Annual Report

North Dakota 

Ambient Monitoring

Network Plan

2008
ii

Annual Report

North Dakota

Ambient Monitoring

Network Plan

2008

June 2008

John Hoeven

Governor

Terry L. Dwelle, M.D.

State Health Officer

L. David Glatt

Environmental Health Section Chief

North Dakota Department of Health

Division of Air Quality

Air Quality Monitoring Branch

918 E. Divide Ave.

Bismarck, N.D. 58501-1947
iii

TABLE OF CONTENTS

Page

LIST OF TABLES.............................................................. iv

LIST OF FIGURES .............................................................. v

1.0 INTRODUCTION ........................................................1

1.1 Network Plan Process ...................................................2

1.2 General Monitoring Needs ................................................3

1.3 Monitoring Objectives ...................................................4

2.0 Ambient Air Monitoring Network Coverage .......................................6

2.1 Sulfur Dioxide ........................................................6

2.1.1 Point Sources ......................................................6

2.1.2 Other Sources......................................................6

2.1.3 Monitoring Network .................................................8

2.1.4 Network Analysis ...................................................8

2.2 Oxides of Nitrogen .................................................... 15

2.2.1 Point Sources ..................................................... 15

2.2.2 Area Sources ..................................................... 15

2.2.3 Monitoring Network ................................................ 15

2.2.4 Network Analysis .................................................. 18

2.3 Ozone............................................................. 20

2.3.1 Point Sources ..................................................... 20

2.3.2 Area Sources ..................................................... 20

2.3.3 Monitoring Network ................................................ 20

2.3.4 Network Analysis .................................................. 22

2.4 Inhalable Particulates................................................... 24

2.4.1 Sources......................................................... 24

2.4.2 Monitoring Network ................................................ 24

2.4.3 PM10 Network Analysis .............................................. 27

2.4.4 PMfine Network.................................................... 28

2.4.5 Speciation Network................................................. 28

2.5 Carbon Monoxide ..................................................... 29

2.5.1 Sources......................................................... 29

2.5.2 Monitoring Network ................................................ 29

2.6 Lead.............................................................. 31

2.7 Hydrogen Sulfide ..................................................... 31

2.7.1 Sources......................................................... 31

2.7.2 Monitoring Network ................................................ 31

2.8 Air Toxics .......................................................... 31

2.8.1 Sources......................................................... 31

2.8.2 Monitoring Network ................................................ 32

3.0 SUMMARY AND CONCLUSIONS ........................................... 33

3.1 Sulfur Dioxide (SO2) ................................................... 33

3.2 Nitrogen Dioxide (NO2) ................................................. 33

3.3 Ozone (O3) ......................................................... 33

3.4 Inhalable Particulates................................................... 34

3.5 Carbon Monoxide (CO) ................................................. 34

3.6 Lead.............................................................. 34

3.7 Hydrogen Sulfide ..................................................... 34

3.8 Air Toxics .......................................................... 34

Appendix A AAQM Site Descriptions .................................................... 36

Appendix B Detailed Site Descriptions.................................................... 58

Appendix C Detailed Monitor Descriptions ................................................ 67

Appendix D Public Comments ......................................................... 109
iv

LIST OF TABLES

Table Page

Table 1 AAQM Network Description................................................................................ 5

Table 2 Major SO2 Sources................................................................................................ 7

Table 3 Sulfur Dioxide......................................................................................................10

Table 3A Trace Level Sulfur Dioxide .................................................................................10

Table 4 SO2 5-Minute Average.........................................................................................11

Table 4A Trace Level SO2 5-Minute Average....................................................................11

Table 5 Major NOx Sources .............................................................................................16

Table 6 Nitrogen Dioxide .................................................................................................18

Table 7 Major VOC Sources.............................................................................................21

Table 8 Ozone ...................................................................................................................22

Table 9 Major PM10 Sources.............................................................................................25

Table 10 FRM PMfine Particulates ......................................................................................26

Table 11 Continuous PM10..................................................................................................27

Table 12 Continuous PMfine ................................................................................................27

Table 13 Major CO Sources................................................................................................30

Table 14 Major Air Toxics Sources....................................................................................32
v

LIST OF FIGURES 

Figure Page

Figure 1 North Dakota Ambient Air Quality Monitoring Sites ........................................ 5

Figure 2 Major Sulfur Dioxide Sources............................................................................ 7

Figure 2A Annual Sulfur Dioxide Emissions ...................................................................... 8

Figure 3 Percentage of Time SO2 Detectable.................................................................. 13

Figure 4 SO2 Maximum 1-Hour Concentrations............................................................. 13

Figure 5 SO2 Maximum 3-Hour Concentrations............................................................. 14

Figure 6 SO2 Maximum 24-Hour Concentrations........................................................... 14

Figure 7 Major Oxides of Nitrogen Sources................................................................... 17

Figure 7A Annual Oxides of Nitrogen Emissions ............................................................. 17

Figure 8 Percentage of Time NO2 Detectable ................................................................. 19

Figure 9 NO2 Annual Average Concentrations............................................................... 19

Figure 10 Major VOC Sources.......................................................................................... 21

Figure 11 Monthly 4th Highest Ozone Concentrations...................................................... 23

Figure 12 Annual 4th Highest Ozone Concentrations........................................................ 23

Figure 13 Major PM10 Sources.......................................................................................... 25

Figure 13A Annual PM Emissions....................................................................................... 26

Figure 14 Major CO Sources............................................................................................. 30

Figure 15 Major Air Toxics Sources................................................................................. 32
1

1.0 INTRODUCTION

The North Dakota Department of Health, Division of Air Quality, has the primary responsibility of 

protecting the health and welfare of North Dakotans from the detrimental effects of air pollution. 

Toward that end, the Division of Air Quality ensures the ambient air quality in North Dakota is 

maintained in accordance with the levels established by the state and federal Ambient Air Quality 

Standards (AAQS) and the Prevention of Significant Deterioration of Air Quality (PSD) Rules. To 

carry out this responsibility, the Division of Air Quality operates and maintains a network of 

ambient air quality monitors and requires three major industrial pollution sources to conduct sourcespecific ambient air quality monitoring. There are 16 ambient air quality monitoring sites currently 

operating in the State. However, this review addresses only the seven department-operated sites. 

The Theodore Roosevelt National Park – South Unit site at Painted Canyon is a National Park 

Service site. The department operates and maintains the sulfur dioxide, ozone and continuous fine 

particulate analyzers at the National Park Service’s request. The remaining eight sites are 

department-required industry-supported sites

To evaluate the effectiveness of the state's air quality monitoring effort, the U.S. Environmental 

Protection Agency (EPA) requires the Division of Air Quality to conduct an annual review of the 

department’s ambient air quality monitoring (AAQM) network. EPA's requirements, as set forth in 

40 CFR 58.10, are to (1) determine if the system meets the monitoring objectives defined in 40 CFR 

58, Appendix D, and (2) identify network modifications such as termination or relocation of 

unnecessary sites or establishment of new sites that are necessary.

The 2005 Draft National Ambient Air Monitoring Strategy (NAAMS, 

www.epa.gov/ttn/amtic/monstratdoc.html ) established a new monitoring site classification system 

for the national AAQM network structure. There are two primary categories: National Core (NCore) 

and State, Local, and Tribal (SLT). The NCore sites are separated into three distinct monitoring 

equipment requirements defined as Level 1, Level 2, and Level 3. NCore levels 1 and 2 are multipollutant sites. NCore Level 3 sites are single pollutant sites. Each state is required to have at least 

one NCore Level 2 site. Fargo NW has been selected as North Dakota’s required NCore Level 2 

site. Fargo NW is also a part of EPA’s 54-site Speciation Trends National Network. The NAAMS 

explains the purpose of these national networks and rationale for each gaseous and particulate 

measurement.

For the States and tribes, the State and Local Monitoring Systems (SLAMS), SPM, Prevention of 

Significant Deterioration (PSD) and Tribal Networks site designations still apply. The remaining six 

department-operated sites are designated as SLAMS sites.
2

1.1 Network Plan Process 

The locations of sites in a monitoring program are established to meet certain objectives. The 

Oc. 17, 2006, Federal Register (40 CFR 58, Appendix D), defined six basic monitoring 

objectives. These objectives are as follows:

1. To determine the highest pollutant concentrations expected to occur in an area covered by 

the network.

2. To determine representative concentrations in areas of high population density.

3. To determine the impact on ambient pollution levels by a significant source or class 

categories.

4. To determine the general/background concentration levels.

5. To determine the impact on air quality by regional transport.

6. To determine welfare-related impacts (such as visibility impacts and vegetation effects).

The link between basic monitoring objectives and the physical location of a particular 

monitoring site involves the concept of spatial scale of representativeness. This spatial scale is 

determined by the physical dimensions of the air parcel nearest a monitoring site throughout 

which actual pollutant concentrations are reasonably similar. The goal in locating sites is to 

match the spatial scale represented by the sample of monitored air with a spatial scale most 

appropriate for the monitoring objective. Spatial scales of representativeness, as specified by 

EPA, are described as follows:

Microscale – dimensions ranging from several meters up to about 100 meters.

Middle Scale – areas up to several city blocks in size with dimensions ranging from about 100 

meters to 0.5 km.

Neighborhood Scale – city areas of relatively uniform land use with dimensions of 0.5 to 4.0 

km.

Urban Scale – overall, city-wide dimensions on the order of 4 to 50 km. (Usually requires more 

than one site for definition.)

Regional Scale – rural areas of reasonably homogeneous geography covering from 50 km to 

hundreds of km.
3

The relationships between monitoring objectives and spatial scales of representativeness, as 

specified by EPA, are as follows:

Monitoring Objective Appropriate Siting Scales

Highest Concentration Micro, middle, neighborhood, (sometimes urban or regional

 for secondarily formed pollutants) 

Population Oriented Neighborhood, urban

Source Impact Micro, middle, neighborhood

General/Background Urban, regional

Regional Transport Urban, regional

Welfare-related Impacts Urban, regional

Recommended scales of representativeness appropriate to the criteria pollutants monitored in 

North Dakota are shown below:

Criteria Pollutant Spatial Scales

Inhalable Particulate micro, middle, neighborhood, urban, regional

Sulfur Dioxide middle, neighborhood, urban, regional

Ozone middle, neighborhood, urban, regional

Nitrogen Dioxide middle, neighborhood, urban

Using this physical basis to locate sites allows for an objective approach, ensures compatibility 

among sites, and provides a common basis for data interpretation and application. The annual 

review process involves reviewing each site and associated monitors to evaluate their 

monitoring objectives and spatial scales to ensure each site and monitor still meets the intended 

purpose. Sites and monitors that no longer satisfy the intended purpose are either terminated or 

modified accordingly. Further details on network design can be found in 40 CFR 58, Appendix

D.

1.2 General Monitoring Needs 

As can be gathered from the prior discussion, each air pollutant has certain characteristics that

must be considered when establishing a monitoring site. These characteristics may result from 

(1) variations in the number and types of sources and emissions in question; (2) reactivity of a 

particular pollutant with other constituents in the air; (3) local site influences such as terrain 

and land use; and (4) climatology. The Department’s AAQM network is designed to monitor 

air quality data for five basic conditions: (1) background monitoring; (2) population exposure; 

(3) significant source or class category; (4) long range transport; and (5) regional haze.

There are a total of 16 ambient air quality monitoring sites operating in the state: eight are 

source-specific industry sites and one site, Painted Canyon in Theodore Roosevelt National 

Park, is a part of the National Park Service’s (NPS) network. The department, at the NPS’s 

request, provides sulfur dioxide and ozone analyzers and a manual fine particulate (PMfine) 

sampler. The NPS also provides a continuous PMfine analyzer, which the department operates 
4

and maintains. The remaining seven sites fall into two categories: 40 CFR 58 required sites (3) 

and supplemental sites (4). The primary function of the department’s three required sites (see 

Table 1) are to satisfy five monitoring objectives. Beulah is a significant source and populationoriented site because of the three major sources in the vicinity of Beulah. Also, the site is 

between the city and downwind of two major sources. Fargo NW is population orientated 

because Fargo is a major population center with five major sources in the Fargo, ND-Moorhead, 

MN, area. The data from this site is used as input to dispersion models to evaluate permits-toconstruct and permits-to-operate for projects located in or near population centers in the eastern 

part of the state. And, TRNP-NU is the background/long-range transport/welfare-related site. 

The remaining four sites are used to support modeling activities (model calibration and/or 

validation) and supplement data collected at the required sites. For the national PMfine program, 

the department is required to operate three “non-Core required” sites (Fargo, Bismarck and 

Beulah).

Background, welfare-related and long-range transport sites are chosen to determine concentrations of air contaminants in areas remote from urban sources and generally are sited using the 

regional spatial scale. This is true for NO2 despite the fact that the regional spatial scale is not 

normally used for NO2 monitoring. Once a specific location is selected for a site, the site is 

established in accordance with the specific sitting criteria specified in 40 CFR 58, Appendices 

A, C, D and E.

1.3 Monitoring Objectives 

The department’s monitoring objective is to track those pollutants that are judged to have the 

potential for violating either state or federal Ambient Air Quality Standards. To accomplish this 

objective, the department operates SLAMS sites at selected locations around the state. Table 1 

lists basic site information: Appendix A contains a full description for each site, site 

photographs, and a site map taken from Google EarthTM mapping service. Figure 1 shows the 

approximate site locations.

With the visibility regulations in 40 CFR 51.300, 40 CFR 51.308 (regional haze rules) and 40 

CFR 51, Appendix Y (Best Available Retrofit Technology, BART) coming into effect, the 

department is beginning to evaluate monitoring requirements and changes needed to support the 

visibility regulations.
5

Table 1

AAQM Network Description 

Site Name

 AQS Site #

Parameter

Monitored1

Monitoring

Objective2

 1 Beulah North

 380570004

SO2, NO2, O3, NH3, MET

cont. PMfine, PM10

Manual PMfine

Population Exposure

&

Significant Source

2 Bismarck Residential

 380150003

SO2, NO2, O3, MET

cont. PMfine, PM10

Manual PMfine

Population Exposure

3 Dunn Center

 380250003

SO2

4

, NO2, O3, MET

cont. PMfine, cont. PM10

General Background

4 Fargo NW

 380171004

SO2, NO2, O3, MET

cont. PMfine, PM10

Manual PMfine

PMfine Speciation

Population Exposure

Population Exposure

Population Exposure

Population Exposure

5 Hannover

 380650002

SO2, NO2, O3, MET

cont. PMfine

Source Impact

6 Lostwood NWR

 380130004

SO2

4

, NO2, O3, MET,

cont. PMfine, cont. PM10

PMfine Speciation (IMPROVE)

General Background

&

Significant Source

7 TRNP - NU

 380530002

SO2

4

, NO2, O3, MET

cont. PMfine, PM10

General Background, Long range Transport,

& 

Welfare-related

1. MET refers to meteorological and indicates wind speed and wind direction monitoring equipment.

2. Not applicable to MET.

3. This analyzer will serve a dual role of population exposure and general background.

4. The SO2 was replaced with a SO2 Trace Level Analyzer.

Figure 1 North Dakota Ambient Air Quality Monitoring Sites 
6

2.0 Ambient Air Monitoring Network Coverage

The State of North Dakota is in attainment for all ambient standards for criteria pollutants, 

including PMfine and 8-hour ozone. The seven department-operated ambient monitoring sites 

are positioned to satisfy five monitoring objectives and collect data to compare to the State 

and federal ambient air quality standards and support dispersion modeling activities relating 

to, first, visibility/regional haze, and, second, source permit evaluation.

