vegas, the Washoe County District 

Health Department, Air Quality Management Division and the Clark County Department of Air 

Quality and Environmental Management operate and maintain their respective monitoring 

networks separate from the NDEP-BAQP. Those agencies submit their Network Plans

independently to the United States Environmental Protection Agency (USEPA). Also, there are 

several federally recognized tribes that conduct air monitoring within Nevada and submit their 

own Annual Network Plans to the USEPA.

The NDEP Bureaus of Air Quality Planning and Air Pollution Control regulate air quality to 

protect public health and the environment. Monitoring data is a crucial component of regulations 

used to determine compliance with the USEPA primary and secondary air quality standards. 

Other important uses of these monitors include support and issuance of air quality forecasts;

support of long-term health assessments; and tracking long-term air quality both to gauge 

effectiveness of emission control and abatement strategies and to quantify accuracy of ambient 

pollutant monitoring.

Goals

The NDEP-BAQP created an ambient air quality monitoring program to provide useful and 

accurate information on air quality, which is used to evaluate the success of the State’s air quality 

programs. The Clean Air Act of 1970, and subsequent amendments, requires the USEPA to 

define national ambient air quality standards (NAAQS) for various air pollutants necessary to 

protect the public from injurious pollution concentrations. Air pollution concentrations that 

exceed the NAAQS can cause a public health hazard, or cause damage to flora, fauna and 

personal property. 

The NAAQS, published by the USEPA, can be found in Title 40 of the Code of Federal 

Regulations (CFR) Part 50. The NAAQS for each pollutant defines the levels of air quality 
2

necessary to protect human health and welfare. An area is considered to be in nonattainment for 

a pollutant if it has violated the NAAQS for that pollutant. The CFR includes procedures for 

evaluating measured air quality against the NAAQS. State air quality standards can be found in 

Nevada Administrative Code (NAC) 445B.22097.

Background

The State of Nevada has four jurisdictions that independently manage their own air programs as 

designated by statute: Department of Conservation and Natural Resources (DCNR), NDEPBAQP; Washoe County District Health Department, Air Quality Management Division; Clark 

County Department of Air Quality and Environmental Management; and various tribal agencies.

State agencies that conduct ambient air monitoring using State and Local Air Monitoring Stations 

(SLAMS) or Special Purpose Monitoring Stations (SPMS), must use Federal Reference Methods 

(FRM) or Federal Equivalent Methods (FEM) that comply with federal quality assurance 

requirements listed in 40 CFR 58, Appendix A. In conjunction with the Network Plan, a BAQP 

quality assurance plan was developed to form the framework for planning, implementing, 

assessing and reporting work performed by the BAQP and for implementing quality assurance 

and quality control protocols.

The Ambient Air Monitoring Program Quality Assurance Project Plan (QAPP) was developed to 

address quality management as well as quality assurance. The QAPP defines the policies, 

procedures, specifications, standards, and documentation necessary to 1) provide data of 

adequate quality to meet monitoring objectives, and 2) minimize loss of air quality data due to 

malfunctions or out-of-control conditions. As part of the QAPP, the Quality Management Plan 

(QMP) describes the organizational structure, functional responsibilities of management and 

staff, lines of authority, and required interfaces between planning, implementing, assessing and 

reporting activities involving environmental data operations. Both the QAPP and QMP will be 

updated during this network plan year.

Additionally, the BAQP has developed ambient monitoring guidelines in order to ensure that 

ambient air quality data collected, at regulated facilities in the State, are of the highest quality and 

conform to federal requirements for quality assurance listed under 40 CFR 58. 
3

Ambient air quality monitoring data must be certified on an annual basis as accurate and 

complete. The certification process begins with the complete submittal of all SLAMS data to the 

federal Air Quality System (AQS) for the calendar year. The 2012 data was submitted for 

certification on March 28, 2013 and the 2013 data was submitted on May 1, 2014. Submittal of 

precision and accuracy data into AQS for 2012 was accomplished on January 4, 2013. Submittal 

of precision and accuracy data into AQS for calendar year 2013 was accomplished by January 

14, 2014.

Network Design

Air quality monitoring is represented by ten SLAMS and one SPMS for a total of eleven ambient 

air quality monitoring stations in Nevada under the jurisdiction of the NDEP-BAQP. The ozone 

monitoring conducted by the NDEP is done on a seasonal basis from April 1st to October 31

st of 

each year. The USEPA’s approval of a seasonal ozone monitoring schedule for the NDEP is 

documented in Appendix A. There are three meteorological stations, one in Carson City, one in 

Pahrump, and one mobile tower that is deployed at various locations within the State. These 

meteorological stations are used to confirm the local meteorological data from the monitoring 

stations.

In addition to these four independent monitoring networks, air quality monitoring is conducted 

through the Interagency Monitoring of Protected Visual Environments (IMPROVE) network by 

the federal land management agencies. There are two IMPROVE monitoring sites in Nevada. 

