# Annual Report

North Dakota

A mbient Monitoring

Network Plan

200 8ii



# Annual Report

North Dakota

Ambient Monitoring

Network Plan

200 8

June 200 8

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

- 1947iii 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 PM 10 Network Analysis

................................ .............. 27

2.4.4 PM fine 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 (SO 2 )

................................ ................... 33

3.2 Nitrogen Dioxide (NO 2 )

................................ ................. 33

3.3 Ozone (O 3 )

................................ ......................... 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



# ................................ ......................... 109iv LIST OF TABLES

Table Page

Table 1 AAQM Network Description

................................ ................................ ................ 5

Table 2 Major SO 2 Sources

................................ ................................ ................................ 7

Table 3 Sulfur Dioxide

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

Table 3A Trace Level Sulfur Dioxide

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

Table 4 SO 2 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 PM 10 Sources

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

Table 10 FRM PM fine Particulates

................................ ................................ ...................... 26

Table 11 Continuous PM 10

................................ ................................ ................................ .. 27

Table 12 Continuous PM fine

................................ ................................ ................................ 27

Table 1 3 Major CO Sources

................................ ................................ ................................ 30

Table 14 Major Air Toxics Sources

................................ ................................ .................... 32v 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 SO 2 Detectable

................................ ................................ .. 13

Figure 4 SO 2 Maximum 1

- Hour Concentrations

................................ ............................. 13

Figure 5 SO 2 Maximum 3

- Hour Concentrations

................................ ............................. 14

Figure 6 SO 2 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 NO 2 Detectable

................................ ................................ . 19

Figure 9 NO 2 Annual Average Concent rations

................................ ............................... 19

Figure 10 Major VOC Sources

................................ ................................ .......................... 21

Figure 11 Monthly 4 th Highest Ozone Concentrations

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

Figure 12 Annual 4 th Highest Ozone Concentrations

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

Figure 13 Major PM 10 Sources

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

Figure 13A Annual PM Emissions

................................ ................................ ....................... 26

Figure 14 Major CO Sources

................................ ................................ ............................. 30

Figur e 15 M ajor Air Toxics Sources

................................ ................................ ................. 321

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 a mbient air quality in North Dakota is

maintained in accordance with the levels established by the s tate and f ederal Ambient Air Quality

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

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

ambient air quality monitors and requires three major industrial pollution sources to conduct source

specific ambient air quality monitoring. There are 16 ambient air quality monitori ng 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 mai ntains 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 s tate's air quality monitor ing effort, the U.S. Environmental

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

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

40 CFR 58.10, are to (1) det ermine 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 pri mary 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 multi

pollutant sites. NCore Level 3 sites are single pollutant sites. Each s tate 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 Netw ork. 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 T ribal Networks site designations still apply. The remaining six

d epartment

- 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 moni toring

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 reasonab ly 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 a s 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 la nd 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 appro priate 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 monit ors 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 s tate: eight are

source

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

Park, i s a part of the National Park Service’s (NPS) network. The d epartment, at the NPS’s

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

sampler. The NPS also provides a continuous PM fine analyzer, which the departm ent operates4

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 population

oriented 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 p opulation 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

- to

construct and permits

- to

- operate for projects located in or near population centers in the e astern

part of the s tate. 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 PM fine program,

the d epartment 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 concentra

tions of air contaminants in areas remote from urban sources and generally are sited using the

regional spatial scale. This is true for NO 2 despite the fact that the regional spatial scale is not

normally used for NO 2 monitoring. Once a specific location is selected for a site, th e site is

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

A, C, D and E.

1.3 Monitoring Objectives

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

potential for violating either s tate or f ederal Ambient Air Quality Standards. To accomplish this

objective, the d epartment operates SLAMS sites at selected locations around the s tate. Table 1

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

photographs, and a site map taken from Google Earth TM 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 neede d to support the

visibility regulations.5 Table 1

AAQM Network Description

Site Name

AQS Site # Parameter

Monitored 1 Monitoring

Objective 2

1 Beulah North

380570004 SO 2 , NO 2 , O 3 , NH 3 , MET

cont. PM fine , PM 10 Manual PM fine Population Exposure

&

Significant Source

2 Bismarck Residential

380150003 SO 2 , NO 2 , O 3 , MET

cont. PM fine , PM 10 Manual PM fine Population Exposure

3 Dunn Center

380250003 SO 2 4 , NO 2 , O 3 , MET

cont. PM fine , cont. PM 10 General Background

4 Fargo NW

380171004 SO 2 , NO 2 , O 3 , MET

cont. PM fine , PM 10 Manual PM fine PM fine Speciation Population Exposure

Population Exposure

Population Exposure

Population Exposure

5 Hannover

380650002 SO 2 , NO 2 , O 3 , MET

cont. PM fine Source Impact

6 Lostwood NWR

380130004 SO 2 4 , NO 2 , O 3 , MET,

cont. PM fine , cont. PM 10 PM fine Speciation (IMPROVE) General Background

&

Significant Source

7 TRNP

- NU

380530002 SO 2 4 , NO 2 , O 3 , MET

cont. PM fine , PM 10 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 SO 2 was replaced with a SO 2 Trace Level Analyzer.