2.1 Sulfur Dioxide 

Energy development in the west and west-central portions of North Dakota has produced a 

number of sources of sulfur dioxide (SO2). These sources include coal-fired steam-powered 

electrical generating facilities, a coal gasification plant, natural gas processing plants, an oil 

refinery, and flaring at oil/gas well sites. As a result, SO2 is one of the Department's primary 

interests in regard to visibility: first, to aid in establishing the visibility baseline, then to track 

visibility improvement over time.

2.1.1 Point Sources 

The major SO2 point sources (>100 Tons Per Year or TPY) based on 2007 emissions are 

listed in Table 2. Figure 2 shows the approximate locations of these facilities (the numbers 

correspond to the site and source tables). Figure 2A shows the total annual SO2 emissions 

from point sources and three sub-categories for 1984 through 2007.

2.1.2 Other Sources 

The western part of the state has a number of potential SO2 sources associated with the 

development of oil and gas. These sources include individual oil/gas wells, oil storage 

facilities, and compressor stations. Emissions from these sources may lead to two problems. 

First, these sources may directly emit significant amounts of hydrogen sulfide (H2S) to the 

ambient air (see Section 2.7). Second, flaring the H2S from these sources may create 

significant concentrations of SO2 in the ambient air. The primary counties for these sources 

in western North Dakota are outlined in green on Figure 2. Figure 2A shows the 

contribution of an “Other Point Sources” category that consists of Dakota Gasification 

Company (DGC), oil refineries, natural gas processing plants, and agricultural processing 

plants.
7

Table 2

Major SO2 Sources

(>100 TPY)

# Company Name SOURCE Facility ID

1 Basin Electric Power Cooperative Leland Olds Station 3805700001

2 Great River Energy Coal Creek Station 3805500017

3 Minnkota Power Cooperative, Inc. Milton R. Young Station 3806500001

4 Basin Electric Power Cooperative Antelope Valley Station 3805700011

5 Otter Tail Power Company Coyote Station 3805700012

6 Dakota Gasification Company Great Plains Synfuels Facility 3805700013

7 Montana Dakota Utilities Company RM Heskett Station 3805900001

8 Great River Energy Stanton Station 3805700004

9 Hess Corporation Tioga Gas Plant 3810500004

10 American Crystal Sugar Company Hillsboro Plant 3809700019

11 Bear Paw Energy, L.L.C. Grasslands Gas Plant 3805300023

12 Tesoro Refining and Marketing Company Mandan Refinery 3805900003

13 University of North Dakota UND Heating Plant 3803500003

14 Petro-Hunt, LLC Little Knife Gas Plant 3800700002

15 North Dakota State University NDSU Heating Plant 3801700005

16 American Crystal Sugar Company Drayton Plant 3806700003

17 Minn-Dak Farmers Cooperative Wahpeton Plant 3807700026

18 ADM Corn Processing Walhalla Ethanol Plant 3806700004

19 Hebron Brick Company Hebron Facility 3805900017

20 Bear Paw Energy, L.L.C. Lignite Gas Plant 3801300071

Figure 2 Major Sulfur Dioxide Sources 
8

2.1.3 Monitoring Network 

The SO2 monitoring sites are shown on Figure 2. The most significant change to the 

network in 2007 is that trace level analyzers were installed at Dunn Center, TRNP – NU, 

and Lostwood. The difference between a standard SO2 analyzer and the trace level analyzer 

is the Minimum Detectable Value (MDV). The standard analyzer MDV is 2 parts per 

billion (ppb) and the trace level MDV is 0.2 ppb. These analyzers were operational for the 

second half of 2007.

As can be seen in Figure 2, the monitoring sites are concentrated in the vicinity of the oil 

and gas development in the west and the coal-fired steam electrical generating plants in the 

west-central part of the state. Tables 3 and 3A show the 2007 annual SO2 data summaries; 

Tables 4 and 4A show the 5-minute data summaries. There were no exceedances of either 

state or federal SO2 standards.

2.1.4 Network Analysis 

Ten major SO2 sources are within 45 miles of both the Beulah and Hannover sites. This 

makes these two sites very important in tracking the impact of these sources on the ambient 

air. Also, Lostwood NWR is within 45 miles of four major sources: two natural gas 

processing plants and two power plants. The two natural gas processing plants are the 

Figure 2A Annual Sulfur Dioxide Emissions 

0

50000

100000

150000

200000

250000

300000

1984 1986 1988 1990 1992 1994 1996 1998 2000 2002 2004 2006 SO2 (TONS)

NORTH DAKOTA

SO2 EMISSIONS

TOTAL OIL & GAS OTHER PT. SOURCES UTILITY BOILERS
9

Lignite Gas Plant and Tioga Gas Plant. The two power plants, Shand Power Station and 

Boundary Dam Power Station, are located near Estevan, Saskatchewan, approximately 40 

miles to the northwest.

One would expect that as the large sources in Oliver and Mercer counties came on line 

beginning in 1980, a noticeable change would be seen on the ambient air quality. This has 

not been the case. There have been possible short-term influences, but no significant longterm impact by these sources combined has been demonstrated in the data. Figures 3, 4, 5 

and 6 present the following for the Department-operated sites: (1) the percentage of data 

greater than the MDV; (2) 1-hour maximums; (3) 3-hour maximums; and (4) 24-hour 

maximums. Because the industry sites are sited specifically for maximum expected 

concentrations (primarily as predicted by dispersion models and secondarily in a downwind 

direction), the industry sites are not reviewed for particular long-term trends.

The best-long term indicator of any change in the amount of SO2 in the ambient air is seen 

by reviewing the percentages of hourly data points greater than the MDV. Figure 3 presents 

this data for the current active department sites from 1980 through 2007. To calculate valid 

statistics, at least 75 percent of the data for each averaging period must be valid. The result 

of the 75 percent requirement is that each 1-hour average must have at least 45 valid 

minutes of data. The 3-hour average must have three valid values. The 24-hour average 

must have at least 18 valid hourly averages. And, the annual average must have 6,570 hours 

of data. For each aggregate statistic (3-hour, 24-hour, and annual), each hourly value used 

that is less than then MDV, one-half the MDV is substituted. For the standard analyzer, 1 

ppb is substituted and 0.1 ppb for the trace level analyzer.
10

TABLE 3 

 

 COMPARISON OF AIR QUALITY DATA WITH

 THE NORTH DAKOTA AMBIENT AIR QUALITY STANDARDS *

POLLUTANT : SULFUR DIOXIDE (ppb)

 M A X I M A

 SAMPLING NUM 1 - HOUR 3 - HOUR 24 - HOUR ARITH 1HR 24HR %

 LOCATION YEAR PERIOD OBS 1ST 2ND 1ST 2ND 1ST 2ND MEAN #>273 #>99 >MDV

 │ │ │ │

Beulah - North 2007 JAN-DEC 8675│ 54 51 │ 35 30 │ 8 7 │ 1.6 16.5

 │ │ │ │

Bismarck Residential 2007 JAN-DEC 8684│ 40 39 │ 31 26 │ 10 8 │ 1.8 19.4

 │ │ │ │

Dunn Center 2007 JAN-JUN 4220│ 22 10 │ 10 8 │ 2 2 │ 1.1 5.9

 │ │ │ │

Hannover 2007 JAN-DEC 8692│ 81 69 │ 60 47 │ 12 11 │ 1.8 15.4

 │ │ │ │

Lostwood NWR 2007 JAN-JUN 4229│ 81 50 │ 33 30 │ 15 10 │ 1.9 18.4

 │ │ │ │

TRNP - NU 2007 JAN-JUN 4241│ 12 11 │ 8 6 │ 4 2 │ 1.1 4.5

 │ │ │ │

* The air quality standards are:

STATE Standards -

 1) 273 ppb maximum 1-hour average concentration.

 2) 99 ppb maximum 24-hour average concentration.

 3) 23 ppb maximum annual arithmetic mean concentration.

 FEDERAL Standards -

 1) 500 ppb maximum 3-hour concentration not to be exceeded more than once per year.

 2) 140 ppb maximum 24-hour concentration not to be exceeded more than once per year.

 3) 30 ppb annual arithmetic mean.

TABLE 3A

 COMPARISON OF AIR QUALITY DATA WITH

 THE NORTH DAKOTA AMBIENT AIR QUALITY STANDARDS *

POLLUTANT : TRACE LEVEL SULFUR DIOXIDE (ppb)

 M A X I M A

 SAMPLING NUM 1 - HOUR 3 - HOUR 24 - HOUR ARITH 1HR 24HR %

 LOCATION YEAR PERIOD OBS 1ST 2ND 1ST 2ND 1ST 2ND MEAN #>273 #>99 >MDV

 │ │ │ │

 │ │ │ │

Dunn Center 2007 JUN-DEC 4456│ 23.4 20.6 │ 18.1 6.6 │ 3.3 2.2 │ 0.4 46.5

 │ │ │ │

Fargo NW 2007 JAN-DEC 8650│ 10.2 8.8 │ 8.0 6.8 │ 3.2 2.2 │ 0.3 48.9

 │ │ │ │

Lostwood NWR 2007 JUN-DEC 4475│ 32.4 29.1 │ 23.6 17.1 │ 8.0 6.4 │ 0.9 64.5

 │ │ │ │

TRNP - NU 2007 JUN-DEC 4473│ 19.0 15.9 │ 12.0 10.2 │ 2.7 2.3 │ 0.5 63.6

* The air quality standards are:

 STATE Standards -

 1) 273 ppb maximum 1-hour average concentration.

 2) 99 ppb maximum 24-hour average concentration.

 3) 23 ppb maximum annual arithmetic mean concentration.

 FEDERAL Standards -

 1) 500 ppb maximum 3-hour concentration not to be exceeded more than once per year.

 2) 140 ppb maximum 24-hour concentration not to be exceeded more than once per year.

 3) 30 ppb annual arithmetic mean.
11

TABLE 4

 COMPARISON OF AIR QUALITY DATA WITH

 THE NORTH DAKOTA AMBIENT AIR QUALITY STANDARDS *

POLLUTANT : SO2 5-Minute Averages (ppb)

 5 - M I N U T E M A X I M A

 SAMPLING NUM # HOURS %

 LOCATION YEAR PERIOD OBS 1ST 2ND 3RD >600 >MDV

 │ │ │ │

Beulah - North 2007 JAN-DEC 8675│ 79 │ 73 │ 72 │ 0 26.7

 │ │ │ │

Bismarck Residential 2007 JAN-DEC 8640│ 80 │ 62 │ 59 │ 0 30.9

 │ │ │ │

Dunn Center 2007 JAN-JUN 4220│ 48 │ 23 │ 17 │ 0 14.1

 │ │ │ │

Hannover 2007 JAN-DEC 8689│ 155 │ 155 │ 137 │ 0 23.9

 │ │ │ │

Lostwood NWR 2007 JAN-JUN 4229│ 108 │ 90 │ 65 │ 0 24.9

 │ │ │ │

TRNP - NU 2007 JAN-JUN 4241│ 18 │ 17 │ 16 │ 0 11.7

 │ │ │ │

* No Standard is currently in effect

TABLE 4A

 COMPARISON OF AIR QUALITY DATA WITH

 THE NORTH DAKOTA AMBIENT AIR QUALITY STANDARDS *

POLLUTANT : Trace Level SO2 5-Minute Averages (ppb)

 5 - M I N U T E M A X I M A

 SAMPLING NUM # HOURS %

 LOCATION YEAR PERIOD OBS 1ST 2ND 3RD >600 >MDV

 │ │ │ │

Dunn Center 2007 JUN-DEC 4456│ 40.8 │ 32.4 │ 26.6 │ 0 64.7

 │ │ │ │

Fargo NW 2007 JAN-DEC 8654│ 20.2 │ 17.7 │ 16.8 │ 0 70.2

 │ │ │ │

Lostwood NWR 2007 JUN-DEC 4475│ 46.0 │ 44.7 │ 39.3 │ 0 66.2

 │ │ │ │

TRNP - NU 2007 JUN-DEC 4464│ 29.9 │ 25.8 │ 17.2 │ 0 77.6

* No Standard is currently in effect:

Beginning in 1980, major events are traceable. In 1980, the oil industry was expanding. In 1981, 

Otter Tail Power’s Coyote Power Station began operation. In 1982 the oil industry in western North 

Dakota hit its peak activity. Dunn Center and TRNP – NU show the influence from the oil field 

activity as the oil fields expanded and flared the gas. As pipelines were built and wells were tied into 

the pipelines, the amount of hydrogen sulfide gas flared decreased, reducing the amount of sulfur 

dioxide emitted. Once the wells were tied into pipelines, the predominant influence at these two sites 

has been long-range transport from major point sources.

Dunn Center and TRNP – NU were indicators of the “oil patch” activity and tracked the activity very 

well. Since TRNP – NU is more centrally located in the “oil patch,” it is the stronger indicator. Dunn 

Center, which is on the eastern edge of the oil development area, demonstrates influences from both 

the “oil patch” and the coal conversion facilities to the east.
12

1983, 1984 and 1985 were startup years for Basin Electric’s Antelope Valley Unit #1, the synthetic 

natural gas plant (aka, Dakota Gasification Company, DGC), and Antelope Valley Unit #2, 

respectively. At Hannover, 1985 and 1986 reflected these startups (1984 had only three months of 

data and shut down Dec. 31, 1986). Hannover was started up again Jan. 1, 1988, and from 1988

through 1993, there was a steady increasing trend in the percentage of data greater than the MDV; 

then, the percentage decreased from 1993 to 2007. The Beulah - North site began operation in 1999 

and has tracked the Hannover data.

The remaining sites – Bismarck, Lostwood NWR and Fargo – do not have enough long-term data to 

assign possible trends. It is interesting to note that the percentages for sites near major sources tend to 

group together and those distant from major sources are grouped together (see Figure 3).