One is at the Jarbidge Wilderness area and the other is at Great Basin National Park, Lehman 

Caves. The IMPROVE program is a cooperative measurement effort governed by a steering 

committee composed of representatives from federal and regional-state organizations. The 

IMPROVE monitoring program was established in 1985 to aid in the creation of state and federal

implementation plans for the protection of visibility in federal Class I areas. In order to meet the 

site objectives, the IMPROVE site must meet the methodologies and quality assurance and 

quality control (QA/QC) procedures approved by the USEPA Regional Administrator. Utilizing 

the criteria set for the Jarbidge site, the NDEP-BAQP is able to satisfy the USEPA’s regional and 

transport monitoring requirements. According to 40 CFR Part 58 Appendix D 4.7.3, “each state 
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shall install and operate at least one PM2.5 site to monitor for regional background and regional 

transport.” The NDEP-BAQP utilizes the Jarbidge site to meet this particular requirement.
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The following table shows the locations and types of monitors operated by NDEP.

Table 1: NDEP’S Ambient Air Monitoring Network

Location Ozone Carbon Monoxide PM10 PM2.5

Elko 1 (SLAMS)

Fallon 1 (SLAMS)

Fernley 1 (SLAMS)

Carson City Armory 1 (SLAMS) 2 (SLAMS)

Pahrump-Church Site 1 (SLAMS)

Pahrump-Manse Elementary 1 (SLAMS)

Pahrump-Glen Oaks 1 (SLAMS)

Pahrump-Linda Street 1 (SLAMS)

Gardnerville Ranchos 1 (SPMS)

Total 3 5 3

SLAMS – State and Local Air Monitoring Station

SPMS – Special Purpose Monitor Station
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Minimum Monitoring Requirements

The USEPA provides minimum site requirements to monitor for ozone (O3) and particulate 

matter (PM) based on metropolitan statistical area (MSA) population. The NDEP-BAQP’s air 

monitoring network meets or, in most cases, exceeds the minimum network requirements. The 

monitors currently required in the NDEP-BAQP monitoring network by the USEPA are located 

in Carson City (O3), Fallon (O3), Fernley (O3) and Pahrump (PM10). The four PM10 monitoring 

sites in Pahrump are required through a Memorandum of Understanding (MOU) between the 

NDEP, USEPA, Nye County and the Town of Pahrump. Otherwise, according to 40 CFR Part 

58 Appendix D, Tables D-4 and D-5, sections 4.2, 4.3.2, 4.3.3, 4.4.2 and 4.5, additional 

monitoring for criteria pollutants is not presently required. However, based on data obtained 

through special study monitoring in Carson City and Gardnerville, the NDEP-BAQP has 

established a PM2.5 monitoring network. These sites will allow the NDEP-BAQP to establish 

credible data to ascertain PM2.5 conditions within both areas. Within three years, after a valid 

design value is established, the NDEP-BAQP will evaluate the program and determine if 

increased PM2.5 monitoring is needed within the SPMS areas. The following table outlines the 

minimum required monitors within the NDEP ambient air monitoring network.
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Table 2: Minimum Monitoring Requirements by Pollutant

ppb: parts per billion

*Based on 40 CFR Part 58 Appendix D, Tables D-4 and D-5 and sections 4.2, 4.3.2, 4.3.3, 4.4.2 and 4.5, additional monitoring for 

criteria pollutants is not presently required. Additionally, based on the 2008 Lead NAAQS Final Rule, 2010 SO2 NAAQS Final Rule,

and the 2010 NO2 NAAQS Final Rule, the NDEP-BAQP is not required to monitor for these criteria pollutants.

Pollutant

Minimum 

# of

Monitors 

Required

# of 

Monitors 

Active

# of 

Monitors 

needed

Location CSA/MSA County

County 

Pop. 

(2013)

Design 

Values

Ozone 3 3 0

Carson City

Reno-Carson CityFernley CSA and 

Carson City 

Metropolitan 

Statistical Area 

(MSA)

Carson City 54,668

67 ppb

(2011-

2013)

Fallon

Fallon 

Micropolitan 

Statistical Area 

(MSA)

Churchill 25,322

57 ppb

(2011-

2013)

Fernley

Reno-Carson CityFernley Combined 

Statistical Area 

(CSA) and Fernley 

Micropolitan 

Statistical Area 

(MSA)

Lyon 52,960

69 ppb

(2011-

2013)

Lead* 0 0 0 N/A N/A N/A N/A N/A

SO2* 0 0 0 N/A N/A N/A N/A N/A

NO2* 0 0 0 N/A N/A N/A N/A N/A

PM10 4 5 0

Elko (1)

Elko Micropolitan 

Statistical Area 

(MSA)

Elko 53,384

0.0

(2011-

2013)

Pahrump (4)

Las Vegas –

Henderson, NV-AZ 

CSA and Pahrump 

Micropolitan 

Statistical Area 

(MSA)

Nye 44,749

Manse = 1.0

Church = 0.3

Glen Oaks = 

N/A

Linda

Street = 0.3

(2011-

2013)

PM2.5 0 2 0 Carson City

Reno-Carson CityFernley CSA and 

Carson City 

Metropolitan 

Statistical Area 

(MSA)

Carson City 54,668 New Site

PM2.5 0 1 0 Gardnerville

Reno-Carson CityFernley CSA and 

Gardnerville 

Ranchos 

Micropolitan 

Statistical Area 

(MSA)

Douglas 48,478 New Site

Total 7 11 0
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Changes in Monitoring Network

In 2011, the NDEP-BAQP was informed that it had to relocate the PM10 monitor located at the 

Manse School in Pahrump due to the school closing. In February 2011, the NDEP-BAQP

submitted a letter to the USEPA requesting approval to relocate the monitor, which approval was 

received in March of 2011 to move the existing monitor to the Nye County School District 

building. However, the Pahrump School District found a new use for the school, allowing the 

NDEP-BAQP’s monitor to remain at the existing site. At this time, the NDEP-BAQP will 

continue to monitor at the Manse School. If needed, the NDEP-BAQP has access to the Nye 

County School District building as a back-up site. 