Figure 1 North Dakota Ambient Air Quality Monitoring Sites6

2.0 Ambient Air Monitoring Network Coverage

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

including PM fine and 8

- hour o zone. The seven d epartment

- operated ambient monitoring sites

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

and f ederal ambient air quality standards and support dispersion modeling activities relating

to

, first, visibility/re gional 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 (SO 2 ). These sources inclu de 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, SO 2 is one of the Department's primary

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

visibility improvement over time.

2.1.1 Point Sources

The major SO 2 point sources (>100 T ons P er Y ear or TPY ) based on 2007 emissions are

listed i n 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 SO 2 emissions

from point sources and three sub

- categories for 1984 through 200 7

.

2.1.2 Other Sources

The western part of the s tate has a number of potential SO 2 sources associated with the

develop ment of oil and gas. These sources include indi vidual oil/gas wells, oil storage

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

First, these sources may directly emit significant amounts of hydrogen sulfide (H 2 S) to the

ambient air (see Section 2.7). Second, flaring the H 2 S from these sources may create

significant c oncentrations of SO 2 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 SO 2 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 Sources8

2.1.3 Monitoring Network

The SO 2 monitoring sites are shown on Figure 2. The most significant c hange to the

network in 200 7 is that tr ace level analyzer s were installed at Dunn Center, TRNP

– NU,

and Lostwood . The difference between a standard SO 2 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 gen erating plants in the

west

- central part of the s tate. Tables 3 and 3A show the 200 7 annual SO 2 data summaries;

Tables 4 and 4A show the 5

- minute data summaries. There were no exceedances of either

s tate or f ederal SO 2 standards.

2.1.4 Network Analysis

Ten major SO 2 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. A lso , Lostwood NWR is within 45 miles of four major sources: t wo natural gas

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

Figure 2A Annual Sulfur Dioxide Emissions9

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

Boundary Dam Power Station

, are locate d 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 bee n the case. There have been possible short

- term influences, but no significant long

term impact by these sources combined has been demonstrate d in the data. Figures 3, 4, 5

and 6 present the following for the Department

- operated sites : ( 1) the percentag e of data

greater than th e 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 dow nwind

direction), the industry sites are not reviewed for particular long

- term trends.

The best

- long term indicator of any change in the amount of SO 2 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 t he dat a 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 su bstituted 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 PERI OD 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

SA MPLING 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 Po wer 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 we re built and wel ls 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 m ajor 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 st ro nger indicator. Dunn

Center, which is on the easter n 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 grea ter than the MDV;

then, the percentage decrease d from 1993 to 200 7 . 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 s ite s 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

concent ration graphs (see Figures 4, 5 and 6, respectively).13 Figure 3 Percentage of Time SO 2 Detectable

Figure 4 SO 2 Maximum 1

- Hour Concentrations14 Figure 5 SO 2 Maximum 3

- Hour Concentrations

Figure 6 SO 2 Maximum 24

- Hour Concentrations15

2.2 Oxides of Nitrogen

“ Oxides of Nitrogen ” (NO

x ) is the term used to represent nitric oxide (NO) plus nitrogen

dioxide (NO 2 ). NO 2 i s 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 NO

x 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 NO

x point sour ces in North Dakota are associated with

coal

- fired steam

- powered electrical generating plants in t he west

- central portion of the s tate

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

of the s tate. Figure 7A shows the contribution of point sources to the total NO X emissions.

The “Point Sources” category consists of u tility b oilers (power plant boilers) and oil and gas

wells.

2.2.2 Area Sources

Another source of NO X is automo bile emissions. North Dakota has no significant urbanized

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

1,000,000 people

. However, currently opera t in g NO analyzers cannot be terminated without

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

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

refineries, natural ga s processing plants and agricultur al processing plants.

2.2.3 Monitoring N etwork

The Department currently operates s even NO/NO 2 /NO

x analyzers. Table 6 shows the 200 7

NO 2 data summaries. The measured NO 2 values are quite low. From Figure 7 it can be

seen that NO/NO 2 /NO

x analyzers, except for Dunn Center and TRNP

- NU, are well placed

with respect to the major NO

x sources: TRNP

- NU is defined as a background and long

range transport/ welfare

- related site

.16 TABLE 5

Major NO

x 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 380070001917 Figure 7A Annual Oxides of Nitrogen Emissions Figure 7 Major Oxides of Nitrogen Sources18 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

N ine of the 10 largest NO X sources in the s tate are within 45 miles of the Beulah and

Hannover monitoring sites. Figures 8 and 9 show the trends for the d epartment

- operated

sites for 1980

- 200 7

.