The similar patterns seen in Figure 3 are discernable in the 1-hour, 3-hour, and 24-hour maximum 

concentration graphs (see Figures 4, 5 and 6, respectively).
13

Figure 3 Percentage of Time SO2 Detectable 

Figure 4 SO2 Maximum 1-Hour Concentrations 
14

Figure 5 SO2 Maximum 3-Hour Concentrations 

Figure 6 SO2 Maximum 24-Hour Concentrations 
15

2.2 Oxides of Nitrogen 

“Oxides of Nitrogen” (NOx) is the term used to represent nitric oxide (NO) plus nitrogen 

dioxide (NO2). NO2 is formed when NO is oxidized in the ambient air. There is no ambient air 

quality standard for NO.

2.2.1 Point Sources 

The major NOx stationary point sources (>100 TPY) are listed in Table 5, along with their 

emissions as calculated from the most recent emission inventories reported to the department. 

Figure 7 shows the approximate locations of these facilities (the numbers correspond to the 

site and source tables). The larger NOx point sources in North Dakota are associated with 

coal-fired steam-powered electrical generating plants in the west-central portion of the state 

and large internal combustion compressor engines in the natural gas fields in the western part 

of the state. Figure 7A shows the contribution of point sources to the total NOX emissions. 

The “Point Sources” category consists of utility boilers (power plant boilers) and oil and gas 

wells.

2.2.2 Area Sources 

Another source of NOX is automobile emissions. North Dakota has no significant urbanized 

areas with regard to oxides of nitrogen; the entire population of the state is less than 

1,000,000 people. However, currently operating NO analyzers cannot be terminated without 

EPA Region 8 administrator permission. Figure 7A shows the contribution of “Other Point 

Sources” and “Utility Boilers.” The “Other Point Sources” category consists of DGC, oil 

refineries, natural gas processing plants and agricultural processing plants.

2.2.3 Monitoring Network 

The Department currently operates seven NO/NO2/NOx analyzers. Table 6 shows the 2007

NO2 data summaries. The measured NO2 values are quite low. From Figure 7 it can be 

seen that NO/NO2/NOx analyzers, except for Dunn Center and TRNP - NU, are well placed 

with respect to the major NOx sources: TRNP - NU is defined as a background and longrange transport/welfare-related site.
16

TABLE 5

Major NOx Sources

(> 100 TPY)

# COMPANY SOURCE Facility ID

1 Minnkota Power Cooperative, Inc. Milton R. Young Station 3806500001

2 Basin Electric Power Cooperative Antelope Valley Station 3805700011

3 Great River Energy GRE Coal Creek Station 3805500017

4 Otter Tail Power Company Coyote Station 3805700012

5 Basin Electric Power Cooperative Leland Olds Station 3805700001

6 Dakota Gasification Company Great Plains Synfuels Facility 3805700013

7 Great River Energy GRE Stanton Station 3805700004

8 Hess Corporation Tioga Gas Plant 3810500004

9 Montana Dakota Utilities Company RM Heskett Station 3805900001

10 Tesoro Refining and Marketing Company Mandan Refinery 3805900003

11 American Crystal Sugar Company Hillsboro Plant 3809700019

12 American Crystal Sugar Company Drayton Plant 3806700003

13 Minn-Dak Farmers Cooperative Wahpeton Plant 3807700026

14 Bear Paw Energy, L.L.C. Alexander Station 3805300024

15 University of North Dakota UND Heating Plant 3803500003

16 Bear Paw Energy, L.L.C. Cow Creek Station 3810500077

17 North Dakota State University NDSU Heating Plant 3801700005

18 TransCanada Northern Border, Inc. Compressor #4 3805300014

19 ADM Corn Processing Walhalla Ethanol Plant 3806700004

20 Northern Sun (Division of ADM) Enderlin Facility 3807300001

21 Bear Paw Energy, L.L.C. Tree Top Station 3800700019
17

Figure 7A Annual Oxides of Nitrogen Emissions 

Figure 7 Major Oxides of Nitrogen Sources 

 Major NOX Sources

 Monitoring Sites

 Class 1 Areas

0 7 M AY0 7 1 3 :5 6
18

TABLE 6

 COMPARISON OF AIR QUALITY DATA WITH

 THE NORTH DAKOTA AMBIENT AIR QUALITY STANDARDS *

POLLUTANT : NITROGEN DIOXIDE (ppb)

 M A X I M A

 SAMPLING NUM 1 - HOUR ARITH %

 LOCATION YEAR PERIOD OBS 1ST 2ND MEAN >MDV

 │ │

│ │

Beulah - North 2007 JAN-DEC 8324│ 31 30 │ 2.6 87.3

 │ │

Bismarck Residential 2007 JAN-DEC 8628│ 44 43 │ 6.2 99.4

 │ │

Dunn Center 2007 JAN-DEC 8422│ 26 19 │ 1.5 71.6

 │ │

Fargo NW 2007 JAN-DEC 8643│ 40 40 │ 5.0 90.4

 │ │

Hannover 2007 JAN-DEC 8662│ 37 34 │ 1.9 78.8

 │ │

Lostwood NWR 2007 JAN-DEC 7916│ 26 20 │ 1.5 65.6

 │ │

TRNP - NU 2007 JAN-DEC 8694│ 11 10 │ 0.8 32.1

*The air quality standards are:

STATE - 53 ppb maximum annual arithmetic mean.

FEDERAL - 53 ppb annual arithmetic mean.

2.2.4 Network Analysis 

Nine of the 10 largest NOX sources in the state are within 45 miles of the Beulah and 

Hannover monitoring sites. Figures 8 and 9 show the trends for the department-operated 

sites for 1980 - 2007.

The percentage of data greater than 1 part per billion is shown in Figure 8, and the annual 

averages in Figure 9. The state and federal annual standard is 53 ppb. However, the annual 

averages are at most 16 percent of the standard; therefore, a more appropriate scale was 

chosen to better show the data. Beginning in 1998, when the percentage of data greater than 

1 ppb exceeded 75 percent, it is easy to see that the annual NO2 averages follow the reported 

NOX emissions shown in Figure 7A.
19

Figure 8 Percentage of Time NO2 Detectable 

Figure 9 NO2 Annual Average Concentrations 
20

2.3 Ozone 

Unlike most other pollutants, ozone (O3) is not emitted directly into the atmosphere but results 

from a complex photochemical reaction between volatile organic compounds (VOC), oxides of 

nitrogen (NOx), and solar radiation. Both VOC and NOx are emitted directly into the 

atmosphere. Since solar radiation is a major factor in O3 production, O3 concentrations are 

known to peak in summer months. 40 CFR 58 defines the O3 monitoring season for North 

Dakota as May 1 through September 30. However, O3 analyzers at all the sites run year round,

collecting data for use in dispersion modeling.

2.3.1 Point Sources 

The major stationary point sources (> 100 TPY) of VOC as calculated from the most recent 

emission inventories reported to the department are listed in Table 7. Figure 10 shows the 

approximate locations of these facilities.

2.3.2 Area Sources 

Point sources contribute only part of the total VOC and NOx emissions. The remaining 

emissions can be attributed to oilfield-related activities and mobile sources in urban areas. 

The EPA has specified design criteria for selecting locations for O3 as any urbanized area 

having a population of 50,000 to less than 350,000. North Dakota has three urbanized areas 

(Bismarck; Fargo, ND-Moorhead, MN; and Grand Forks) populated enough to qualify for 

population-oriented monitoring. However, to require monitoring, the 4th highest 8-hour 

average concentration must be at least 68 parts per billion.

2.3.3 Monitoring Network 

The department currently has seven continuous ozone analyzers in operation. See Table 1 

and Figure 10 for locations. Table 8 presents the 2007 8-hour data summaries.
21

TABLE 7

Major VOC Sources

(> 100 TPY)

# Company Source Facility ID

1 Tesoro Refining and Marketing Company Mandan Refinery 3805900003

2 Dakota Gasification Company Great Plains Synfuels Facility 3805700013

3 Northern Sun (Division of ADM) Enderlin Facility 3807300001

4 Minnkota Power Cooperative, Inc. Milton R. Young Station 3806500001

5 ADM Processing Velva Facility 3804900005

6 Basin Electric Power Cooperative Antelope Valley Station 3805700011

7 Minn-Dak Farmers Cooperative Wahpeton Plant 3807700026

8 DMI Industries DMI Industries 3801700122

9 Great River Energy Coal Creek Station 3805500017

10 Kaneb Pipe Line Operating Partnership, L.P. Jamestown East Products Terminal 3809300037

11 Basin Electric Power Cooperative Leland Olds Station 3805700001

12 ADM Corn Processing Walhalla Ethanol Plant 3806700004

13 Hood Packaging Corporation Hood Packaging Corporation 3803500052

14 Plains Marketing, LP Fryburg Station 3800700038

Figure 10 Major VOC Sources 
22

TABLE 8

 COMPARISON OF AIR QUALITY DATA WITH

 THE NORTH DAKOTA AMBIENT AIR QUALITY STANDARDS *

POLLUTANT : Ozone (ppb)

 M A X I M A

 SAMPLING NUM 1 - HOUR 8 - HOUR 1HR 8HR

 LOCATION YEAR PERIOD OBS 1ST 2ND 1ST 2ND 3RD 4

TH #>120 #>80

 │ │ │

Beulah - North 2007 JAN-DEC 8355│ 68 66 │ 62 61 60 59 │ 

 │ │ │

Bismarck Residential 2007 JAN-DEC 8622│ 70 67 │ 62 62 60 58 │ 

 │ │ │

Dunn Center 2007 JAN-DEC 8282│ 67 67 │ 59 59 58 58 │ 

 │ │ │

Fargo NW 2007 JAN-DEC 8274│ 65 63 │ 62 57 56 55 │ 

 │ │ │

Hannover 2007 JAN-DEC 8695│ 69 68 │ 64 60 59 59 │ 

 │ │ │

Lostwood NWR 2007 JAN-DEC 8710│ 71 67 │ 64 62 61 59 │ 

 │ │ │

TRNP - NU 2007 JAN-DEC 8719│ 76 75 │ 71 69 67 65 │ 

 │ │ │

* The air quality standards for ozone are:

 STATE - 120 ppb not to be exceeded more than once per year.

 FEDERAL Standards -

 1) 120 ppb maximum 1-hour concentration with no more than one expected exceedance per year.

 2) Fourth highest daily maximum 8-hour averages for a 3-year period not to exceed 80 ppb.

2.3.4 Network Analysis 

Only three of the seven monitoring sites are in an area not significantly influenced by VOC 

sources (see Figure 10). Beulah and Hannover are within 45 miles of six of the 14 major VOC 

sources in the state. Lostwood NWR and TRNP - NU are located in Class I areas surrounded by 

oil fields. Bismarck Residential and Fargo NW are located in population centers and influenced by 

city traffic. Dunn Center is located in a rural area surrounded by crop land. With this diversity of 

site locations and influences, one would expect to see a diversity of ozone concentrations. On the 

contrary, Figures 11 and 12 shows a significant similarity among the 4th maximum 8-hour 

concentrations whether view monthly or annually. Since 1980, only four 8-hour averages have 

been higher than 70 ppb. Another, even stronger, indication of a uniform ozone distribution is the 

8-hour concentrations: for all sites, the difference among the 4th highest average is 8 ppb (see 

Table 8).
23

25

30

35

40

45

50

55

60

65

70

75

80

85

1980 1982 1984 1986 1988 1990 1992 1994 1996 1998 2000 2002 2004 2006

Parts Per Billion

Beulah - N Dunn Center Fargo NW Hannover

TRNP-NU Lostwood Bismarck

Figure 11 Monthly 4th Highest Ozone Concentrations

Figure 12 Annual 4th Highest 8-HR Ozone Concentrations
24

2.4 Inhalable Particulates 

The inhalable particulate standards are designed to protect against those particulates that can be 

inhaled deep into the lungs and cause respiratory problems. The major designation for 

particulates is PM. Within this designation there are two subgroups: PM10 and PMfine. The PM10

particulates have an aerodynamic diameter less than or equal to a nominal 10 microns and are 

designated as PM10. The PMfine particulates have an aerodynamic diameter less than or equal to 

a nominal 2.5 microns. The EPA is working on a new PM subgroup of particles called “coarse

fraction,” or PMcoarse. This subgroup is made up of PM10 – PMfine. Specific health effects have 

been identified for both the PMcoarse and PMfine. The EPA is working with equipment 

manufacturers to develop a continuous analyzer and a manual sampler to collect and report both 

of these subgroups. As soon as a continuous analyzer is available, the department will develop a 

plan and schedule to deploy these analyzers. First, these new analyzers will be deployed at the 

Beulah, Fargo and TRNP - NU sites, and at the other four sites as the current continuous PM10

and PMfine analyzers are scheduled for replacement and funding is available.

2.4.1 Sources 

The major PM10 point sources (>100 TPY) are listed in Table 9. Figure 13 shows the 

approximate locations of these facilities (the numbers correspond to the site and source 

tables). Most of these sources are large coal-fired facilities, and the PM10 particles are part 

of the boiler stack emissions; however, some of the emissions are the result of processing 

operations. Not included in this table are sources of fugitive dust such as coal mines, gravel 

pits, agricultural fields and unpaved roads. Figure 13A shows the contribution of point 

sources to the total PM10 emissions. The “Utility Boilers” category consists of power plant 

boilers. The “Other Point Sources” category consists of DGC, oil refineries, natural gas 

processing plants and agricultural processing plants.

2.4.2 Monitoring Network 

The Department operated six continuous PM10 analyzers, three manual PMfine samplers, 

seven continuous PMfine analyzers, and one speciation sampler. Tables 11 shows the 

continuous PM10 particulate data summary. Tables 10 and 12 show the manual and 

continuous PMfine data summaries, respectively.
25

TABLE 9

Major PM10 Sources 

(> 100 TPY)

# COMPANY SOURCE Facility ID

1 Basin Electric Power Cooperative Antelope Valley Station 3805700011

2 Dakota Gasification Company Great Plains Synfuels Facility 3805700013

3 Otter Tail Power Company Coyote Station 3805700012

4 American Crystal Sugar Company Drayton Plant 3806700003

5 Basin Electric Power Cooperative Leland Olds Station 3805700001

6 American Crystal Sugar Company Hillsboro Plant 3809700019

7 American Colloid Company Reeder Leonardite Facility 3801100071

8 Great River Energy GRE Coal Creek Station 3805500017

9 Minn-Dak Farmers Cooperative Wahpeton Plant 3807700026

10 Tesoro Refining and Marketing Company Mandan Refinery 3805900003

11 Great River Energy Stanton Station 3805700004

Figure 13 Major PM10 Sources 
26

TABLE 10 

 COMPARISON OF AIR QUALITY DATA WITH

 THE NORTH DAKOTA AMBIENT AIR QUALITY STANDARDS *

POLLUTANT : FRM PMfine Particulates (g/m3)

 M A X I M A

 SAMPLING NUM ARITH %

 LOCATION YEAR PERIOD OBS MIN 1ST 2ND 3RD MEAN #>150 AM>50 >MDV

 │ │

 │ │

Beulah - North 2007 JAN-DEC 58 2.3│ 16.4 13.5 11.8│ 6.6 100.0

 │ │

Bismarck Residential 2007 JAN-DEC 120 1.8│ 17.0 16.4 13.5│ 6.8 99.2

 │ │

Fargo NW 2007 JAN-DEC 110 1.0│ 19.5 16.4 15.0│ 7.5 99.1

* The ambient air quality standards are:

 FEDERAL Standards -

 1) 24-hour: 3-year average of 98th percentiles not to exceed 35 g/m3.