The monitoring start date for both PM2.5 monitors at the Carson Armory site was entered 

incorrectly in last year’s annual network plan. The corrected monitoring start date has been

changed from March 1, 2013 to April 1, 2013. There are no further expected changes for this 

next year. Over the next five years, through 2019, the NDEP-BAQP will evaluate the current 

network to determine if any new sites or monitors are required to be added to the existing 

monitoring network. In the event that a review of changes to the PM2.5 monitoring network were

required, the annual network plan and five year network assessment would be used to provide for 

this review. No changes are proposed for the PM2.5 monitoring network for 2013-2014.

Purpose of Monitors

The purpose of the Nevada Air Monitoring Network is to provide useful and accurate 

information on air quality, which is used to evaluate the success of the State’s air quality 

programs. To accomplish this task, the NDEP-BAQP utilizes the NAAQS for each criteria 

pollutant set forth in the Clean Air Act: Carbon Monoxide (CO), Lead (Pb), Nitrogen Dioxide

(NO2), Ozone (O3), coarse and fine particulate matter (PM10 and PM2.5), and Sulfur Dioxide

(SO2). By measuring pollutant concentrations in outdoor air and comparing the measured 

concentrations to corresponding standards, the NDEP-BAQP is able to identify the ambient air 

quality status of an area as either attainment or nonattainment.

The NAAQS are broken down into primary and secondary standards. Primary standards are 

those established to protect public health. Secondary standards are those established to protect 
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the public welfare from adverse pollution effects on soils, water, vegetation, man-made materials, 

animals, weather, visibility, climate, property, and the economy. The scientific criteria upon 

which the standards are based are reviewed periodically by the USEPA, which may reestablish or 

change the standards according to its findings. 

A pollutant measurement that is greater than the ambient air quality standard for its specific 

averaging time is called an exceedance. This is not necessarily a synonym for a violation; for 

each pollutant, there are specific rules about how many exceedances are allowed in a given time 

period before a pattern of exceedances is considered to be a violation of the NAAQS. A 

violation may result in regulatory action to clean-up the area’s air. Exceptions are made to allow 

for certain limited exceedances of the standard that may occur, for example, during exceptional 

events, such as an unusual weather pattern or wildfire. Regulatory action is typically reserved for 

cases where the exceedances are too large or too frequent.

Historically, ambient air quality monitoring by the NDEP-BAQP has looked at trends in air 

quality to aid in the local planning process. Traffic, wood burning stoves, and growth-related 

activities have prompted air quality monitoring in specific areas around the State. Data from 

these sites has led to public education and outreach to communities, identifying the potential 

health effects caused by air pollutants in the environment. Ordinances have also been developed 

and implemented to help control surface area disturbances and other related activities that 

produce dust.

Overview of Monitored Parameters

Carbon Monoxide (CO)

CO is a poisonous gas that, when introduced into the bloodstream, inhibits the delivery of oxygen 

to body tissue. According to the USEPA, the health risk is greatest for individuals with 

cardiovascular disease.

Ozone (O3)

Ground-level ozone, or photochemical smog, is not emitted into the atmosphere as ozone, but 

rather is formed by the reactions of other pollutants. The primary pollutants entering into this 

reaction, volatile organic compounds (VOCs) and oxides of nitrogen, create ozone in the 
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presence of sunlight. According to the USEPA, ozone is a strong irritant of the upper respiratory 

system and also causes damage to crops.

Particulate Matter (PM10)

Particulate matter with an aerodynamic diameter of 10 microns or less is emitted from 

transportation and industrial sources. According to the USEPA, exposure to particle pollution is 

linked to a variety of significant health problems ranging from aggravated asthma to premature 

death in people with heart and lung disease.

Fine Particulate Matter (PM2.5)

Fine particulate matter with a diameter of 2.5 microns or less is created primarily from industrial 

processes and fuel combustion. According to the USEPA, these particles are breathed deeply 

into the lungs. Exposure to fine particle pollution is linked to a variety of significant health 

problems ranging from aggravated asthma to premature death in people with heart and lung 

disease.
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Site Map

Figure 1: A map showing the locations of the monitoring stations maintained in the NDEPBAQP’s network.
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Elko: Detailed Site Information

Prior to 1992 the location for this sampler was the fire station at 723 Railroad Street (ID #32-007-003) in a 

commercial area. In November of 1992 this continuous PM10 monitoring site was relocated to the roof of the State 

offices at 850 Elm Street in a predominantly residential area. The monitoring objective was to determine typical 

concentration/population oriented. The manual sampler was replaced with a continuous Tapered Element Oscillating 

Microbalance (TEOM) PM10 monitor in December 1998. In September 2008, the TEOM monitor was closed and a 

new BAM 1020 monitor was sited at the Elko Grammar School #2.