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 NO 2 averages follow the reported

NO X emissions shown in Figure 7A.19 Figure 8 Percentage of Time NO 2 Detectable

Figure 9 NO 2 Annual Average Concentrations20

2.3 Ozone

Unlike most other pollutants, ozone (O 3 ) is not emitted directly into the atmosphere but results

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

ni trogen (NO

x ), and solar radia tion. Both VOC and NO

x are emitted directly into the

atmosphere. Since solar radiation is a major factor in O 3 production, O 3 concen trations are

known to peak in summer months. 40 CFR 58 defines the O 3 monitoring season fo r North

Dakota as May 1 through September 30. However, O 3 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) o f VOC as calculated from the most recent

emissi on inventories reported to the d epartment 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 NO

x 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 O 3 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 moni toring, the 4 th highest 8

- hour

average concentration must be at least 68 parts per billion.

2.3.3 Monitoring Network

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

and Figur e 10 for locat ions. 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 Sources22 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 1 ST 2ND 1ST 2ND 3RD 4 TH #>120 #>80 │ │ │

Beulah

- North 2007 JAN

- DEC 8355 │ 68 66 │ 62 6 1 60 59 │ │ │ │

Bismarck Residential 2007 JAN

- DEC 8622 │ 70 67 │ 62 62 6 0 5 8 │ │ │ │

Dunn Center 2007 JAN

- DEC 8282 │ 67 67 │ 59 59 5 8 5 8 │ │ │ │

Fargo NW 2007 JAN

- DEC 8274 │ 65 63 │ 6 2 57 5 6 5 5 │ │ │ │

Hannover 2007 JAN

- DEC 8695 │ 69 68 │ 64 60 59 59 │ │ │ │

Lostwood NWR 2007 JAN

- DEC 8710 │ 71 67 │ 64 6 2 6 1 59 │ │ │ │

TRNP

- NU 2007 JAN

- DEC 8719 │ 76 75 │ 7 1 69 6 7 6 5 │ │ │ │

* 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 s tate. 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, o ne would expect to see a diversity of ozone concentrations. On the

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

- hour

concentrations whether view monthly or annually. Since 1980, only four 8

- hour averages have

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

8

- hour concentrations: for all sites, the difference among the 4 th 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 4 th Highest Ozone Concentrations

Figure 12 Annual 4 th Highest 8

- HR Ozone Concentrations24

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: PM 10 and PM fine . The PM 10

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

designated as PM 10 . The PM fine 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 PM

coarse . This subgroup is made up of PM 10

– PM fine . Specific health effects have

been identified for both the PM

co a rse and PM fine . The EPA is working with equipment

manufacturers to develop a continuous analyzer and a manual sampler to c ollect 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 PM 10

and PM fine analyzers are scheduled for replacement and funding is available.

2.4.1 Sources

The major PM 10 point sources (>100 TPY) are listed in T able 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 PM 10 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 PM 10 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 PM 10 analyzers, three manual PM fine samplers,

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

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

continuous PM fine data summaries, respectively.25 TABLE 9

Major PM 10 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 PM 10 Sources26 TABLE 10

COMPARISON OF AIR QUALITY DATA WITH

THE NORTH DAKOTA AMBIENT AIR QUALITY STANDARDS *

POLLUTANT : FRM PM fine Particulates (  g/m 3 )

M A X I M A

SAMPLING NUM ARITH %

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

Beulah

- North 2007 JAN

- DEC 58 2.3 │ 16.4 13.5 11.8 │ 6.6 100.0 │ │

Bismarck Resi dential 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 3 5  g/m 3

. 2) Annual: 3

- year average not to exceed 15  g/m 3

.

*** Less than 80% of the possible samples (data) were collected. Figure 13A Annual PM Emissions27 Table 11

COMPARISON OF AIR QUALITY DATA WITH

THE NORTH DAKOTA AMBIENT AIR QUALITY STANDARDS *

POLLUTANT : Inhalable Continuous PM 10 (  g/m 3 )

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 3 2.5 │ 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/m 3 maximum averaged over a 24

- hour period with no more than one expected exceedance per year.

2) 50  g/m 3 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 PM fine (  g/m 3 )

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 1 3.3 │ 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/m 3

. 2) Annual: 3

- year average not to exceed 15  g/m 3

.

2.4.3 PM 10 Network Analysis

PM 10 and smaller particles are of concern mainly because of th eir health effects.

C ontinuous PM 10 analyzers are install ed at Beulah, Bismarck, Dunn Center, Fargo,

Lostwood NWR , and TRNP

– NU. The primary purpose for the continuous PM 10

analyzers is to be used with the continuous PM fine analyzers to determine the PM

coarse

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

standards.28

2.4.4 PM fine Network

The manual P M fine 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 operate s on a 1

- in

- 6 day schedule. Continuous PM fine 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 Tr ends Network sampler in Fargo. The

data collected by th is 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. Nor th Dakota does not have

sufficient population with the corresponding traffic congestion and

geographical/meteorological conditions to create significant CO emission problems.

However, there are sev eral stationary sources in the s tate that emit more than 1 00 TPY of

CO.

2.5.1 Sources

The major stationary CO sources (>100 TPY) are listed in Table 1 3 . 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 SO 2 and

NO

x . However, the corresponding CO levels from these sources ar e 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

h ave 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 L evel

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 380070001931

2.6 Lead

Through prior sampling efforts, the d epartment has determined that the s tate has low lead

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

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

populations greater than 500,000, resulted in terminating th e lead monit oring 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 Federa l Ambient Air Quality Standard exists for hydrogen sulfide (H 2 S), the

s tate of North Dakota has developed H 2 S standards.