 2) Annual: 3-year average not to exceed 15 g/m3.

*** Less than 80% of the possible samples (data) were collected.

Figure 13A Annual PM Emissions 

0

2000

4000

6000

8000

10000

12000

14000

1984 1986 1988 1990 1992 1994 1996 1998 2000 2002 2004 2006 PARTICULATE (tons)

NORTH DAKOTA

PARTICULATE EMISSIONS

TOTAL UTILITY BOILERS OTHER POINT SOURCES
27

Table 11 

 COMPARISON OF AIR QUALITY DATA WITH

 THE NORTH DAKOTA AMBIENT AIR QUALITY STANDARDS *

POLLUTANT : Inhalable Continuous PM10 (g/m3)

 M A X I M A

 

 SAMPLING NUM 1 - HOUR 24 - HOUR 24HR

 LOCATION YEAR PERIOD OBS 1ST 2ND 1ST 2ND 3RD 4TH MEAN #>150 AM>50

 │ │ │

 │ │ │

Beulah - North 2007 JAN-DEC 8675│ 164.0 108.0 │ 40.6 39.1 38.1 34.2│ 13.1 

 │ │ │

Bismarck Residential 2007 JAN-DEC 8651│ 305.0 218.0 │ 79.1 44.1 41.8 40.9│ 15.0 

 │ │ │

Dunn Center 2007 JAN-DEC 8579│ 246.0 239.0 │ 57.4 41.0 37.9 37.9│ 13.2 

 │ │ │

Fargo NW 2007 JAN-DEC 8667│ 367.0 260.0 │ 77.9 51.7 47.3 45.8│ 14.8 

 │ │ │

Lostwood NWR 2007 JAN-DEC 8692│ 332.0 206.0 │ 76.5 43.1 34.5 32.5│ 10.7 

 │ │ │

TRNP - NU 2007 JAN-DEC 7620│ 161.0 130.0 │ 47.5 44.2 30.2 26.4│ 9.2 

 │ │ │

* The STATE and FEDERAL air quality standards are:

 1) 150 g/m3 maximum averaged over a 24-hour period with no more than one expected exceedance per year.

 2) 50 g/m3 expected annual arithmetic mean.

*** Less than 80% of the possible samples (data) were collected.

Table 12

 COMPARISON OF AIR QUALITY DATA WITH

 THE NORTH DAKOTA AMBIENT AIR QUALITY STANDARDS *

POLLUTANT : Inhalable Continuous PMfine (g/m3)

 M A X I M A

 SAMPLING NUM 1 - HOUR 24 - HOUR 24HR

 LOCATION YEAR PERIOD OBS 1ST 2ND 1ST 2ND 3RD 4TH MEAN #>65 AM>15

 │ │ │

 │ │ │

Beulah - North 2007 JAN-DEC 8499│ 59.2 42.8 │ 18.7 14.3 14.2 14.2│ 3.7 

 │ │ │

Bismarck Residential 2007 JAN-DEC 8418│ 55.9 54.7 │ 21.0 16.2 13.1 12.8│ 4.5 

 │ │ │

Dunn Center 2007 JAN-DEC 8425│ 47.5 45.6 │ 19.1 17.9 15.8 13.3│ 3.6 

 │ │ │

Fargo NW 2007 JAN-DEC 8627│ 101.6 62.1 │ 17.4 17.1 17.1 15.2│ 4.8 

 │ │ │

Hannover 2007 JAN-DEC 8519│ 72.7 45.2 │ 21.9 18.1 16.5 16.4│ 6.7 

 │ │ │

Lostwood NWR 2007 JAN-DEC 8427│ 113.0 76.2 │ 15.1 11.7 11.3 10.8│ 3.2 

 │ │ │

TRNP - NU 2007 JAN-DEC 8227│ 71.0 68.3 │ 22.2 19.9 14.3 13.4│ 3.2 

* The ambient air quality standards are:

 FEDERAL Standards -

 1) 24-hour: 3-year average of 98th percentiles not to exceed 35 g/m3.

 2) Annual: 3-year average not to exceed 15 g/m3.

2.4.3 PM10 Network Analysis 

PM10 and smaller particles are of concern mainly because of their health effects. 

Continuous PM10 analyzers are installed at Beulah, Bismarck, Dunn Center, Fargo, 

Lostwood NWR, and TRNP – NU. The primary purpose for the continuous PM10

analyzers is to be used with the continuous PMfine analyzers to determine the PMcoarse

fraction. The data also was compared to both the data and federal ambient air quality 

standards. 
28

2.4.4 PMfine Network 

The manual PMfine network currently has three sites. Bismarck, Fargo and Beulah are 

non-CORE required sites. Bismarck and Fargo operate on a 1-in-3 day schedule, while 

Beulah operates on a 1-in-6 day schedule. Continuous PMfine analyzers (TEOMs) have 

been installed at Beulah, Bismarck, Dunn Center, Fargo, Hannover, Lostwood NWR and 

TRNP-NU.

2.4.5 Speciation Network 

One speciation sampler is installed as a National Trends Network sampler in Fargo. The 

data collected by this sampler is added to the AQS database by RTI.
29

2.5 Carbon Monoxide 

Many large urban areas in the United States have problems attaining the NAAQS for carbon 

monoxide (CO) where the primary source of CO is automobiles. North Dakota does not have 

sufficient population with the corresponding traffic congestion and 

geographical/meteorological conditions to create significant CO emission problems. 

However, there are several stationary sources in the state that emit more than 100 TPY of 

CO.

2.5.1 Sources 

The major stationary CO sources (>100 TPY) are listed in Table 13. Figure 14 shows the 

approximate locations of these facilities (the numbers correspond to the site and source 

tables). Most of these sources are the same sources that are the major emitters of SO2 and 

NOx. However, the corresponding CO levels from these sources are considerably lower.

2.5.2 Monitoring Network 

Carbon monoxide monitoring in North Dakota was terminated March 31, 1994, after 

operating five years. The conclusion drawn from the data was that North Dakota did not 

have a CO problem. A summary report of the data collected at the West Acres Shopping 

Mall was drafted for the Fargo-Moorhead Council of Governments for use in its traffic 

planning program. Starting in 2008, the department will begin operation of a Trace Level 

CO analyzer at the Fargo NW site in order to comply with the NCore requirements.
30

Figure 14 Major CO Sources 

TABLE 14

Major CO Sources

(> 100 TPY)

# COMPANY SOURCE Facility ID

1 Great River Energy Coal Creek Station 3805500017

2 Dakota Gasification Company Great Plains Synfuels Facility 3805700013

3 American Crystal Sugar Company Hillsboro Plant 3809700019

4 Basin Electric Power Cooperative Antelope Valley Station 3805700011

5 Montana Dakota Utilities Company RM Heskett Station 3805900001

6 Minnkota Power Cooperative, Inc. Milton R. Young Station 3806500020

7 Basin Electric Power Cooperative Leland Olds Station 3805700001

8 Otter Tail Power Company Coyote Station 3805700012

9 Minn-Dak Farmers Cooperative Wahpeton Plant 3807700026

10 Tesoro Refining and Marketing Company Mandan Refinery 3805900003

11 American Crystal Sugar Company Drayton Plant 3806700003

12 Hess Corporation Tioga Gas Plant 3810500004

13 Northern Sun (Division of ADM) Enderlin Facility 3807300001

14 Bear Paw Energy, L.L.C. Alexander Station 3805300024

15 Great River Energy GRE Stanton Station 3805700004

16 University of North Dakota UND Heating Plant 3803500003

17 Bear Paw Energy, L.L.C. Cow Creek Station 3810500077

18 Bear Paw Energy, L.L.C. Tree Top Station 3800700019
31

2.6 Lead 

Through prior sampling efforts, the department has determined that the state has low lead 

concentrations (38.6% of the standard) and no significant lead sources. This determination, 

coupled with the federal requirement for a NAMS network only in urbanized areas with 

populations greater than 500,000, resulted in terminating the lead monitoring program 

effective Dec. 31, 1983. Along with the low monitored concentrations, lead has been 

completely removed from gasoline since lead monitoring began in 1979.

2.7 Hydrogen Sulfide 

Although no Federal Ambient Air Quality Standard exists for hydrogen sulfide (H2S), the 

state of North Dakota has developed H2S standards.

2.7.1 Sources 

H2S emissions of concern stems almost totally from the oil and gas operations in the 

western part of the state; principally from the green outlined area on Figure 2. Flares and 

treater stacks associated with oil/gas wells, oil storage tanks, compressor stations, pipeline 

risers, and natural gas processing plants are potential H2S emission sources.

2.7.2 Monitoring Network 

Currently there are no state or industry H2S monitoring sites.

2.8 Air Toxics 

Currently there are no state or federal air toxics monitoring sites.

2.8.1 Sources 

The major air toxics sources are listed in Table 14 and Figure 15 shows the approximate 

locations of these facilities (the numbers correspond to the source table).
32

 Major Air Toxics Sources

 Air Toxics Monitoring Sites

 Class 1 Areas

0 7 M AY0 7 1 3 :5 6

2.8.2 Monitoring Network

Currently there are no state or industry air toxics monitoring sites. The historic raw data 

and associated summaries are available in EPA’s Air Quality System.

Table 15 

Major Air Toxics Sources 

(>100 TPY)

# COMPANY SOURCE Facility ID

1 Dakota Gasification Company Great Plains Synfuels Facility 3805700013

2 ADM Processing Velva Facility 3804900005

3 Northern Sun (Division of ADM) Enderlin Facility 3807300001

4 Great River Energy Coal Creek Station 3805500017

5 Tesoro Refining and Marketing Company Mandan Refinery 3805900003

Figure 15 Major Air Toxics Sources
33

3.0 SUMMARY AND CONCLUSIONS

The North Dakota Ambient Air Quality Monitoring Network is designed to monitor those air 

pollutants that demonstrate the greatest potential for deteriorating the air quality of North Dakota. 

Due to a greater number of pollution-producing sources in the western part of the state (primarily 

associated with the energy producing industries) the greatest percentage of the network is located in 

the western part of the State.

3.1 Sulfur Dioxide (SO2) 

Neither the state nor federal standards were exceeded at any monitoring site. The maximum 

concentrations and the maximum concentrations expressed as a percentage of the applicable 

standard are as follows: 1-hour – 81 ppb (29.7%); 3-hour – 60 ppb (12.0%); 24-hour – 15 ppb 

(15.2%); annual – 1.9 ppb (8.3%).

There is no SO2 5-minute standard currently in effect. The maximum 5-minute average was 

155 ppb.

3.2 Nitrogen Dioxide (NO2) 

Neither the state nor federal standards were exceeded at any of the monitoring sites. The 

maximum concentrations and the maximum concentrations expressed as a percentage of the 

applicable standard are as follows: annual – 6.2 ppb (11.7%)

3.3 Ozone (O3) 

Neither the state nor federal standard was exceeded during the year. The 1-hour maximum and 

highest 4th highest 8-hour concentrations and the concentrations expressed as a percentage of 

the applicable standard are as follows: 1-hour – 76 ppb (63.3%); highest 4th highest 8-hour – 65 

ppb (81.3%).
34

3.4 Inhalable Particulates 

Neither the state nor federal PM10 standards were exceeded during the year. The maximum 

concentrations and the maximum concentrations expressed as a percentage of the applicable 

PM10 standard are as follows: 24-hour – 79.1 μg/m3(52.7%); annual – 15.0 μg/m3(30.0%).

The federal PMfine standards were not exceeded during the year. The maximum concentrations 

and maximum concentrations expressed as a percentage of the standard are as follows: 24-

hour FRM – 19.5 μg/m3(55.7%); annual FRM – 7.5 μg/m3(50.0%).

3.5 Carbon Monoxide (CO) 

No monitoring was conducted.

3.6 Lead 

No monitoring was conducted.

3.7 Hydrogen Sulfide 

No monitoring was conducted.

3.8 Air Toxics 

No monitoring was conducted. 
Appendix A

AAQM Site Descriptions
36

This appendix is a condensation of Appendices B and C, combined with a site description and any 

information relating to specific analyzer or sampler. Please note that all sites meet the siting criteria 

specified in 40 CFR 58, Appendices A, C, D, and E. When selecting a site, five factors are 

considered: modeling results, landowner permission, power availability, year-round access to the site, 

and prevailing wind direction.

The sites addressed in this report are only the current active sites. A complete list of sites and all 

monitoring that has been conducted at each site that has ever reported data to EPA, you may go to 

www.epa.gov/air/data/aqsdb.html. The site is very easy to use and with a little experimenting, site and 

monitor selections can be made very specific. Also available at this site are air quality summary data 

and emissions data.

Another useful tool is Google EarthTM. (http://free.download.earth.googlepages.com/) With this tool, 

one can enter latitude and longitude to get either an expanded view or close-up view of each 

monitoring site.

For both of these tools, a high-speed Internet connection is highly recommended. They can be used 

with a dial-up connection, but it is not recommended.
37

Site: Beulah – North Station Type: SLAMS (required)

AQS#: 38-057-0004 MSA: 0000

Address: 6024 Highway 200, Beulah

Latitude: +47.298611 Longitude: -101.766944

Site Description: This is one of three key sites in the department’s ambient monitoring network to meet 

the six required monitoring objectives. When this site was established, it was decided to enhance the site 

to include ammonia, solar radiation and delta temperature to support air quality dispersion modeling. 