Pollutant, POC PM10; 1

Parameter Code 81102

Basic monitor objective(s) NAAQS

Site type(s) Population exposure

Monitoring type(s) SLAMS

Instrumental manufacturer and model Met One BAM 1020

Method Code 122

FRM/FEM/ARM/other FEM

Collecting Agency NDEP-BAQP

Analytical Lab N/A

Spatial Scale Neighborhood

Monitoring start date 09/25/2008

Current sampling frequency Continuous

Calculated sampling frequency N/A

Sampling season 01/01-12/31

Analysis Method EQPM-0798-122

Probe Height 2.6 Meters

Dist. fm. supporting structure Vertical Distance =1.2 meters

Dist. fm. obstructions on roof N/A

Dist. fm. Obstructions not on roof (meters) N/A

Dist. fm. trees 27 Meters

Distance to furnace or incinerator flue N/A

Distance between collocated monitors in 

(meters)

N/A

Unrestricted air flow 360 degrees

Probe material Aluminum

Residence time N/A

Site Name Elko

AQS ID 32-007-0005

GIS Coordinates Lat +40.838350

Long -115.766029

Location Elko Grammar School #2

Address 1055 7th Street 

County Elko

Distance to Road 18 Meters

Traffic Count 2600 AADT (2012) Station #0070208

Groundcover Asphalt

Representative Area Elko Micropolitan Statistical Area (MSA)
13

Elko: Detailed Site Information (Cont.)

Changes in the next 18 months? No

Suitable for PM2.5 comparison? N/A

Frequency of flow rate verification manual 

PM

N/A

Frequency of flow rate verification 

automated PM

Monthly

Frequency of one point QC check (gaseous) N/A

Last Annual Performance Evaluation 

(gaseous)

N/A

Last two semi-annual flow rate audits for 

PM

6/19/2013, 11/20/2013
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Figure 2: PM10 Monitor located at Elko Grammar School #2, 1055 7th Street, 

Elko, NV. 
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Fallon: Detailed Site Information

The ozone monitoring site at 280 South Russell Street is at the West End Elementary School in a residential 

neighborhood that may be affected by agricultural operations surrounding the City of Fallon. The monitoring 

objective is to determine typical concentration/population oriented. PM10 sampling commenced at this site in May 

1993 and was discontinued at the end of June 1998. Monitoring for ozone began in October 1999 as an ozone 

transport site downwind of Reno and Fernley.

Pollutant, POC Ozone, 1

Parameter Code 44201

Basic monitoring objective(s) NAAQS

Site type(s) Population Exposure

Monitor type(s) SLAMS

Instrument manufacturer and model Teledyne API Model 400 Series

Method Code 087

FRM/FEM/ARM/other FEM

Collecting Agency NDEP-BAQP

Analytical Lab N/A

Spatial Scale Neighborhood

Monitoring start date 10/01/1999

Current sampling frequency Seasonal

Calculated sampling frequency N/A

Sampling season 04/01-10/31

Analysis Method EQOA-0992-087

Probe Height 3.2 Meters

Dist. fm. supporting structure 1 meter from wall

Dist. fm. obstructions on roof N/A

Distance from obstruction not on roof 

(meters)

22 Meters

Distance fm. trees Greater than 10 meters

Distance to furnace or incinerator flue N/A

Distance between collocated monitors 

(meters)

N/A

Unrestricted airflow 180 Degrees

Probe material Teflon

Site Name Fallon

AQS ID 32-001-0002

GIS Coordinates Lat +39.472471

Long -118.783624

Location West End Elementary School

Address 280 South Russell Street

County Churchill

Distance to Road 65 Meters

Traffic Count 250 AADT (2012) Station #0010135

Groundcover Dirt and Gravel

Representative Area Fallon Micropolitan Statistical Area (MSA)
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Fallon: Detailed Site Information (Cont.)

Residence time 9.4 seconds

Changes in the next 18 months? No

Suitable for PM 2.5 comparison? N/A

Frequency of flow rate verification 

Manual PM

N/A

Frequency of flow rate verification 

automated PM

N/A

Frequency of one point QC check 

(gaseous)

Every two weeks during sampling season 

Last Annual Performance Evaluation 

(Gaseous)

09/18/2013

Last two semi-annual flow rate audits 

for PM 

N/A
17

Figure 3: Ozone Monitor located at West End Elementary School, 280 S. 

Russell Street, Fallon, NV. 
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Fernley Intermediate School: Detailed Site Information

Ozone monitoring is done at the Fernley Intermediate School, which is located at 320 Hardie Lane. This is an area 

of mainly residential and agricultural use. There has recently been a large growth of industry both upwind and 

downwind of this site. Monitoring for PM10 at this site commenced on May 1995 to determine the agricultural and 

industrial source impacts and population exposure. PM10 sampling was discontinued in November 1998. Ozone 

monitoring began at this site in July 2007. However, ozone monitoring (SPMS) was previously conducted at the 

Fernley Volunteer Fire Department starting in October 1997 and discontinued in October 2003.