2.7.1 Sources

H 2 S emissions of concern stems almost totally from the oil and gas operations in the

western part of the s tate; 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 H 2 S emission source s.

2.7.2 Monitoring Network

Currently there are no s tate or industry H 2 S monitoring sites.

2.8 Air Toxics

Currently there are no s tate or f ederal air toxics monitoring sites.

2.8.1 Sources

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

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

2.8.2 Monitoring Network

Currently there are no s tate or industry air toxics monitoring sites. The h istoric raw data

and associated summaries are available in EPA’s A ir Quality S ystem

.

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 Sources33

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 we stern part of the s tate (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 (SO 2 )

Neither the state nor f

ederal standards were exceeded at any monitoring site. The maximum

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

s tandard 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 SO 2 5

- minute standard currently in effect. The maximum 5

- minute average was

155 ppb.

3.2 Nitrogen Dioxide (NO 2 )

Neither the s tate nor f

ederal 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 (O 3 )

Neither the state nor f

ederal standard was exceeded during the year. The 1

- hour maximum and

highest 4 th 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 4 th highest 8

- hour

– 6 5

ppb (81 .3%).34

3.4 Inhalable Particulates

Neither the state nor f

ederal PM 10 standards were exceeded during the year. The maximum

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

PM 10 standa rd are as follows: 24

- hour

– 79 .1 μg/m 3 (52

. 7 %); annual

– 1 5.0 μg/m 3 (30.0 %).

The f ederal PM fine 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/m 3 ( 55.7 %); annual FRM

– 7.5 μg/m 3 ( 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 Descriptions36

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: m odeling 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 Earth TM . ( http://free.download.earth.googlepages.com/ ) W ith this tool,

one can enter latitude a nd longitude to get either an expanded view or close

- up view of each

monitoring site.

For both of these tools

, a high

- speed I nternet 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 d epartment’s ambient monitoring network to meet

the six required monitoring objectives. When this si te was established

, it was decided to enhance the site

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

This site is one of the required PM fine monitoring site s for North Dakota

Gas/Particulate paramet ers:

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

PM fine 24

- hour Gravimetric 1/6 Population Exposure Urban

PM fine PM fine SCC W/ No Correction

TEOM Gravimetric 40 deg. Celsius Continuous Population Exposure Urban

PM 10 PM 10 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 PM fine data may be compared to the a nnual NAAQS.38 Site Pictures: Beulah North

North South

East West

Looking Northeast Looking Northwest39 Beulah

North40

Site: Bismarck Residential Station Type: SLAMS

AQS#: 38

- 015

- 0003 MSA: 1010

Address: 1810 N 16 th Street, Bismarck

Latitude: +46.825425 Longitude:

- 100.768210

Site Description: This site is located in the second largest metropolitan are a in the s tate.

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

pre ssure) 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

PM fine 24

- hour Gravimetric 1/6 Population Exposure Urban

PM fine PM fine SCC W/ No Correction

TEOM Gravimetric 40 deg. Celsius Continuous Population Exposure Urban

PM 10 PM 10 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 pla ns to move or remove this site.

The manual PM fine data may be compared to the a nnual NAAQS.41 Site Pictures: Bismarck Residential

North East

West Looking Northwest

South Looking Southeast42 Bismarck

Residential43

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

dioxi de, and PM fine 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

PM fine PM fine SCC W/ No Correction

TEOM Gravimetric 40 deg. Celsius Continuous General/Background Urban

PM 10 PM 10 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

N orth West

East South

Looking Northwest Looking Northeast45 Dunn Center46 Site Name: Fargo NW Station Type: SLAMS (required)

AQS#: 38

- 017

- 1004 MSA: 2520

Address: 4266 40 th Avenue North, Fargo

Latitude: +46.933754 Longitude:

- 96.855350

Site Description: This site is one of EPA’s 54 Speciation Trends Network sites, the s tate’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, cal ibration and validation. An NCORE Level II site is

required to have trace level analyzers for sulfur dioxide, carbon monoxide, and NO Y (total reactive

nitrogen) operati onal 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

PM fine 24

- hour Gravimetric 1/3 Population Exposure Urban

PM fine PM FINE SCC W/ No Correction

TEOM Gravimetric 40 deg. Celsius Continuous Population Exposure Urban

PM 10 PM 10 TEOM Gravimetric 50° Celsius Continuous Population Exposure Urban

PM fine 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 pla ns to move or remove this site.

The manual PM fine data may be compared to the annual NAAQS47 Site Pictures: Fargo NW

North West

East South

Looking Northeast Looking West48 Fargo NW49

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

- Mercer

McLean c ounty 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

PM fine PM fine 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 No r theast

Site Location51 Hannover52

Site Name: Lostwood NWR Station Type: SLAMS

AQS#: 38

- 013

- 0004 MSA: 0000

Address: 8315 Highway 8

, Kenmare

Latitude: +48.641 930 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 use d with the other ambient data collected here to evaluate long

- range

transport of aerosols a ffecting regional haze/visibility.