This site is one of the required PMfine monitoring sites for North Dakota

Gas/Particulate parameters:

Parameter

Sampling &

Analysis Method

Operating

Schedule

Monitoring

Objective

Spatial

Scale

Sulfur Dioxide Instrumental Pulsed Florescent Continuous Population Exposure Urban

Nitrogen Dioxide Instrumental Chemiluminescence Continuous Population Exposure Urban

Ozone Instrumental Ultra Violet Continuous Population Exposure Urban

Ammonia Instrumental Chemiluminescence Continuous General Background Regional

PMfine 24-hour Gravimetric 1/6 Population Exposure Urban

PMfine PMfine SCC W/ No Correction

TEOM Gravimetric 40 deg. Celsius

Continuous Population Exposure Urban

PM10 PM10 TEOM Gravimetric 50° 

Celsius

Continuous Population Exposure Urban

Meteorological parameters:

Parameter

Sampling &

Analysis Method

Operating

Schedule Tower Height

Spatial

Scale

Wind Speed Elec. or Mach Avg. Level 1 Continuous 10 meters Urban

Wind Direction Elec. or Mach Avg. Level 1 Continuous 10 meters Urban

Ambient Temperature Elec. or Mach Avg. Continuous 10 meters Urban

Delta Temperature Elec. or Mach Avg. Continuous 10 - 2 meters Urban

Ambient Pressure Barometric Pressure Transducer Continuous 6 meters Urban

Solar Radiation Pyranometer Continuous 2 meters Urban

There are no plans to move or remove this site.

The manual PMfine data may be compared to the annual NAAQS.
38

Site Pictures: Beulah North

 

 North South

 

 East West

 

Looking Northeast Looking Northwest
39

Beulah 

North
40

Site: Bismarck Residential Station Type: SLAMS

AQS#: 38-015-0003 MSA: 1010

Address: 1810 N 16th Street, Bismarck

Latitude: +46.825425 Longitude: -100.768210

Site Description: This site is located in the second largest metropolitan area in the state. 

When two special purpose sites in Mandan were closed, this site was expanded from a 

particulates-only site to be a full site for gases, continuous particulates (inc. ambient 

pressure) and the basic meteorological parameters (wind speed, wind direction and 

temperature). Another key role this site plays is to field test new types of equipment and 

procedures isolated from the equipment used to report data to AQS.

Gas/Particulate parameters:

Parameter

Sampling &

Analysis Method

Operating

Schedule

Monitoring

Objective

Spatial

Scale

Sulfur Dioxide Instrumental Pulsed Florescent Continuous Population Exposure Urban

Nitrogen Dioxide Instrumental Chemiluminescence Continuous Population Exposure Urban

Ozone Instrumental Ultra Violet Continuous Population Exposure Urban

PMfine 24-hour Gravimetric 1/6 Population Exposure Urban

PMfine PMfine SCC W/ No Correction

TEOM Gravimetric 40 deg. Celsius

Continuous Population Exposure Urban

PM10 PM10 TEOM Gravimetric 50° 

Celsius

Continuous Population Exposure Urban

Meteorological parameters:

Parameter

Sampling &

Analysis Method

Operating

Schedule Tower Height

Spatial

Scale

Wind Speed Elec. or Mach Avg. Level 1 Continuous 10 meters Urban

Wind Direction Elec. or Mach Avg. Level 1 Continuous 10 meters Urban

Ambient Temperature Elec. or Mach Avg. Continuous 10 meters Urban

Ambient Pressure Barometric Pressure Transducer Continuous 6 meters Urban

There are no plans to move or remove this site.

The manual PMfine data may be compared to the annual NAAQS.
41

Site Pictures: Bismarck Residential

 

 North East

 

 West Looking Northwest

 

 South Looking Southeast
42

Bismarck

Residential
43

Site: Dunn Center Station Type: SLAMS

AQS#: 38-025-0003 MSA: 0000

Address: 9610 Seventh Street SW, Dunn Center

Latitude: +47.313200 Longitude: -102.527300

Site Description: This site is located about midway between the oil development all along 

the North Dakota – Montana border and the seven coal conversion facilities to the east. 

The importance lies in the ability to monitor the transport of sulfur dioxide, nitrogen 

dioxide, and PMfine between these two areas. Also, this is a key site used in dispersion 

model calibration and validation.

Gas/Particulate parameters

Parameter

Sampling &

Analysis Method

Operating

Schedule

Monitoring

Objective

Spatial

Scale

Sulfur Dioxide Instrumental Pulsed Florescent Continuous General/Background Urban

Nitrogen Dioxide Instrumental Chemiluminescence Continuous General/Background Urban

Ozone Instrumental Ultra Violet Continuous General/Background Urban

PMfine PMfine SCC W/ No Correction

TEOM Gravimetric 40 deg. Celsius

Continuous General/Background Urban

PM10 PM10 TEOM Gravimetric 50° Celsius Continuous General/Background Urban

Meteorological parameters:

Parameter

Sampling &

Analysis Method

Operating

Schedule Tower Height

Spatial

Scale

Wind Speed Elec. or Mach Avg. Level 1 Continuous 10 meters Urban

Wind Direction Elec. or Mach Avg. Level 1 Continuous 10 meters Urban

Ambient Temperature Elec. or Mach Avg. Continuous 10 meters Urban

Delta Temperature Elec. or Mach Avg. Continuous 10 - 2 meters Urban

Ambient Pressure Barometric Pressure Transducer Continuous 6 meters Urban

Solar Radiation Pyranometer Continuous 2 meters Urban

There are no plans to move or remove this site. 
44

Site Pictures: Dunn Center

 

North West

 

 East South

 

 Looking Northwest Looking Northeast
45

Dunn Center
46

Site Name: Fargo NW Station Type: SLAMS (required)

AQS#: 38-017-1004 MSA: 2520

Address: 4266 40th Avenue North, Fargo

Latitude: +46.933754 Longitude: -96.855350

Site Description: This site is one of EPA’s 54 Speciation Trends Network sites, the state’s required 

NCORE Level II site, located in the largest metropolitan area in North Dakota. The data collected at this 

site is used in dispersion modeling for input, calibration and validation. An NCORE Level II site is 

required to have trace level analyzers for sulfur dioxide, carbon monoxide, and NOY (total reactive 

nitrogen) operational by January 1, 2011. The trace level sulfur dioxide is installed. The other two 

analyzers have been ordered and will be installed when the Department is satisfied with their operation.

Gas/Particulate parameters:

Parameter

Sampling &

Analysis Method

Operating

Schedule

Monitoring

Objective

Spatial

Scale

Sulfur Dioxide Instrumental Pulsed Florescent Continuous Population Exposure Urban

Nitrogen Dioxide Instrumental Chemiluminescence Continuous Population Exposure Urban

Ozone Instrumental Ultra Violet Continuous Population Exposure Urban

PMfine 24-hour Gravimetric 1/3 Population Exposure Urban

PMfine PMFINE SCC W/ No Correction

TEOM Gravimetric 40 deg. Celsius

Continuous Population Exposure Urban

PM10 PM10 TEOM Gravimetric 50° Celsius Continuous Population Exposure Urban

PMfine Speciation METOne SASS 24-hour Gravimetric 1/3 Population Exposure Urban

Meteorological parameters:

Parameter

Sampling &

Analysis Method

Operating

Schedule Tower Height

Spatial

Scale

Wind Speed Elec. or Mach Avg. Level 1 Continuous 10 meters Urban

Wind Direction Elec. or Mach Avg. Level 1 Continuous 10 meters Urban

Ambient Temperature Elec. or Mach Avg. Continuous 10 meters Urban

Delta Temperature Elec. or Mach Avg. Continuous 10 - 2 meters Urban

Ambient Pressure Barometric Pressure Transducer Continuous 6 meters Urban

Relative Humidity Hygroscopic Plastic Film Continuous 10 meters Urban

Solar Radiation Pyranometer Continuous 2 meters Urban

There are no plans to move or remove this site.

The manual PMfine data may be compared to the annual NAAQS
47

Site Pictures: Fargo NW

 

 North West

 

East South

 

 Looking Northeast Looking West
48

Fargo NW
49

Site Name: Hannover Station Type: SLAMS

AQS#: 38-065-0002 MSA: 0000

Address: 1575 Highway 31, Stanton

Latitude: +47.185833 Longitude: -101.428056

Site Description: This site is centrally located to the power plants in the Oliver-MercerMcLean county area. The data collected here is used to supplement ambient data collected 

at Beulah – North and TRNP – NU.

Gas/Particulate parameters:

Parameter

Sampling &

Analysis Method

Operating

Schedule

Monitoring

Objective

Spatial

Scale

Sulfur Dioxide Instrumental Pulsed Florescent Continuous Source Oriented Urban

Nitrogen Dioxide Instrumental Chemiluminescence Continuous Source Oriented Urban

Ozone Instrumental Ultra Violet Continuous Source Oriented Urban

PMfine PMfine SCC W/ No Correction

TEOM Gravimetric 40 deg. Celsius

Continuous Source Oriented Urban

Meteorological parameters:

Parameter

Sampling &

Analysis Method

Operating

Schedule Tower Height

Spatial

Scale

Wind Speed Elec. or Mach Avg. Level 1 Continuous 10 meters Urban

Wind Direction Elec. or Mach Avg. Level 1 Continuous 10 meters Urban

Ambient Temperature Elec. or Mach Avg. Continuous 10 meters Urban

Ambient Pressure Barometric Pressure Transducer Continuous 6 meters Urban

There are no plans to move or remove this site. 
50

Site Pictures: Hannover

 

 North East

 

 South West

 

 Looking Southwest Looking Northeast

Site Location 
51

Hannover
52

Site Name: Lostwood NWR Station Type: SLAMS

AQS#: 38-013-0004 MSA: 0000

Address: 8315 Highway 8, Kenmare

Latitude: +48.641930 Longitude: -102.401800

Site Description: This site is located in a PSD Class I area. Because this site is downwind 

of the two power plants near Estevan, SK, and located in the Souris River Airshed, this 

data is also usable by SaskEnvironment in a study they are conducting in the western 

region of the Souris Basin Airshed.

The site has an IMPROVE sampler operated by the US Fish and Wildlife Service. This 

data will be used with the other ambient data collected here to evaluate long-range 

transport of aerosols affecting regional haze/visibility.

Gas/Particulate parameters:

Parameter

Sampling &

Analysis Method

Operating

Schedule

Monitoring

Objective

Spatial

Scale

Sulfur Dioxide Instrumental Pulsed Florescent Continuous Regional Transport Regional

Nitrogen Dioxide Instrumental Chemiluminescence Continuous Regional Transport Regional

Ozone Instrumental Ultra Violet Continuous Regional Transport Regional

PMfine PMfine SCC W/ No Correction

TEOM Gravimetric 40 deg. Celsius

Continuous Regional Transport Regional

PM10 PM10 TEOM Gravimetric 50° Celsius Continuous Regional Transport Regional

Meteorological parameters: 

Parameter

Sampling &

Analysis Method

Operating

Schedule Tower Height

Spatial

Scale

Wind Speed Elec. or Mach Avg. Level 1 Continuous 10 meters Urban

Wind Direction Elec. or Mach Avg. Level 1 Continuous 10 meters Urban

Ambient Temperature Elec. or Mach Avg. Continuous 10 meters Urban

Delta Temperature Elec. or Mach Avg. Continuous 10 - 2 meters Urban

Ambient Pressure Barometric Pressure Transducer Continuous 6 meters Urban

Solar Radiation Pyranometer Continuous 2 meters Urban

Relative Humidity Hygroscopic Plastic Film Continuous 10 meters Urban

There are no plans to move or remove this site. 
53

Site Pictures: Lostwood NWR

 

North South

 

East West

 

 Looking Northwest Looking North
54

Lostwood
55

Site Name: TRNP-NU Station Type: SLAMS(required)

AQS#: 38-053-0002 MSA: 0000

Address: 229 Service Road, Watford City

Latitude: +47.581200 Longitude: -103.299500

Site Description: This site is located in Theodore Roosevelt National Park – North Unit 

and is one of three key sites in the department’s ambient monitoring network to meet the 

six required monitoring objectives. The data collected is used for model 

calibration/validation.

Gas/Particulate parameters:

Parameter

Sampling &

Analysis Method

Operating

Schedule

Monitoring

Objective

Spatial

Scale

Sulfur Dioxide Instrumental Pulsed Florescent Continuous General/Background Regional

Nitrogen Dioxide Instrumental Chemiluminescence Continuous General/Background Regional

Ozone Instrumental Ultra Violet Continuous General/Background Regional

PMfine PMfine SCC W/ No Correction

TEOM Gravimetric 40 deg. Celsius

Continuous General/Background

Regional Transport

Regional

PM10 PM10 TEOM Gravimetric 50° Celsius Continuous General/Background

Regional Transport

Regional

Meteorological parameters:

Parameter Sampling &

Analysis Method

Operating

Schedule

Tower Height Spatial

Scale

Wind Speed Elec. or Mach Avg. Level 1 Continuous 10 meters Urban

Wind Direction Elec. or Mach Avg. Level 1 Continuous 10 meters Urban

Ambient Temperature Elec. or Mach Avg. Continuous 10 meters Urban

Ambient Pressure Barometric Pressure Transducer Continuous 6 meters Urban

Relative Humidity Hygroscopic Plastic Film Continuous 10 meters Urban

There are no plans to move or remove this site. 
56

Site Pictures: TRNP-NU

 

 North South

 

East West

 

 Looking Northwest Looking Northeast
57

TRNP-NU
Appendix B

Detailed Site Descriptions
59

This appendix is a listing printed from the EPA’s Air Quality System (AQS) database. Please note that 

if the latitude and longitude are used in Google EarthTM, the display generated may not exactly match 

the display in Appendix A. This is a problem with Google EarthTM, not the coordinates in AQS.
60

 

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

AIR QUALITY SYSTEM

May. 18, 2007

SITE DESCRIPTION REPORT

North Dakota

Site ID: 38-013-0004 Site Name: LOSTWOOD NWR Local ID:

Street Address: 8315 HIGHWAY 8, KENMARE

Date Established: 19990101 Date Terminated: Last Updated: 20060814

HQ Eval. Date:

EPA Region: DENVER

County: Burke

MSA: Not in a MSA CMSA: Not in a CMSA

City: Not in a city

City Population: 1 Dir. to CBD: Dist. to City(km):

AQCR : NORTH DAKOTA

Local Region:

Urban Area: NOT IN AN URBAN AREA

Class 1 Area: Lostwood National Wildlife Refuge

Zip Code: 58721

Census Block: Block Group: Census Tract:

Congressional District:

Site Latitude: +48.641930

UTM Zone: 13

Accuracy: .01

Site Longitude: -102.401800 Time Zone: CENTRAL

UTM Northing: 5390691.44

Datum: WGS84

Coll. Method: GPS CODE (PSEUDO RANGE) DIFFERENTIAL

Vertical Measure(m): 696.0

UTM Easting: 691395.29

Scale: 24000 Point/Line/Area: POINT

Location Description: MONITORING POINT

Type Met Site: ON-SITE MET EQUIP

Met. Site ID:

Dist to Met. Site(m):

Direct Met Site:

Regional Eval. Date:

Location Setting: RURAL

Land Use: AGRICULTURAL

SUPPORTING

Role

North Dakota State Department Of Health

Agency Desc

20031027

Begin Date End Date

AGENCY ROLES

SLAMS

OTHER

IMPROVE

Monitor Type

5

12

59

# of

Monitors

1

2

3

4

Road

Number

90TH STREET NW

ND HIGHWAY 8

NDHIGHWAY 8

COUNTY ROAD 11

Road Name

10

100

100

10

Traffic

Count

2002

2002

2002

2002

Traffic

Year

DOT

DOT

DOT

DOT

Traffic Volume Source

LOCAL ST OR 

HYTHRU ST OR HY

THRU ST OR HY

LOCAL ST OR 

HY

Road Type

N

E

S

W

Compass

Sector

Vert Datum NAVD88 Vert Method: GPS CODE (PSEUDO RANGE) DIFFERENTIAL

Vert Accuracy: .01

ACTIVE MONITOR TYPES

TANGENT ROADS

State:
61

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

AIR QUALITY SYSTEM

May. 18, 2007

SITE DESCRIPTION REPORT

North Dakota

Site ID: 38-015-0003 Site Name: BISMARCK RESIDENTIAL Local ID:

Street Address: 1810 N 16TH STREET

Date Established: 19950501 Date Terminated: Last Updated: 20060814

HQ Eval. Date:

EPA Region: DENVER

County: Burleigh

MSA: Bismarck,ND CMSA:

City: Bismarck

City Population: 55532 Dir. to CBD: N Dist. to City(km): 2

AQCR : NORTH DAKOTA

Local Region:

Urban Area: BISMARCK, ND

Class 1 Area:

Zip Code: 58501

Census Block: Block Group: Census Tract:

Congressional District:

Site Latitude: +46.825425

UTM Zone: 14

Accuracy: .03

Site Longitude: -100.768210 Time Zone: CENTRAL

UTM Northing: 5187064

Datum: WGS84

Coll. Method: GPS CODE (PSEUDO RANGE) DIFFERENTIAL

Vertical Measure(m): 580.0

UTM Easting: 365130.78

Scale: 0 Point/Line/Area: POINT

Location Description: MONITORING POINT

Type Met Site: NWS

Met. Site ID:

Dist to Met. Site(m): 3200

Direct Met Site: S

Regional Eval. Date:

Location Setting: SUBURBAN

Land Use: RESIDENTIAL

SUPPORTING

Role

North Dakota State Department Of Health

Agency Desc

19950501

Begin Date End Date

AGENCY ROLES

SUPPLMNTL 

SPECIAT OTHER

SLAMS

Monitor Type

134

18

16

# of

Monitors

1

2

3

4

Road

Number

16TH AVE.

15TH ST

17TH ST

SPALDING AVE.

Road Name

10650

150

100

20

Traffic

Count

1991

1994

1994

1994

Traffic

Year Traffic Volume Source

LOCAL ST OR 

HYLOCAL ST OR 

HYLOCAL ST OR 

HYLOCAL ST OR 

HY

Road Type

S

W

E

N

Compass

Sector

Vert Datum NAVD88 Vert Method: GPS CODE (PSEUDO RANGE) DIFFERENTIAL

Vert Accuracy: .03

ACTIVE MONITOR TYPES

TANGENT ROADS

State:
62

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

AIR QUALITY SYSTEM

May. 18, 2007

SITE DESCRIPTION REPORT

North Dakota

Site ID: 38-017-1004 Site Name: FARGO NW Local ID:

Street Address: 4266 40TH AVE NORTH

Date Established: 19980513 Date Terminated: Last Updated: 20060814

HQ Eval. Date:

EPA Region: DENVER

County: Cass

MSA: Fargo-Moorhead,ND-MN CMSA:

City: Fargo

City Population: 90599 Dir. to CBD: N Dist. to City(km): 4

AQCR : METROPOLITAN FARGO-MOORHEAD

Local Region:

Urban Area: FARGO-MOORHEAD, ND-MN

Class 1 Area:

Zip Code: 58102

Census Block: Block Group: Census Tract:

Congressional District: 1

Site Latitude: +46.933754

UTM Zone: 14

Accuracy: .03

Site Longitude: - 96.855350 Time Zone: CENTRAL

UTM Northing: 5199816.62

Datum: WGS84

Coll. Method: GPS CODE (PSEUDO RANGE) DIFFERENTIAL

Vertical Measure(m): 275.0

UTM Easting: 663252.17

Scale: 0 Point/Line/Area: POINT

Location Description: MONITORING POINT

Type Met Site: ON-SITE MET EQUIP

Met. Site ID:

Dist to Met. Site(m):

Direct Met Site:

Regional Eval. Date:

Location Setting: SUBURBAN

Land Use: AGRICULTURAL

SUPPORTING

Role

North Dakota State Department Of Health

Agency Desc

19980513

Begin Date End Date

AGENCY ROLES

TRENDS SPECIATION

OTHER

SLAMS

Monitor Type

67

23 Air Toxics

6

# of

Monitors

1

2

3

Road

Number

19TH AVE N.

INTERSTATE 94

COUNTY 20

Road Name

550

8790

975

Traffic

Count

1989

1989

1989

Traffic

Year Traffic Volume Source

THRU ST OR HY

ARTERIAL

THRU ST OR HY

Road Type

S

E

N

Compass

Sector

Vert Datum NAVD88 Vert Method: GPS CODE (PSEUDO RANGE) DIFFERENTIAL

Vert Accuracy: .03

ACTIVE MONITOR TYPES

TANGENT ROADS

State:
63

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

AIR QUALITY SYSTEM

May. 18, 2007

SITE DESCRIPTION REPORT

North Dakota

Site ID: 38-025-0003 Site Name: DUNN CENTER Local ID:

Street Address: 9610 SEVENTH STREET SW

Date Established: 19750701 Date Terminated: Last Updated: 20060814

HQ Eval. Date:

EPA Region: DENVER

County: Dunn

MSA: Not in a MSA CMSA: Not in a CMSA

City: Not in a city

City Population: 1 Dir. to CBD: Dist. to City(km):

AQCR : NORTH DAKOTA

Local Region:

Urban Area: NOT IN AN URBAN AREA

Class 1 Area:

Zip Code: 58626

Census Block: Block Group: Census Tract:

Congressional District: 1

Site Latitude: +47.313200

UTM Zone: 13

Accuracy: .03

Site Longitude: -102.527300 Time Zone: MOUNTAIN

UTM Northing: 5242716.42

Datum: WGS84

Coll. Method: GPS CARRIER PHASE STATIC RELATIVE POSITION

Vertical Measure(m): 683.0

UTM Easting: 686888.26

Scale: 0 Point/Line/Area: POINT

Location Description: MONITORING POINT

Type Met Site: ON-SITE MET EQUIP

Met. Site ID:

Dist to Met. Site(m):

Direct Met Site:

Regional Eval. Date:

Location Setting: RURAL

Land Use: AGRICULTURAL

* *

SITE COMMENTS

SUPPORTING

Role

North Dakota State Department Of Health

Agency Desc

19750701

Begin Date End Date

AGENCY ROLES

INDEX SITE

OTHER

SLAMS

Monitor Type

1

10

7

# of

Monitors

1

Road

Number

SEVENTH STREET SW

Road Name

10

Traffic

Count

2004

Traffic

Year

DOT

Traffic Volume Source

LOCAL ST OR 

HY

Road Type

N

Compass

Sector

Vert Datum NAVD88 Vert Method: GPS CODE (PSEUDO RANGE) DIFFERENTIAL

Vert Accuracy: .03

ACTIVE MONITOR TYPES

TANGENT ROADS

State:
64

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

AIR QUALITY SYSTEM

May. 18, 2007

SITE DESCRIPTION REPORT

North Dakota

Site ID: 38-053-0002 Site Name: TRNP-NU Local ID:

Street Address: 229 SERVICE RD., WATFORD CITY

Date Established: 19781201 Date Terminated: Last Updated: 20060814

HQ Eval. Date:

EPA Region: DENVER

County: McKenzie

MSA: Not in a MSA CMSA: Not in a CMSA

City: Not in a city

City Population: 1 Dir. to CBD: Dist. to City(km):

AQCR : NORTH DAKOTA

Local Region:

Urban Area: NOT IN AN URBAN AREA

Class 1 Area: T. Roosevelt Park (North)

Zip Code: 58854

Census Block: Block Group: Census Tract:

Congressional District:

Site Latitude: +47.581200

UTM Zone: 13

Accuracy: .03

Site Longitude: -103.299500 Time Zone: MOUNTAIN

UTM Northing: 5270936.38

Datum: NAD83

Coll. Method: GPS CARRIER PHASE STATIC RELATIVE POSITION

Vertical Measure(m): 624.0

UTM Easting: 627875.21

Scale: 0 Point/Line/Area: POINT

Location Description: MONITORING POINT

Type Met Site: ON-SITE MET EQUIP

Met. Site ID:

Dist to Met. Site(m):

Direct Met Site:

Regional Eval. Date:

Location Setting: RURAL

Land Use: AGRICULTURAL

LOCATED IN THE THOEDORE ROOSEVELT NATIONAL PARK APPROXIMATELY 10 KM INSIDE THE PARK ENTRANCE.

SITE COMMENTS

SUPPORTING

Role

North Dakota State Department Of Health

Agency Desc

19781201

Begin Date End Date

AGENCY ROLES

SLAMS

SUPPLMNTL SPECIAT

OTHER

Monitor Type

6

67

9

# of

Monitors

Vert Datum NAVD88 Vert Method: GPS CODE (PSEUDO RANGE) DIFFERENTIAL

Vert Accuracy: 0

ACTIVE MONITOR TYPES

State:
65

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

AIR QUALITY SYSTEM

May. 18, 2007

SITE DESCRIPTION REPORT

North Dakota

Site ID: 38-057-0004 Site Name: BEULAH NORTH Local ID:

Street Address: 6024 HIGHWAY 200

Date Established: 19981213 Date Terminated: Last Updated: 20031212

HQ Eval. Date:

EPA Region: DENVER

County: Mercer

MSA: Not in a MSA CMSA: Not in a CMSA

City: Beulah

City Population: 3152 Dir. to CBD: Dist. to City(km):

AQCR : NORTH DAKOTA

Local Region:

Urban Area: NOT IN AN URBAN AREA

Class 1 Area:

Zip Code: 58571

Census Block: Block Group: Census Tract:

Congressional District:

Site Latitude: +47.298611

UTM Zone: 14

Accuracy: .03

Site Longitude: -101.766944 Time Zone: MOUNTAIN

UTM Northing: 5241843

Datum: WGS84

Coll. Method: GPS CODE (PSEUDO RANGE) DIFFERENTIAL

Vertical Measure(m): 630.0

UTM Easting: 290816

Scale: 0 Point/Line/Area: POINT

Location Description: MONITORING POINT

Type Met Site: ON-SITE MET EQUIP

Met. Site ID:

Dist to Met. Site(m):

Direct Met Site:

Regional Eval. Date:

Location Setting: RURAL

Land Use: AGRICULTURAL

SUPPORTING

Role

North Dakota State Department Of Health

Agency Desc

19981213

Begin Date End Date

AGENCY ROLES

SLAMS

OTHER

Monitor Type

10

78 Air Toxics

# of

Monitors

1

2

3

Road

Number

HIGHWAY 200

COUNTY ROAD

CITY STREET

Road Name

1000

100

250

Traffic

Count

1998

1998

1998

Traffic

Year Traffic Volume Source

THRU ST OR HY

LOCAL ST OR 

HYTHRU ST OR HY

Road Type

N

W

S

Compass

Sector

Vert Datum NAVD88 Vert Method: GPS CODE (PSEUDO RANGE) DIFFERENTIAL

Vert Accuracy: .03

ACTIVE MONITOR TYPES

TANGENT ROADS

State:
66

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

AIR QUALITY SYSTEM

May. 18, 2007

SITE DESCRIPTION REPORT

North Dakota

Site ID: 38-065-0002 Site Name: HANNOVER Local ID:

Street Address: 1575 HIGHWAY 31

Date Established: 19841004 Date Terminated: Last Updated: 20050304

HQ Eval. Date:

EPA Region: DENVER

County: Oliver

MSA: Not in a MSA CMSA: Not in a CMSA

City: Not in a city

City Population: 1 Dir. to CBD: S Dist. to City(km): 7

AQCR : NORTH DAKOTA

Local Region:

Urban Area: NOT IN AN URBAN AREA

Class 1 Area:

Zip Code:

Census Block: Block Group: Census Tract:

Congressional District: 1

Site Latitude: +47.185833

UTM Zone: 14

Accuracy: .01

Site Longitude: -101.428056 Time Zone: MOUNTAIN

UTM Northing: 5228457

Datum: WGS84

Coll. Method: GPS CODE (PSEUDO RANGE) DIFFERENTIAL

Vertical Measure(m): 697.0

UTM Easting: 316045

Scale: 0 Point/Line/Area: POINT

Location Description: MONITORING POINT

Type Met Site: ON-SITE MET EQUIP

Met. Site ID:

Dist to Met. Site(m):

Direct Met Site:

Regional Eval. Date:

Location Setting: RURAL

Land Use: AGRICULTURAL

*

SITE COMMENTS

SUPPORTING

Role

North Dakota State Department Of Health

Agency Desc

19841004

Begin Date End Date

AGENCY ROLES

OTHER

SLAMS

Monitor Type

6

5

# of

Monitors

1

Road

Number

STATE HIGHWAY 31

Road Name

350

Traffic

Count

2000

Traffic

Year

DOT

Traffic Volume Source

LOCAL ST OR 

HY

Road Type

E

Compass

Sector

Vert Datum NAVD88 Vert Method: GPS CODE (PSEUDO RANGE) DIFFERENTIAL

Vert Accuracy: .01

ACTIVE MONITOR TYPES

TANGENT ROADS

State:
Appendix C

Detailed Monitor Descriptions
68

This appendix is a listing printed from the AQS database for only the gaseous parameters for each site. 
69

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Nitrogen Dioxide

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Beulah

Site Name: BEULAH NORTH

Street Address: 6024 HIGHWAY 200

MSA: Not in a MSA

County: Mercer UAR: NOT IN AN URBAN AREA

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: AREA

Meas. Scale: URBAN SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

*

MONITOR COMMENT

19990114

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

REPORTING

COLLECTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19990114

19990114

19990114

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

19990114

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19990101

19990101

19990101

Date Met

REGULATION INFORMATION

HIGHWAY 200

COUNTY ROAD

CITY STREET

Street Name

THRU ST OR HY

LOCAL ST OR HY

THRU ST OR HY

Type Road

1000

100

250

Traff

Count

1998

1998

1998

Traff

Yr

32

1000

3200

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

38-057-0004-42602-1
70

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Ammonia

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Beulah

Site Name: BEULAH NORTH

Street Address: 6024 HIGHWAY 200

MSA: Not in a MSA

County: Mercer UAR: NOT IN AN URBAN AREA

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: AREA

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

20001103

Begin Date End Date

DATES OF OPERATION

GENERAL/BACKGROUND

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20001103

20001103

20001103

Begin Date End Date

AGENCY ROLES

OTHER

SLAMS

Monitor Type

20001114

20001103

Begin Date

20001113

End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20001103

20001101

20001101

Date Met

REGULATION INFORMATION

HIGHWAY 200

COUNTY ROAD

CITY STREET

Street Name

THRU ST OR HY

LOCAL ST OR HY

THRU ST OR HY

Type Road

1000

100

250

Traff

Count

1998

1998

1998

Traff

Yr

32

1000

3200

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

38-057-0004-42604-1
71

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM-Fine

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070507

Owner: North Dakota Bismarck

Site Name: BISMARCK RESIDENTIAL

Street Address: 1810 N 16TH STREET

MSA: Bismarck,ND

County: Burleigh UAR: BISMARCK, ND

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: POINT

Meas. Scale: URBAN SCALE Location Setting: SUBURBAN

Probe Location: GROUND LEVEL SUPPORT Horizontal Distance (m):

Probe Height (m): 3.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

20060125

Begin Date End Date Dist.(m)

Y

Primary?