Pollutant, POC Ozone, 1

Parameter Code 44201

Basic monitor objective(s) NAAQS

Site type(s) Population Exposure

Monitoring type(s) SLAMS

Instrumental manufacturer and model Teledyne API Model 400 Series

Method Code 087

FRM/FEM/ARM/other FEM

Collecting Agency NDEP-BAQP

Analytical Lab N/A

Spatial Scale Neighborhood

Monitoring start date 07/06/2007

Current sampling frequency Continuous

Calculated sampling frequency N/A

Sampling season 04/01-10/31

Analysis Method EQOA-0992-087

Probe Height 7 meters

Dist. fm. supporting structure Vertical Distance above 2.1 meters

Dist. fm. obstructions on roof N/A

Dist. fm. Obstructions not on roof 

(meters)

N/A

Dist. fm. trees 15 Meters

Distance to furnace or incinerator flue N/A

Site Name Fernley 

AQS ID 32-019-0006

GIS Coordinates Lat +39.602787

Long -119.247741

Location Fernley Intermediate School

Address 320 Hardie Lane

County Lyon

Distance to Road 119 Meters

Traffic Count 8600 AADT (2012) Station # 0190022

Groundcover Paved, cement, gravel and dirt

Representative Area Reno-Carson City-Fernley Combined Statistical Area 

(CSA) and Fernley Micropolitan Statistical Area (MSA)
19

Fernley Intermediate School: Detailed Site Information (Cont.)

Distance between collocated monitors in 

(meters)

N/A

Unrestricted air flow 360 Degrees

Probe material Teflon

Residence time 9.5 Seconds

Changes in the next 18 months? No

Suitable for PM 2.5 comparison? N/A

Frequency of flow rate verification 

manual PM

N/A

Frequency of flow rate verification 

automated PM

N/A

Frequency of one point QC check 

(gaseous)

Every two weeks during sampling 

season.

Last Annual Performance Evaluation 

(gaseous)

06/27/2013

Last two semi-annual flow rate audits 

for PM

N/A
20

Figure 4: Ozone Monitor located at Fernley Intermediate School, 320 Hardie 

Lane Fernley, NV.
21

2601 S. Carson Street: Detailed Site Information

Due to the city of Carson City re-purposing use of the old monitoring location on 3300 East Fifth Street, the new SLAMS 

monitoring site is now adjacent to Hwy 395, in a residential neighborhood and a light industrial area. The new collocated 

PM2.5 and ozone monitoring site is located at 2601 S. Carson Street where the old Army National Guard site used to reside. 

The monitoring objective for PM2.5 and ozone is to determine maximum concentration based on Appendix D CFR 58 (4.1) (b)

for this site.

Pollutant, POC PM2.5, 1 PM2.5, 2 Ozone, 1

Parameter Code 88101 88101 44201

Basic monitoring objective(s) NAAQS NAAQS NAAQS

Site type(s) Max concentration Max concentration Max 

Concentration

Monitor type(s) SLAMS QA COLLOCATED SLAMS

Instrument manufacturer and 

model

MET ONE BAM 

1020

BGI PQ200 TELEDYNE 

400 Series

Method Code 170 116 087

FRM/FEM/ARM/other FEM FRM FEM

Collecting Agency NDEP-BAQP NDEP-BAQP NDEP-BAQP

Analytical Lab N/A Desert Research 

Institute

N/A

Spatial Scale Neighborhood Neighborhood Neighborhood

Monitoring start date 04/01/2013 04/01/2013 04/01/2013

Current sampling frequency Continuous 1:6 Seasonal

Calculated sampling frequency N/A N/A N/A

Sampling season 01/01-12/31 01/01-12/31 04/01-10/31

Analysis Method EQPM-0308-170 RFPS-0498-116 EQOA-0992-087

Probe Height 4.9 Meters 4.9 Meters 4 Meters

Dist. fm. supporting structure 1.5 Meters 1.5 Meters 1 Meter

Site Name Carson City Armory

AQS ID 32-510-0020

GIS Coordinates Lat +39.1447

Long -119.7661

Location Carson City

Address 2601 S. Carson Street

County Carson

Distance to Road 109 Meters

Traffic Count 43,500 AADT (2012) Station #0250148

Groundcover Gravel

Representative Area Reno-Carson City-Fernley CSA and Carson City Metropolitan 

Statistical Area (MSA)
22

2601 S. Carson Street: Detailed Site Information (Cont.)

** Only one semi-annual flow rate was required for this new site due to the initial operational period of 9 months.

Dist. fm. obstructions on roof N/A N/A N/A

Distance from obstruction not 

on roof (meters)

N/A N/A N/A

Distance fm. trees 37 Meters to West 37 Meters to the West 37 Meters to the 

West

Distance to furnace or 

incinerator flue

N/A N/A N/A

Distance between collocated 

monitors (meters)

3 Meters 3 Meters N/A

Unrestricted airflow 360 Degrees 360 Degrees 360 Degrees

Probe material N/A N/A N/A

Residence time N/A N/A 5.7 Seconds

Changes in the next 18 

months?

No No No

Suitable for PM2.5

comparison?

Yes Yes N/A

Frequency of flow rate 

verification Manual PM

Monthly N/A

Frequency of flow rate 

verification automated PM

Monthly N/A

Frequency of one point QC 

check (gaseous)

N/A N/A Every two 

weeks during 

sampling 

season.

Last Annual Performance 

Evaluation (Gaseous)

N/A N/A 09/24/2013

Last two semi-annual flow rate 

audits for PM 

11/01/2013 ** 11/01/2013 ** N/A 
23

Figure 5: Ozone/PM2.5 Monitors located at Carson City Armory, 2601 S. 

Carson Street Carson City, NV.
24

Church: Detailed Site Information

The Church Site began operation in 2004 to complement the existing three other sites in the Pahrump monitoring 

network. Monitoring is accomplished with a continuous beta attenuated monitor located in the southeast corner of 

the Catholic Church. This site represents the southern-most monitoring location in Pahrump Valley. The monitoring 

objective of this site is a significant source of PM10. The surrounding area is characterized by residential use with 

little commercial use, as well as some native desert with a mix of dirt and paved roads.

Pollutant, POC PM10, 1

Parameter Code 81102

Basic monitor objective(s) NAAQS

Site type(s) Source Oriented – Dry lake bed 6 miles to the 

south

Monitoring type(s) SLAMS

Instrumental manufacturer and model Met One BAM 1020

Method Code 122

FRM/FEM/ARM/other FEM

Collecting Agency NDEP-BAQP

Analytical Lab N/A

Spatial Scale Urban

Monitoring start date 02/14/2004

Current sampling frequency Continuous

Calculated sampling frequency N/A

Sampling season 01/01-12/31

Analysis Method EQPM-0798-122

Probe Height 4 Meters

Dist. fm. supporting structure Vertical distance above 2 meters

Dist. fm. obstructions on roof N/A

Dist. fm. Obstructions not on roof 

(meters)

14 Meters

Dist. fm. trees 50 Meters

Distance to furnace or incinerator flue N/A

Distance between collocated monitors in 

(meters)

N/A

Site Name Church

AQS ID 32-023-0013

GIS Coordinates Lat + 36.159639

Long -115.996263

Location Pahrump

Address 781 E. Gamebird

County Nye

Distance to Road 100 Meters

Traffic Count 950 AADT (2012) Station #0230010

Groundcover Desert

Representative Area Las Vegas – Henderson, NV-AZ CSA and Pahrump 

Micropolitan Statistical Area (MSA)
25

Church: Detailed Site Information (Cont.)

Unrestricted air flow 360 Degrees

Probe material Aluminum

Residence time N/A

Changes in the next 18 months? No

Suitable for PM2.5 comparison? N/A

Frequency of flow rate verification 

manual PM

N/A

Frequency of flow rate verification 

automated PM

Monthly

Frequency of one point QC check 

(gaseous)

N/A

Last Annual Performance Evaluation 

(gaseous)

N/A

Last two semi-annual flow rate audits for 

PM

05/21/2013, 11/18/2013
26

Figure 6: PM10 Monitor located at Church Site, 781 E. Gamebird Pahrump, 

NV.
27

Manse Elementary: Detailed Site Information

The Manse site represents the monitoring objective for the highest concentrations of PM10 in Pahrump. This site 

replaces the Community Pool site, which at the time it was operating, represented the highest concentrations of PM10

in Pahrump. Located at 1020 E. Wilson Road, the Manse Elementary site is located on the roof of the school and 

monitors for PM10 using the continuous beta attenuation monitor. The area adjacent to this site is characterized by

mostly commercial use with some residential use, and is adjacent to the busiest activity area of Pahrump. This site is 

located downwind from residential construction developments that have cleared large parcels of ground for building, 

as well as agricultural areas that cultivate large areas of farm-ground and raise livestock. Roads surrounding this site 

are both paved and dirt. 

Site Name Manse Elementary

AQS ID 32-023-0014

GIS Coordinates Lat +36.212787 

Long -115.994802

Location Pahrump

Address 1020 E. Wilson Road

County Nye

Distance to Road 50 Meters

Traffic Count 11,000 AADT (2012) Station #0230006

Groundcover Gravel Schoolyard

Representative area Las Vegas – Henderson, NV-AZ CSA 

and Pahrump Micropolitan Statistical 

Area (MSA)

Pollutant, POC PM10, 1

Parameter Code 81102

Basic monitor objective(s) NAAQS

Site type(s) Highest Concentration

Monitoring type(s) SLAMS

Instrumental manufacturer and model Met One BAM 1020

Method Code 122

FRM/FEM/ARM/other FEM

Collecting Agency NDEP-BAQP

Analytical Lab N/A

Spatial Scale Middle

Monitoring start date 11/17/2005

Current sampling frequency Continuous

Calculated sampling frequency N/A

Sampling season 01/01-12/31

Analysis Method EQPM-0798-122

Probe Height 3.0 Meters

Dist. fm. supporting structure Vertical distance above 1 meters

Dist. fm. obstructions on roof N/A

Dist. fm. Obstructions not on roof 

(meters)

N/A

Dist. fm. trees 10 Meters

Distance to furnace or incinerator flue N/A
28

Manse Elementary: Detailed Site Information (Cont.)