COLLOCATION INFORMATION

19990101

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

Monitor Objective Type

BISMARCK, ND

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

Inter-Mountain Laboratory Sheridan, WY

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19990101

19990101

19990101

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

19990101

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19990101

19990101

19990101

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-015-0003-88101-1
72

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM-Fine

North Dakota

Monitor ID:

Date of Latest Collection: 20061231 Last Updated: 20070226

Owner: North Dakota Not in a city

Site Name: TRNP-NU

Street Address: 229 SERVICE RD., WATFORD CITY

MSA: Not in a MSA

County: McKenzie UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: GROUND LEVEL SUPPORT Horizontal Distance (m):

Probe Height (m): 2.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

20020101

Begin Date

20061231

End Date

DATES OF OPERATION

REGIONAL TRANSPORT

GENERAL/BACKGROUND

Monitor Objective Type

NOT IN AN URBAN AREA

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

Inter-Mountain Laboratory Sheridan, WY

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20020101

20020101

20020101

Begin Date

20061231

End Date

AGENCY ROLES

SLAMS

Monitor Type

20020101

Begin Date

20061231

End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20020101

20020101

20020101

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-053-0002-88101-1
73

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM-Fine

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: TRNP-NU

Street Address: 229 SERVICE RD., WATFORD CITY

MSA: Not in a MSA

County: McKenzie UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: POINT

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

20021001

Begin Date End Date

DATES OF OPERATION

GENERAL/BACKGROUND

REGIONAL TRANSPORT

Monitor Objective Type

NOT IN AN URBAN AREA

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20021001

20021001

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20021001

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

City:

MONITORING OBJECTIVES

38-053-0002-88501-3
74

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM-Fine

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070507

Owner: North Dakota Beulah

Site Name: BEULAH NORTH

Street Address: 6024 HIGHWAY 200

MSA: Not in a MSA

County: Mercer UAR: NOT IN AN URBAN AREA

Project Type: SOURCE-ORIENTED AMBIENT SURVEILLANCE Dominant Source: AREA

Meas. Scale: URBAN SCALE Location Setting: RURAL

Probe Location: GROUND LEVEL SUPPORT Horizontal Distance (m):

Probe Height (m): 3.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

20000101

Begin Date

20030714

End Date Dist.(m)

Y

Primary?

COLLOCATION INFORMATION

*

MONITOR COMMENT

19990101

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

Inter-Mountain Laboratory Sheridan, WY

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19990101

19990101

19990101

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

19990101

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19990101

19990101

19990101

Date Met

REGULATION INFORMATION

HIGHWAY 200

COUNTY ROAD

CITY STREET

Street Name

THRU ST OR HY

LOCAL ST OR HY

THRU ST OR HY

Type Road

1000

100

250

Traff

Count

1998

1998

1998

Traff

Yr

32

1000

3200

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

38-057-0004-88101-1
75

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Ozone

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: LOSTWOOD NWR

Street Address: 8315 HIGHWAY 8, KENMARE

MSA: Not in a MSA

County: Burke UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: POINT

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

20031028

Begin Date End Date

DATES OF OPERATION

REGIONAL TRANSPORT

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20031028

20031028

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20031028

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20031028

20031028

20031028

Date Met

REGULATION INFORMATION

90TH STREET NW

ND HIGHWAY 8

NDHIGHWAY 8

COUNTY ROAD 11

Street Name

LOCAL ST OR HY

THRU ST OR HY

THRU ST OR HY

LOCAL ST OR HY

Type Road

10

100

100

10

Traff

Count

2002

2002

2002

2002

Traff

Yr

8290

1120

840

13800

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

38-013-0004-44201-1
76

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Nitrogen Dioxide

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: DUNN CENTER

Street Address: 9610 SEVENTH STREET SW

MSA: Not in a MSA

County: Dunn UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?:

*

MONITOR COMMENT

19791001

19981214

Begin Date

19890331

End Date

DATES OF OPERATION

GENERAL/BACKGROUND

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19791001

19791001

19791001

Begin Date End Date

AGENCY ROLES

OTHER

SLAMS

Monitor Type

19791001

19800101

Begin Date

19791231

End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19800101

19800101

19800101

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-025-0003-42602-1
77

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Ozone

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Fargo

Site Name: FARGO NW

Street Address: 4266 40TH AVE NORTH

MSA: Fargo-Moorhead,ND-MN

County: Cass UAR: FARGO-MOORHEAD, ND-MN

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: AREA

Meas. Scale: URBAN SCALE Location Setting: SUBURBAN

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

19980527

Begin Date End Date

DATES OF OPERATION

MAX PRECURSOR EMISSIONS

IMPACT

POPULATION EXPOSURE

Monitor Objective Type

FARGO-MOORHEAD, ND-MN

UAR Name

Fargo-Moorhead,ND-MN

MSA Name CMSA Name

ANALYZING

REPORTING

COLLECTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19980527

19980527

19980527

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

19980527

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19980501

19980501

19980501

Date Met

REGULATION INFORMATION

19TH AVE N.

INTERSTATE 94

COUNTY 20

Street Name

THRU ST OR HY

ARTERIAL

THRU ST OR HY

Type Road

550

8790

975

Traff

Count

1989

1989

1989

Traff

Yr

1600

350

30

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

38-017-1004-44201-1
78

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Ozone

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Bismarck

Site Name: BISMARCK RESIDENTIAL

Street Address: 1810 N 16TH STREET

MSA: Bismarck,ND

County: Burleigh UAR: BISMARCK, ND

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: AREA

Meas. Scale: URBAN SCALE Location Setting: SUBURBAN

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?:

20051003

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

Monitor Objective Type

BISMARCK, ND

UAR Name MSA Name CMSA Name

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20051003

20051003

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20051003

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20051003

20051003

20051003

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-015-0003-44201-1
79

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Sulfur Dioxide

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Beulah

Site Name: BEULAH NORTH

Street Address: 6024 HIGHWAY 200

MSA: Not in a MSA

County: Mercer UAR: NOT IN AN URBAN AREA

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: AREA

Meas. Scale: URBAN SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

*

MONITOR COMMENT

19990114

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19990114

19990114

19990114

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

19990114

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19990101

19990101

19990101

Date Met

REGULATION INFORMATION

HIGHWAY 200

COUNTY ROAD

CITY STREET

Street Name

THRU ST OR HY

LOCAL ST OR HY

THRU ST OR HY

Type Road

1000

100

250

Traff

Count

1998

1998

1998

Traff

Yr

32

1000

3200

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

38-057-0004-42401-1
80

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Ozone

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Beulah

Site Name: BEULAH NORTH

Street Address: 6024 HIGHWAY 200

MSA: Not in a MSA

County: Mercer UAR: NOT IN AN URBAN AREA

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: AREA

Meas. Scale: URBAN SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

*

MONITOR COMMENT

19990114

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19990114

19990114

19990114

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

19990114

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19990101

19990101

19990101

Date Met

REGULATION INFORMATION

HIGHWAY 200

COUNTY ROAD

CITY STREET

Street Name

THRU ST OR HY

LOCAL ST OR HY

THRU ST OR HY

Type Road

1000

100

250

Traff

Count

1998

1998

1998

Traff

Yr

32

1000

3200

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

38-057-0004-44201-1
81

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Nitrogen Dioxide

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: HANNOVER

Street Address: 1575 HIGHWAY 31

MSA: Not in a MSA

County: Oliver UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: URBAN SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 3.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

19880323

Begin Date End Date

DATES OF OPERATION

SOURCE ORIENTED

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19880323

19880323

19880323

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

19880323

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19880301

19880301

19880301

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-065-0002-42602-1
82

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM-Fine

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: DUNN CENTER

Street Address: 9610 SEVENTH STREET SW

MSA: Not in a MSA

County: Dunn UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

*

MONITOR COMMENT

20040908

Begin Date End Date

DATES OF OPERATION

GENERAL/BACKGROUND

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20040908

20040908

20040908

Begin Date End Date

AGENCY ROLES

INDEX SITE

OTHER

SLAMS

Monitor Type

20040908

20040908

20040908

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

City:

MONITORING OBJECTIVES

38-025-0003-88501-3
83

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Ozone

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: TRNP-NU

Street Address: 229 SERVICE RD., WATFORD CITY

MSA: Not in a MSA

County: McKenzie UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

SITE RESTARTED ON AUG 8, 2001

MONITOR COMMENT

19821105

20010801

Begin Date

19980630

End Date

DATES OF OPERATION

GENERAL/BACKGROUND

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

REPORTING

COLLECTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19821105

19821105

19821105

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

19821105

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19821101

19821101

19821101

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-053-0002-44201-1
84

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Sulfur Dioxide

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Fargo

Site Name: FARGO NW

Street Address: 4266 40TH AVE NORTH

MSA: Fargo-Moorhead,ND-MN

County: Cass UAR: FARGO-MOORHEAD, ND-MN

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: POINT

Meas. Scale: URBAN SCALE Location Setting: SUBURBAN

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 3.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

19980527

Begin Date End Date

DATES OF OPERATION

MAX PRECURSOR EMISSIONS

IMPACT

POPULATION EXPOSURE

Monitor Objective Type

FARGO-MOORHEAD, ND-MN

UAR Name

Fargo-Moorhead,ND-MN

MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19980527

19980527

19980527

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

19980527

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19980501

19980501

19980501

Date Met

REGULATION INFORMATION

19TH AVE N.

INTERSTATE 94

COUNTY 20

Street Name

THRU ST OR HY

ARTERIAL

THRU ST OR HY

Type Road

550

8790

975

Traff

Count

1989

1989

1989

Traff

Yr

1600

350

30

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

38-017-1004-42401-1
85

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Nitrogen Dioxide

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Fargo

Site Name: FARGO NW

Street Address: 4266 40TH AVE NORTH

MSA: Fargo-Moorhead,ND-MN

County: Cass UAR: FARGO-MOORHEAD, ND-MN

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: MOBILE

Meas. Scale: URBAN SCALE Location Setting: SUBURBAN

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

19980527

Begin Date End Date

DATES OF OPERATION

MAX PRECURSOR EMISSIONS

IMPACT

POPULATION EXPOSURE

Monitor Objective Type

FARGO-MOORHEAD, ND-MN

UAR Name

Fargo-Moorhead,ND-MN

MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19980527

19980527

19980527

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

19980527

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19980501

19980501

19980501

Date Met

REGULATION INFORMATION

19TH AVE N.

INTERSTATE 94

COUNTY 20

Street Name

THRU ST OR HY

ARTERIAL

THRU ST OR HY

Type Road

550

8790

975

Traff

Count

1989

1989

1989

Traff

Yr

1600

350

30

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

38-017-1004-42602-1
86

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM-Fine

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Bismarck

Site Name: BISMARCK RESIDENTIAL

Street Address: 1810 N 16TH STREET

MSA: Bismarck,ND

County: Burleigh UAR: BISMARCK, ND

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: AREA

Meas. Scale: URBAN SCALE Location Setting: SUBURBAN

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

20051005

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

Monitor Objective Type

BISMARCK, ND

UAR Name MSA Name CMSA Name

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20051005

20051005

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20051005

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20051005

20051005

20051005

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-015-0003-88501-3
87

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM-Fine

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070507

Owner: North Dakota Fargo

Site Name: FARGO NW

Street Address: 4266 40TH AVE NORTH

MSA: Fargo-Moorhead,ND-MN

County: Cass UAR: FARGO-MOORHEAD, ND-MN

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: POINT

Meas. Scale: URBAN SCALE Location Setting: SUBURBAN

Probe Location: GROUND LEVEL SUPPORT Horizontal Distance (m):

Probe Height (m): 2.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

20000101

Begin Date

20011230

End Date Dist.(m)

Y

Primary?

COLLOCATION INFORMATION

19990101

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

SOURCE ORIENTED

Monitor Objective Type

FARGO-MOORHEAD, ND-MN

FARGO-MOORHEAD, ND-MN

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

Inter-Mountain Laboratory Sheridan, WY

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19990101

19990101

19990101

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

19990101

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19990101

19990101

19990101

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-017-1004-88101-1
88

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Nitrogen Dioxide

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: TRNP-NU

Street Address: 229 SERVICE RD., WATFORD CITY

MSA: Not in a MSA

County: McKenzie UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

20010801

Begin Date End Date

DATES OF OPERATION

GENERAL/BACKGROUND

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20010801

20010801

20010801

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20010801

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20010801

20010801

20010801

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-053-0002-42602-1
89

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Sulfur Dioxide

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: LOSTWOOD NWR

Street Address: 8315 HIGHWAY 8, KENMARE

MSA: Not in a MSA

County: Burke UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

20031028

Begin Date End Date

DATES OF OPERATION

REGIONAL TRANSPORT

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

REPORTING

COLLECTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20031028

20031028

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20031028

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20031028

20031028

20031028

Date Met

REGULATION INFORMATION

90TH STREET NW

ND HIGHWAY 8

NDHIGHWAY 8

COUNTY ROAD 11

Street Name

LOCAL ST OR HY

THRU ST OR HY

THRU ST OR HY

LOCAL ST OR HY

Type Road

10

100

100

10

Traff

Count

2002

2002

2002

2002

Traff

Yr

8290

1120

840

13800

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

38-013-0004-42401-1
90

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Sulfur Dioxide

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Bismarck

Site Name: BISMARCK RESIDENTIAL

Street Address: 1810 N 16TH STREET

MSA: Bismarck,ND

County: Burleigh UAR: BISMARCK, ND

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: POINT

Meas. Scale: URBAN SCALE Location Setting: SUBURBAN

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?:

20051003

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

Monitor Objective Type

BISMARCK, ND

UAR Name MSA Name CMSA Name

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20051003

20051003

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20051003

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20051003

20051003

20051003

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-015-0003-42401-1
91

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM10

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: DUNN CENTER

Street Address: 9610 SEVENTH STREET SW

MSA: Not in a MSA

County: Dunn UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

20040908

Begin Date End Date

DATES OF OPERATION

GENERAL/BACKGROUND

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

REPORTING

COLLECTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20040908

20040908

20040908

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20040908

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

City:

MONITORING OBJECTIVES

38-025-0003-81102-3
92

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM-Fine

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070507

Owner: North Dakota Bismarck

Site Name: BISMARCK RESIDENTIAL

Street Address: 1810 N 16TH STREET

MSA: Bismarck,ND

County: Burleigh UAR: BISMARCK, ND

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: POINT

Meas. Scale: URBAN SCALE Location Setting: SUBURBAN

Probe Location: GROUND LEVEL SUPPORT Horizontal Distance (m):

Probe Height (m): 3.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

20060125

Begin Date End Date

2

Dist.(m)

N

Primary?

COLLOCATION INFORMATION

20060125

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

Monitor Objective Type

BISMARCK, ND

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

Inter-Mountain Laboratory Sheridan, WY

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20060125

20060125

20060125

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20060125

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

City:

MONITORING OBJECTIVES

38-015-0003-88101-2
93

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM-Fine

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Beulah

Site Name: BEULAH NORTH

Street Address: 6024 HIGHWAY 200

MSA: Not in a MSA

County: Mercer UAR: NOT IN AN URBAN AREA

Project Type: SOURCE-ORIENTED AMBIENT SURVEILLANCE Dominant Source: AREA

Meas. Scale: URBAN SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

ND UNCLASSIFIED NOT

SPECIFIED

Pollutant Area Name Worst Site Type

Community 

Monitoring Zone

Spatial 

Average Ind

Schedule

Exemption

Applicable

NAAQS Ind

20001011

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20001011

20001011

20001011

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20001011

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20001011

20001001

20001001

Date Met

REGULATION INFORMATION

HIGHWAY 200

COUNTY ROAD

CITY STREET

Street Name

THRU ST OR HY

LOCAL ST OR HY

THRU ST OR HY

Type Road

1000

100

250

Traff

Count

1998

1998

1998

Traff

Yr

32

1000

3200

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

POLLUTANT AREA INFORMATION

38-057-0004-88501-3
94

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Ozone

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: HANNOVER

Street Address: 1575 HIGHWAY 31

MSA: Not in a MSA

County: Oliver UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: URBAN SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 3.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

19880323

Begin Date End Date

DATES OF OPERATION

SOURCE ORIENTED

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19880323

19880323

19880323

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

19880323

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19880301

19880301

19880301

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-065-0002-44201-1
95

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM-Fine

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: HANNOVER

Street Address: 1575 HIGHWAY 31

MSA: Not in a MSA

County: Oliver UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: POINT

Meas. Scale: URBAN SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 2.0

Sample Residence Time: Unrestricted Air FLow?: Y

20020917

Begin Date End Date

DATES OF OPERATION

SOURCE ORIENTED

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20020917

20020917

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20020917

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

City:

MONITORING OBJECTIVES

38-065-0002-88501-3
96

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Nitrogen Dioxide

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: LOSTWOOD NWR

Street Address: 8315 HIGHWAY 8, KENMARE

MSA: Not in a MSA

County: Burke UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

20031028

Begin Date End Date

DATES OF OPERATION

REGIONAL TRANSPORT

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20031028

20031028

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20031028

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20031028

20031028

20031028

Date Met

REGULATION INFORMATION

90TH STREET NW

ND HIGHWAY 8

NDHIGHWAY 8

COUNTY ROAD 11

Street Name

LOCAL ST OR HY

THRU ST OR HY

THRU ST OR HY

LOCAL ST OR HY

Type Road

10

100

100

10

Traff

Count

2002

2002

2002

2002

Traff

Yr

8290

1120

840

13800

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

38-013-0004-42602-1
97

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Sulfur Dioxide

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: TRNP-NU

Street Address: 229 SERVICE RD., WATFORD CITY

MSA: Not in a MSA

County: McKenzie UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

SITE RESTARTED AUG 8, 2001

MONITOR COMMENT

19800101

20010801

Begin Date

19980630

End Date

DATES OF OPERATION

GENERAL/BACKGROUND

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

ANALYZING

COLLECTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19800101

19800101

19800101

20010801

20010801

Begin Date

19980630

19980630

End Date

AGENCY ROLES

SLAMS

Monitor Type

19800101

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19800101

19800101

19800101

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-053-0002-42401-1
98

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Ozone

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: DUNN CENTER

Street Address: 9610 SEVENTH STREET SW

MSA: Not in a MSA

County: Dunn UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

*

MONITOR COMMENT

19791001

19981214

Begin Date

19890430

End Date

DATES OF OPERATION

GENERAL/BACKGROUND

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

COLLECTING

REPORTING

ANALYZING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19791001

19791001

19791001

Begin Date End Date

AGENCY ROLES

OTHER

SLAMS

Monitor Type

19791001

19800101

Begin Date

19791231

End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19800101

19800101

19800101

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-025-0003-44201-1
99

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM10

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Beulah

Site Name: BEULAH NORTH

Street Address: 6024 HIGHWAY 200

MSA: Not in a MSA

County: Mercer UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: URBAN SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

20060717

Begin Date End Date Dist.(m)

Y

Primary?

COLLOCATION INFORMATION

20060717

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

REPORTING

ANALYZING

COLLECTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20060717

20060717

20060717

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20060717

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

City:

MONITORING OBJECTIVES

38-057-0004-81102-3
100

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Sulfur Dioxide

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: DUNN CENTER

Street Address: 9610 SEVENTH STREET SW

MSA: Not in a MSA

County: Dunn UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?:

*

MONITOR COMMENT

19791001

Begin Date End Date

DATES OF OPERATION

GENERAL/BACKGROUND

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

COLLECTING

REPORTING

ANALYZING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19791001

19791001

19791001

Begin Date End Date

AGENCY ROLES

OTHER

SLAMS

Monitor Type

19791001

19800101

Begin Date

19791231

End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19800101

19800101

19800101

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-025-0003-42401-1
101

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Sulfur Dioxide

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: HANNOVER

Street Address: 1575 HIGHWAY 31

MSA: Not in a MSA

County: Oliver UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: AREA

Meas. Scale: URBAN SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 3.0 Surrogate?: Vertical Distance (m):

Sample Residence Time: Unrestricted Air FLow?: Y

19880323

Begin Date End Date

DATES OF OPERATION

SOURCE ORIENTED

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

19880323

19880323

19880323

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

19880323

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

19880301

19880301

19880301

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-065-0002-42401-1
102

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM10

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: LOSTWOOD NWR

Street Address: 8315 HIGHWAY 8, KENMARE

MSA: Not in a MSA

County: Burke UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: POINT

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

20031028

Begin Date End Date

DATES OF OPERATION

REGIONAL TRANSPORT

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

REPORTING

COLLECTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20031028

20031028

20031028

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20031028

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Short Term Satisfied

Regulation

Y

Y

Y

Y

Met?

20031028

20031028

20031028

20031028

Date Met

REGULATION INFORMATION

90TH STREET NW

ND HIGHWAY 8

NDHIGHWAY 8

COUNTY ROAD 11

Street Name

LOCAL ST OR HY

THRU ST OR HY

THRU ST OR HY

LOCAL ST OR HY

Type Road

10

100

100

10

Traff

Count

2002

2002

2002

2002

Traff

Yr

8290

1120

840

13800

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

38-013-0004-81102-3
103

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM-Fine

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: LOSTWOOD NWR

Street Address: 8315 HIGHWAY 8, KENMARE

MSA: Not in a MSA

County: Burke UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: POINT

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

20031028

Begin Date End Date

DATES OF OPERATION

REGIONAL TRANSPORT

Monitor Objective Type

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

ANALYZING

REPORTING

COLLECTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20031028

20031028

20031028

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20031028

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20031028

20031028

20031028

Date Met

REGULATION INFORMATION

90TH STREET NW

ND HIGHWAY 8

NDHIGHWAY 8

COUNTY ROAD 11

Street Name

LOCAL ST OR HY

THRU ST OR HY

THRU ST OR HY

LOCAL ST OR HY

Type Road

10

100

100

10

Traff

Count

2002

2002

2002

2002

Traff

Yr

8290

1120

840

13800

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

38-013-0004-88501-3
104

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM-Fine

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Fargo

Site Name: FARGO NW

Street Address: 4266 40TH AVE NORTH

MSA: Fargo-Moorhead,ND-MN

County: Cass UAR: FARGO-MOORHEAD, ND-MN

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: POINT

Meas. Scale: URBAN SCALE Location Setting: SUBURBAN

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

ND UNCLASSIFIED NOT

SPECIFIED

Pollutant Area Name

Classified as

having the highest

PM-10 concentration

and is expected to

monitor at

recommended

sampling frequency.

Worst Site Type

Community 

Monitoring Zone

Spatial 

Average Ind

Schedule

Exemption

Applicable

NAAQS Ind

20000608

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

SOURCE ORIENTED

Monitor Objective Type

FARGO-MOORHEAD, ND-MN

FARGO-MOORHEAD, ND-MN

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20000608

20000608

20000608

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20000608

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20000608

20000601

20000601

Date Met

REGULATION INFORMATION

19TH AVE N.

INTERSTATE 94

COUNTY 20

Street Name

THRU ST OR HY

ARTERIAL

THRU ST OR HY

Type Road

550

8790

975

Traff

Count

1989

1989

1989

Traff

Yr

1600

350

30

Dist. to Road (m)

TANGENT ROAD INFORMATION

City:

MONITORING OBJECTIVES

POLLUTANT AREA INFORMATION

38-017-1004-88501-3
105

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM10

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Fargo

Site Name: FARGO NW

Street Address: 4266 40TH AVE NORTH

MSA: Fargo-Moorhead,ND-MN

County: Cass UAR: FARGO-MOORHEAD, ND-MN

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: POINT

Meas. Scale: URBAN SCALE Location Setting: SUBURBAN

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

ND UNCLASSIFIED NOT

SPECIFIED

Pollutant Area Name

Classified as

having the highest

PM-10 concentration

and is expected to

monitor at

recommended

sampling frequency.

Worst Site Type

Community 

Monitoring Zone

Spatial 

Average Ind

Schedule

Exemption

Applicable

NAAQS Ind

20040628

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

Monitor Objective Type

FARGO-MOORHEAD, ND-MN

UAR Name MSA Name CMSA Name

ANALYZING

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20040628

20040628

20040628

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20040628

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20040628

20040628

20040628

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

POLLUTANT AREA INFORMATION

38-017-1004-81102-3
106

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM10

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Not in a city

Site Name: TRNP-NU

Street Address: 229 SERVICE RD., WATFORD CITY

MSA: Not in a MSA

County: McKenzie UAR: NOT IN AN URBAN AREA

Project Type: BACKGROUND SURVEILLANCE Dominant Source: POINT

Meas. Scale: REGIONAL SCALE Location Setting: RURAL

Probe Location: TOP OF BUILDING Horizontal Distance (m):

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

ND UNCLASSIFIED NOT

SPECIFIED

Pollutant Area Name

Classified as

having the highest

PM-10 concentration

and is expected to

monitor at

recommended

sampling frequency.

Worst Site Type

Community 

Monitoring Zone

Spatial 

Average Ind

Schedule

Exemption

Applicable

NAAQS Ind

20040616

Begin Date End Date

DATES OF OPERATION

GENERAL/BACKGROUND

REGIONAL TRANSPORT

Monitor Objective Type

NOT IN AN URBAN AREA

NOT IN AN URBAN AREA

UAR Name MSA Name CMSA Name

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20040616

20040616

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20040616

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20040616

20040616

20040616

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

POLLUTANT AREA INFORMATION

38-053-0002-81102-3
107

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: PM10

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Bismarck

Site Name: BISMARCK RESIDENTIAL

Street Address: 1810 N 16TH STREET

MSA: Bismarck,ND

County: Burleigh UAR: BISMARCK, ND

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: AREA

Meas. Scale: URBAN SCALE Location Setting: SUBURBAN

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?: Y

ND UNCLASSIFIED NOT

SPECIFIED

Pollutant Area Name

Classified as

having the highest

PM-10 concentration

and is expected to

monitor at

recommended

sampling frequency.

Worst Site Type

Community 

Monitoring Zone

Spatial 

Average Ind

Schedule

Exemption

Applicable

NAAQS Ind

20051001

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

Monitor Objective Type

BISMARCK, ND

UAR Name MSA Name CMSA Name

REPORTING

COLLECTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20051001

20051001

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20051001

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20051001

20051001

20051001

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

POLLUTANT AREA INFORMATION

38-015-0003-81102-3
108

May. 18, 2007

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Parameter Measured: Nitrogen Dioxide

North Dakota

Monitor ID:

Date of Latest Collection: 20070331 Last Updated: 20070430

Owner: North Dakota Bismarck

Site Name: BISMARCK RESIDENTIAL

Street Address: 1810 N 16TH STREET

MSA: Bismarck,ND

County: Burleigh UAR: BISMARCK, ND

Project Type: POPULATION-ORIENTED SURVEILLANCE Dominant Source: MOBILE

Meas. Scale: URBAN SCALE Location Setting: SUBURBAN

Probe Location: TOP OF BUILDING Horizontal Distance (m): 0.0

Probe Height (m): 4.0 Surrogate?: Vertical Distance (m): 1.0

Sample Residence Time: Unrestricted Air FLow?:

20051003

Begin Date End Date

DATES OF OPERATION

POPULATION EXPOSURE

Monitor Objective Type

BISMARCK, ND

UAR Name MSA Name CMSA Name

COLLECTING

REPORTING

Agency Role

North Dakota State Department Of Health

North Dakota State Department Of Health

Agency Name

20051003

20051003

Begin Date End Date

AGENCY ROLES

SLAMS

Monitor Type

20051003

Begin Date End Date Action Type Action Reason

MONITOR TYPE INFORMATION

Quality Assurance Criteria Met

Reference Method Used

Siting Criteria Met

Regulation

Y

Y

Y

Met?

20051003

20051003

20051003

Date Met

REGULATION INFORMATION

City:

MONITORING OBJECTIVES

38-015-0003-42602-1
109

Appendix D

Public Comments