Distance between collocated monitors in 

(meters)

N/A

Unrestricted air flow 360 Degrees

Probe material Aluminum

Residence time N/A

Changes in the next 18 months? No

Suitable for PM2.5 comparison? N/A

Frequency of flow rate verification 

manual PM

N/A

Frequency of flow rate verification 

automated PM

Monthly

Frequency of one point QC check 

(gaseous)

N/A

Last Annual Performance Evaluation 

(gaseous)

N/A

Last two semi-annual flow rate audits 

for PM

5/21/2013, 11/18/2013
29

Figure 7: PM10 Monitor located at Manse Elementary, 1020 E. Wilson Road 

Pahrump, NV.
30

Glen Oaks: Detailed Site Information

Monitoring began at the Willow Creek site in 2003. The monitor was located at 1500 Red Butte on the roof of a 

building in which irrigation equipment for a golf course was housed. The monitoring objective of this site was to 

measure typical concentrations/population oriented of PM10 using the beta attenuation monitor. The surrounding 

area adjacent to this site was fairway/golf course and residential structures. Due to closure of the golf course, the 

Willow Creek site was relocated to the Glen Oaks sewage treatment plant in 2009. The Glen Oaks site is a short 

distance away from the existing golf course site and the monitoring objective did not change.

Site Name Glen Oaks

AQS ID 32-023-0015

GIS Coordinates Lat +36.193469

Long -116.007584

Location Pahrump

Address 145 Glen Oaks St.

County Nye

Distance to Road 200 Meters

Traffic Count 11,000 AADT (2012) Station #0230006

Groundcover Grass/Gravel

Representative Area Las Vegas – Henderson, NV-AZ CSA and Pahrump 

Micropolitan Statistical Area (MSA)

Pollutant, POC PM10, 1

Parameter Code 81102

Basic monitor objective(s) NAAQS

Site type(s) Population Exposure

Monitoring type(s) SLAMS

Instrumental manufacturer and model Met One BAM 1020

Method Code 122

FRM/FEM/ARM/other FEM

Collecting Agency NDEP-BAQP

Analytical Lab N/A

Spatial Scale Neighborhood

Monitoring start date 07/10/2009

Current sampling frequency Continuous

Calculated sampling frequency N/A

Sampling season 01/01-12/31

Analysis Method EQPM-0798-122

Probe Height 6.0 Meters 

Dist. fm. supporting structure Vertical Distance above 3 meters

Dist. fm. obstructions on roof N/A

Dist. fm. Obstructions not on roof 

(meters)

15 Meters

Dist. fm. trees 12 Meters

Distance to furnace or incinerator flue N/A

Distance between collocated monitors in 

(meters)

N/A
31

Glen Oaks: Detailed Site Information (Cont.)

Unrestricted air flow 360 Degrees

Probe material Aluminum

Residence time N/A

Changes in the next 18 months? No

Suitable for PM2.5 comparison? N/A

Frequency of flow rate verification 

manual PM

N/A

Frequency of flow rate verification 

automated PM

Monthly

Frequency of one point QC check 

(gaseous)

N/A

Last Annual Performance Evaluation 

(gaseous)

N/A

Last two semi-annual flow rate audits 

for PM

5/21/2013, 11/18/2013
32

Figure 8: PM10 Monitor located at 145 Glen Oaks St., Pahrump, NV.
33

Linda Street: Detailed Site Information

Monitoring at the Linda Street site was started in 2003. The site is located at 8825 North Linda Street. The beta 

attenuation monitor is located on the roof of an old railroad box car and represents not only the northern-most site in 

the Pahrump monitoring network, but the most rural area. There is some residential surrounding this site, but mainly 

native desert vegetation with little or no surface disturbances. The monitoring objective for this site is general 

background levels of PM10 in Pahrump.

Site Name Linda Street

AQS ID 32-023-0011

GIS Coordinates Lat +36.349408

Long -116.031976

Location Pahrump

Address 8825 N. Linda

County Nye

Distance to Road 20 Meters

Traffic Count 22,500 AADT (2012) Station #0230008

Groundcover Desert

Representative Area Las Vegas – Henderson, NV-AZ CSA and Pahrump 

Micropolitan Statistical Area (MSA)

Pollutant, POC PM10, 1

Parameter Code 81102

Basic monitor objective(s) NAAQS

Site type(s) General Background

Monitoring type(s) SLAMS

Instrumental manufacturer 

and model

Met One BAM 1020

Method Code 122

FRM/FEM/ARM/other FEM

Collecting Agency NDEP-BAQP

Analytical Lab N/A

Spatial Scale Regional

Monitoring start date 05/03/2003

Current sampling frequency continuous

Calculated sampling 

frequency

N/A

Sampling season 01/01-12/31

Analysis Method EQPM-0798-122

Probe Height 6.7 Meters 

Dist. fm. supporting structure Vertical Distance above 3 meters

Dist. fm. obstructions on roof N/A

Dist. fm. obstructions not on 

roof (meters)

21 Meters

Dist. fm. trees 10 Meters

Distance to furnace or 

incinerator flue

N/A
34

Linda Street: Detailed Site Information (Cont.)

Distance between collocated 

monitors in (meters)

N/A

Unrestricted air flow 360 Degrees

Probe material Aluminum

Residence time N/A

Changes in the next 18 

months?

No

Suitable for PM2.5

comparison?

N/A

Frequency of flow rate 

verification manual PM

N/A

Frequency of flow rate 

verification automated PM

Monthly

Frequency of one point QC 

check (gaseous)

N/A

Last Annual Performance 

Evaluation (gaseous)

N/A

Last two semi-annual flow rate 

audits for PM

5/21/2013, 11/18/2013
35

Figure 9: PM10 Monitor located at 8825 N. Linda Pahrump, NV.
36

Ranchos Aspen Park: Detailed Site Information

The Ranchos Aspen Park site is a new Special Purpose Monitoring (SPM) site within the NDEP network. The 

monitoring objective is to determine typical concentration/population exposure.

Site Name Ranchos Aspen Park

AQS ID 32-005-0007

GIS Coordinates Lat +38.897557

Long -119.732507

Location Gardnerville

Address 820 Lyell Way

County Douglas

Distance to Road 20 Meters

Traffic Count 5600 AADT (2012) Station #0050066

Groundcover Gravel

Representative Area Reno-Carson City-Fernley CSA and Gardnerville 

Ranchos Micropolitan Statistical Area (MSA)

Pollutant, POC PM2.5, 1

Parameter Code 88101

Basic monitor objective(s) NAAQS

Site type(s) Population exposure

Monitoring type(s) SPMS

Instrumental manufacturer 

and model

Met One BAM 1020

Method Code 170

FRM/FEM/ARM/other FEM

Collecting Agency NDEP-BAQP

Analytical Lab N/A

Spatial Scale Neighborhood

Monitoring start date 04/01/2013

Current sampling frequency Continuous

Calculated sampling 

frequency

NA

Sampling season 01/01-12/31

Analysis Method EQPM-0308-170

Probe Height 6.7 Meters 

Dist. fm. supporting structure Vertical Distance above 3 meters

Dist. fm. obstructions on roof N/A

Dist. fm. Obstructions not on 

roof (meters)

7 Meters

Dist. fm. trees 10 Meters

Distance to furnace or 

incinerator flue

N/A

Distance between collocated 

monitors in (meters)

N/A

Unrestricted air flow 360 Degrees

Probe material Aluminum
37

Ranchos Aspen Park: Detailed Site Information (Cont.)

Residence time N/A

Changes in the next 18 

months?

No

Suitable for PM2.5

comparison?

Yes

Frequency of flow rate 

verification manual PM

N/A

Frequency of flow rate 

verification automated PM

Monthly

Frequency of one point QC 

check (gaseous)

N/A

Last Annual Performance 

Evaluation (gaseous)

N/A

Last two semi-annual flow rate 

audits for PM

10/28/2013 **

** Only one semi-annual flow rate was required for this new site due to the initial operational period of 9 months.
38

Figure 10: PM2.5 Monitor located at Ranchos Aspen Park, 820 Lyell Way 

Gardnerville, NV.
39

IMPROVE Station: Detailed Site Information

Site Name Jarbidge Wilderness IMPROVE

AQS ID 32-007-9000

GIS Coordinates Lat +41.8926

Long -115.4261

Location Mahoney Forest Service Station

Address Jarbidge Wilderness

County Elko

Distance to Road 100 Feet

Traffic Count N/A

Groundcover Dirt/Grass

Representative Area Rural (Not in an urban area)

Pollutant, POC PM2.5, 1

Parameter Code 88101

Basic monitor objective(s) Other

Site type(s) General/Background

Monitoring type(s) IMPROVE

Instrumental manufacturer 

and model

Crocker Nuclear Lab, IMPROVE Sampler Version II

Method Code N/A

FRM/FEM/ARM/other Other 

Collecting Agency US Forest Service (USFS)

Analytical Lab Crocker Nuclear Lab

Spatial Scale Regional

Monitoring start date 01/1988

Current sampling frequency 1:3 Filters Collected Weekly

Calculated sampling frequency N/A

Sampling season 01/01-12/31

Analysis Method N/A

Probe Height 4 Meters

Dist. fm. supporting structure 2 Meters

Dist. fm. obstructions on roof N/A

Dist. fm. Obstructions not on 

roof (meters)

18 Meters

Dist. fm. trees 15 Meters

Distance to furnace or 

incinerator flue

N/A

Distance between collocated 

monitors in (meters)

N/A

Unrestricted air flow Yes

Probe material Aluminum

Residence time N/A
40

IMPROVE Station: Detailed Site Information (Cont.)

Changes in the next 18 

months?

No

Suitable for PM2.5

comparison?

No

Frequency of flow rate 

verification manual PM

Unable to Determine

Frequency of flow rate 

verification automated PM

N/A

Frequency of one point QC 

check (gaseous)

N/A

Last Annual Performance 

Evaluation (gaseous)

N/A

Last two semi-annual flow 

rate audits for PM

Unable to Determine
41

FIGURE 11: Mahoney Forest Service IMPROVE Station, Jarbidge , NV
42

Appendix A.

Ozone Seasonality Approval Letter
43

Appendix B.

Manse PM10 Monitor Relocation Approval
44
45
46

Appendix D.

Comment Submittal Information

The proposed 2014 Ambient Air Monitoring Network Plan is posted on the NDEP website for 

review and comment for thirty (30) days.

Comments may be emailed to

Daren Winkelman (dwinkelman@ndep.nv.gov)

or mailed to,

Daren Winkelman

Ambient Monitoring Program

Bureau of Air Quality Planning

901 S. Stewart Street, Suite 4001

Carson City, Nevada 89701