Gas/Particulate parameters:

Parameter Sampling &

Analysis Method Operating

Sc hedule 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

PM fine PM fine SCC W/ No Correction

TEOM Gravimetric 40 deg. Celsius Continuous Regional Transport Regional

PM 10 PM 10 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 L ooking North54 Lostwood55

Site Name: TRNP

- NU Station Type: SLAMS (required)

AQS#: 38

- 053

- 0002 MSA: 0000

Address: 229 Service Road

, Watford City

Latitude: +47.58 1200 Longitude:

- 103.299 500

Site Description: Th is site is located in Theodore Roosevelt National Park

– North Unit

and is one of three key sites in the d epartment’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

PM fine PM fine SCC W/ No Correction

TEOM Gravimetric 40 deg. Celsius Continuous General/Background

Regional Transport Regional

PM 10 PM 10 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 North e ast57 TRNP

- NU

### Appendix B

Detailed Site Descriptions59

This appendix is a listing printed from the EPA’s Air Quality System (AQS) database. Please not e that

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

the display in Appendix A. This is a problem with Google Earth TM , not the coordinates in AQS.60 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

AIR QUALITY SYSTEM

May. 18, 2007 SITE DESCRIPTION REPORT

North Dakota 38

- 013

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

8315 HIGHWAY 8, KENMARE Street Address:

19990101 Date Established: Date Terminated: 20060814 Last Updated:

HQ Eval . Date:

DENVER EPA Region:

Burke County:

Not in a MSA MSA: Not in a CMSA CMSA: Not in a city City:

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

Local Region:

NOT IN AN URBAN AREA Urban Area:

Lostwood National Wildlife Refuge Class 1 Area: 58721 Zip Code:

Census Block: Block Group: Census Tract:

Congressional District:

+48.641930 Site Latitude:

13 UTM Zone:

.01 Accuracy: CENTRAL Time Zone:

- 102.401800 Site Longitude:

5390691.44 UTM Northing:

WGS84 Datum: GPS CODE (PSEUDO RANGE) DIFFERENTIAL Coll. Method:

696.0 Vertical Measure(m): 691395.29 UTM Easting:

24000 Scale: POINT Point/Line/Area: MONITORING POINT Location Description:

ON

- SITE MET EQUIP Type Met Site: Met. Site ID:

Dist to Met. Site(m): Direct Met Site: Regional Eval. Date: RURAL Location Setting:

AGRICULTURAL Land Use:

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

HY THRU ST OR HY

THRU ST OR HY

LOCAL ST OR

HY Road Type

N

E

S

W Compass

Sector GPS CODE (PSEUDO RANGE) DIFFERENTIAL Vert Method: NAVD88 Vert Datum .01 Vert Accuracy:

ACTIVE MONITOR TYPES

TANGENT ROADS State:61 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

AIR QUALITY SYSTEM

May. 18, 2007 SITE DESCRIPTION REPORT

North Dakota 38

- 015

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

1810 N 16TH STREET Street Address:

19950501 Date Established: Date Terminated: 20060814 Last Updated:

HQ Eval. Date:

DENVER EPA Region:

Burleigh County:

Bismarck,ND MSA: CMSA: Bismarck City:

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

Local Region:

BISMARCK, ND Urban Area:

Class 1 Area: 58501 Zip Code:

Census Block: Block Group: Census Tract:

Congressional District:

+46.825425 Site Latitude:

14 UTM Zone:

.03 Accuracy: CENTRAL Time Zone:

- 100.768210 Site Longitude:

5187064 UTM Northing:

WGS84 Datum: GPS CODE (PSEUDO RANGE) DIFFERENTIAL Coll. Method:

580.0 Vertical Measure(m): 365130.78 UTM Easting:

0 Scale: POINT Point/Line/Area: MONITORING POINT Location Description:

NWS Type Met Site: Met. Site ID:

3200 Dist to Met. Site(m): S Direct Met Site: Regional Eval. Date: SUBURBAN Location Setting:

RESIDENTIAL Land Use:

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

HY LOCAL ST OR

HY LOCAL ST OR

HY LOCAL ST OR

HY Road Type

S

W

E

N Compass

Sector GPS CODE (PSEUDO RANGE) DIFFERENTIAL Vert Method: NAVD88 Vert Datum .03 Vert Accuracy:

ACTIVE MONITOR TYPES

TANGENT ROADS State:62 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

AIR QUALITY SYSTEM

May. 18, 2007 SITE DESCRIPTION REPORT

North Dakota 38

- 017

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

4266 40TH AVE NORTH Street Address:

19980513 Date Established: Date Terminated: 20060814 Last Updated:

HQ Eval. Date:

DENVER EPA Region:

Cass County:

Fargo

- Moorhead,ND

- MN MSA: CMSA: Fargo City:

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

- MOORHEAD AQCR :

Local Region:

FARGO

- MOORHEAD, ND

- MN Urban Area:

Class 1 Area: 58102 Zip Code:

Census Block: Block Group: Census Tract:

1 Congressional District:

+46.933754 Site Latitude:

14 UTM Zone:

.03 Accuracy: CENTRAL Time Zone:

- 96.855350 Site Longitude:

5199816.62 UTM Northing:

WGS84 Datum: GPS CODE (PSEUDO RANGE) DIFFERENTIAL Coll. Method:

275.0 Vertical Measure(m): 663252.17 UTM Easting:

0 Scale: POINT Point/Line/Area: MONITORING POINT Location Description:

ON

- SITE MET EQUIP Type Met Site: Met. Site ID:

Dist to Met. Site(m): Direct Met Site: Regional Eval. Date: SUBURBAN Location Setting:

AGRICULTURAL Land Use:

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 GPS CODE (PSEUDO RANGE) DIFFERENTIAL Vert Method: NAVD88 Vert Datum .03 Vert Accuracy:

ACTIVE MONITOR TYPES

TANGENT ROADS State:63 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

AIR QUALITY SYSTEM

May. 18, 2007 SITE DESCRIPTION REPORT

North Dakota 38

- 025

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

9610 SEVENTH STREET SW Street Address:

19750701 Date Established: Date Terminated: 20060814 Last Updated:

HQ Eval. Date:

DENVER EPA Region:

Dunn County:

Not in a MSA MSA: Not in a CMSA CMSA: Not in a city City:

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

Local Region:

NOT IN AN URBAN AREA Urban Area:

Class 1 Area: 58626 Zip Code:

Census Block: Block Group: Census Tract:

1 Congressional District:

+47.313200 Site Latitude:

13 UTM Zone:

.03 Accuracy: MOUNTAIN Time Zone:

- 102.527300 Site Longitude:

5242716.42 UTM Northing:

WGS84 Datum: GPS CARRIER PHASE STATIC RELATIVE POSITION Coll. Method:

683.0 Vertical Measure(m): 686888.26 UTM Easting:

0 Scale: POINT Point/Line/Area: MONITORING POINT Location Description:

ON

- SITE MET EQUIP Type Met Site: Met. Site ID:

Dist to Met. Site(m): Direct Met Site: Regional Eval. Date: RURAL Location Setting:

AGRICULTURAL Land Use:

* * 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 GPS CODE (PSEUDO RANGE) DIFFERENTIAL Vert Method: NAVD88 Vert Datum .03 Vert Accuracy:

ACTIVE MONITOR TYPES

TANGENT ROADS State:64 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

AIR QUALITY SYSTEM

May. 18, 2007 SITE DESCRIPTION REPORT

North Dakota 38

- 053

- 0002 Site ID: TRNP

- NU Site Name: Local ID:

229 SERVICE RD., WATFORD CITY Street Address:

19781201 Date Established: Date Terminated: 20060814 Last Updated:

HQ Eval. Date:

DENVER EPA Region:

McKenzie County:

Not in a MSA MSA: Not in a CMSA CMSA: Not in a city City:

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

Local Region:

NOT IN AN URBAN AREA Urban Area:

T. Roosevelt Park (North) Class 1 Area: 58854 Zip Code:

Census Block: Block Group: Census Tract:

Congressional District:

+47.581200 Site Latitude:

13 UTM Zone:

.03 Accuracy: MOUNTAIN Time Zone:

- 103.299500 Site Longitude:

5270936.38 UTM Northing:

NAD83 Datum: GPS CARRIER PHASE STATIC RELATIVE POSITION Coll. Method:

624.0 Vertical Measure(m): 627875.21 UTM Easting:

0 Scale: POINT Point/Line/Area: MONITORING POINT Location Description:

ON

- SITE MET EQUIP Type Met Site: Met. Site ID:

Dist to Met. Site(m): Direct Met Site: Regional Eval. Date: RURAL Location Setting:

AGRICULTURAL Land Use:

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 GPS CODE (PSEUDO RANGE) DIFFERENTIAL Vert Method: NAVD88 Vert Datum 0 Vert Accuracy:

ACTIVE MONITOR TYPES State:65 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

AIR QUALITY SYSTEM

May. 18, 2007 SITE DESCRIPTION REPORT

North Dakota 38

- 057

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

6024 HIGHWAY 200 Street Address:

19981213 Date Established: Date Terminated: 20031212 Last Updated:

HQ Eval. Date:

DENVER EPA Region:

Mercer County:

Not in a MSA MSA: Not in a CMSA CMSA: Beulah City:

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

Local Region:

NOT IN AN URBAN AREA Urban Area:

Class 1 Area: 58571 Zip Code:

Census Block: Block Group: Census Tract:

Congressional District:

+47.298611 Site Latitude:

14 UTM Zone:

.03 Accuracy: MOUNTAIN Time Zone:

- 101.766944 Site Longitude:

5241843 UTM Northing:

WGS84 Datum: GPS CODE (PSEUDO RANGE) DIFFERENTIAL Coll. Method:

630.0 Vertical Measure(m): 290816 UTM Easting:

0 Scale: POINT Point/Line/Area: MONITORING POINT Location Description:

ON

- SITE MET EQUIP Type Met Site: Met. Site ID:

Dist to Met. Site(m): Direct Met Site: Regional Eval. Date: RURAL Location Setting:

AGRICULTURAL Land Use:

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

HY THRU ST OR HY Road Type

N

W

S Compass

Sector GPS CODE (PSEUDO RANGE) DIFFERENTIAL Vert Method: NAVD88 Vert Datum .03 Vert Accuracy:

ACTIVE MONITOR TYPES

TANGENT ROADS State:66 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

AIR QUALITY SYSTEM

May. 18, 2007 SITE DESCRIPTION REPORT

North Dakota 38

- 065

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

1575 HIGHWAY 31 Street Address:

19841004 Date Established: Date Terminated: 20050304 Last Updated:

HQ Eval. Date:

DENVER EPA Region:

Oliver County:

Not in a MSA MSA: Not in a CMSA CMSA: Not in a city City:

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

Local Region:

NOT IN AN URBAN AREA Urban Area:

Class 1 Area: Zip Code:

Census Block: Block Group: Census Tract:

1 Congressional District:

+47.185833 Site Latitude:

14 UTM Zone:

.01 Accuracy: MOUNTAIN Time Zone:

- 101.428056 Site Longitude:

5228457 UTM Northing:

WGS84 Datum: GPS CODE (PSEUDO RANGE) DIFFERENTIAL Coll. Method:

697.0 Vertical Measure(m): 316045 UTM Easting:

0 Scale: POINT Point/Line/Area: MONITORING POINT Location Description:

ON

- SITE MET EQUIP Type Met Site: Met. Site ID:

Dist to Met. Site(m): Direct Met Site: Regional Eval. Date: RURAL Location Setting:

AGRICULTURAL Land Use:

* 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 GPS CODE (PSEUDO RANGE) DIFFERENTIAL Vert Method: NAVD88 Vert Datum .01 Vert Accuracy:

ACTIVE MONITOR TYPES

TANGENT ROADS State:

### Appendix C

Detailed Monitor Descriptions68

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

Nitrogen Dioxide

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Beulah

BEULAH NORTH Site Name: 6024 HIGHWAY 200 Street Address:

Not in a MSA MSA:

Mercer County: NOT IN AN URBAN AREA UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: AREA Dominant Source:

URBAN SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

* 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

- 170 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Ammonia

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Beulah

BEULAH NORTH Site Name: 6024 HIGHWAY 200 Street Address:

Not in a MSA MSA:

Mercer County: NOT IN AN URBAN AREA UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: AREA Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 171 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM

- Fine

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070507 Last Updated:

North Dakota Owner: Bismarck

BISMARCK RESIDENTIAL Site Name: 1810 N 16TH STREET Street Address:

Bismarck,ND MSA:

Burleigh County: BISMARCK, ND UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: POINT Dominant Source:

URBAN SCALE Meas. Scale: SUBURBAN Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 172 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM

- Fine

Parameter Measured: North Dakota

Monitor ID:

20061231 Date of Latest Collection: 20070226 Last Updated:

North Dakota Owner: Not in a city

TRNP

- NU Site Name: 229 SERVICE RD., WATFORD CITY Street Address:

Not in a MSA MSA:

McKenzie County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 173 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM

- Fine

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

TRNP

- NU Site Name: 229 SERVICE RD., WATFORD CITY Street Address:

Not in a MSA MSA:

McKenzie County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: POINT Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 374 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM

- Fine

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070507 Last Updated:

North Dakota Owner: Beulah

BEULAH NORTH Site Name: 6024 HIGHWAY 200 Street Address:

Not in a MSA MSA:

Mercer County: NOT IN AN URBAN AREA UAR:

SOURCE

- ORIENTED AMBIENT SURVEILLANCE Project Type: AREA Dominant Source:

URBAN SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 175 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Ozone

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

LOSTWOOD NWR Site Name: 8315 HIGHWAY 8, KENMARE Street Address:

Not in a MSA MSA:

Burke County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: POINT Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 176 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Nitrogen Dioxide

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

DUNN CENTER Site Name: 9610 SEVENTH STREET SW Street Address:

Not in a MSA MSA:

Dunn County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

4.0 Probe Height (m): 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

- 177 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Ozone

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Fargo

FARGO NW Site Name: 4266 40TH AVE NORTH Street Address:

Fargo

- Moorhead,ND

- MN MSA:

Cass County: FARGO

- MOORHEAD, ND

- MN UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: AREA Dominant Source:

URBAN SCALE Meas. Scale: SUBURBAN Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 178 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Ozone

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Bismarck

BISMARCK RESIDENTIAL Site Name: 1810 N 16TH STREET Street Address:

Bismarck,ND MSA:

Burleigh County: BISMARCK, ND UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: AREA Dominant Source:

URBAN SCALE Meas. Scale: SUBURBAN Location Setting:

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

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

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

- 179 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Sulfur Dioxide

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Beulah

BEULAH NORTH Site Name: 6024 HIGHWAY 200 Street Address:

Not in a MSA MSA:

Mercer County: NOT IN AN URBAN AREA UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: AREA Dominant Source:

URBAN SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

* 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

- 180 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Ozone

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Beulah

BEULAH NORTH Site Name: 6024 HIGHWAY 200 Street Address:

Not in a MSA MSA:

Mercer County: NOT IN AN URBAN AREA UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: AREA Dominant Source:

URBAN SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

* 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

- 181 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Nitrogen Dioxide

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

HANNOVER Site Name: 1575 HIGHWAY 31 Street Address:

Not in a MSA MSA:

Oliver County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

URBAN SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 182 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM

- Fine

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

DUNN CENTER Site Name: 9610 SEVENTH STREET SW Street Address:

Not in a MSA MSA:

Dunn County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

* 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

- 383 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Ozone

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

TRNP

- NU Site Name: 229 SERVICE RD., WATFORD CITY Street Address:

Not in a MSA MSA:

McKenzie County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 184 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Sulfur Dioxide

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Fargo

FARGO NW Site Name: 4266 40TH AVE NORTH Street Address:

Fargo

- Moorhead,ND

- MN MSA:

Cass County: FARGO

- MOORHEAD, ND

- MN UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: POINT Dominant Source:

URBAN SCALE Meas. Scale: SUBURBAN Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 185 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Nitrogen Dioxide

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Fargo

FARGO NW Site Name: 4266 40TH AVE NORTH Street Address:

Fargo

- Moorhead,ND

- MN MSA:

Cass County: FARGO

- MOORHEAD, ND

- MN UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: MOBILE Dominant Source:

URBAN SCALE Meas. Scale: SUBURBAN Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 186 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM

- Fine

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Bismarck

BISMARCK RESIDENTIAL Site Name: 1810 N 16TH STREET Street Address:

Bismarck,ND MSA:

Burleigh County: BISMARCK, ND UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: AREA Dominant Source:

URBAN SCALE Meas. Scale: SUBURBAN Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 387 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM

- Fine

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070507 Last Updated:

North Dakota Owner: Fargo

FARGO NW Site Name: 4266 40TH AVE NORTH Street Address:

Fargo

- Moorhead,ND

- MN MSA:

Cass County: FARGO

- MOORHEAD, ND

- MN UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: POINT Dominant Source:

URBAN SCALE Meas. Scale: SUBURBAN Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 188 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Nitrogen Dioxide

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

TRNP

- NU Site Name: 229 SERVICE RD., WATFORD CITY Street Address:

Not in a MSA MSA:

McKenzie County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 189 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Sulfur Dioxide

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

LOSTWOOD NWR Site Name: 8315 HIGHWAY 8, KENMARE Street Address:

Not in a MSA MSA:

Burke County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 190 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Sulfur Dioxide

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Bismarck

BISMARCK RESIDENTIAL Site Name: 1810 N 16TH STREET Street Address:

Bismarck,ND MSA:

Burleigh County: BISMARCK, ND UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: POINT Dominant Source:

URBAN SCALE Meas. Scale: SUBURBAN Location Setting:

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

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

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

- 191 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM10

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

DUNN CENTER Site Name: 9610 SEVENTH STREET SW Street Address:

Not in a MSA MSA:

Dunn County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 392 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM

- Fine

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070507 Last Updated:

North Dakota Owner: Bismarck

BISMARCK RESIDENTIAL Site Name: 1810 N 16TH STREET Street Address:

Bismarck,ND MSA:

Burleigh County: BISMARCK, ND UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: POINT Dominant Source:

URBAN SCALE Meas. Scale: SUBURBAN Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 293 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM

- Fine

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Beulah

BEULAH NORTH Site Name: 6024 HIGHWAY 200 Street Address:

Not in a MSA MSA:

Mercer County: NOT IN AN URBAN AREA UAR:

SOURCE

- ORIENTED AMBIENT SURVEILLANCE Project Type: AREA Dominant Source:

URBAN SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 394 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Ozone

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

HANNOVER Site Name: 1575 HIGHWAY 31 Street Address:

Not in a MSA MSA:

Oliver County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

URBAN SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 195 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM

- Fine

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

HANNOVER Site Name: 1575 HIGHWAY 31 Street Address:

Not in a MSA MSA:

Oliver County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: POINT Dominant Source:

URBAN SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 396 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Nitrogen Dioxide

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

LOSTWOOD NWR Site Name: 8315 HIGHWAY 8, KENMARE Street Address:

Not in a MSA MSA:

Burke County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 197 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Sulfur Dioxide

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

TRNP

- NU Site Name: 229 SERVICE RD., WATFORD CITY Street Address:

Not in a MSA MSA:

McKenzie County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 198 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Ozone

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

DUNN CENTER Site Name: 9610 SEVENTH STREET SW Street Address:

Not in a MSA MSA:

Dunn County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

4.0 Probe Height (m): 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

- 199 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM10

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Beulah

BEULAH NORTH Site Name: 6024 HIGHWAY 200 Street Address:

Not in a MSA MSA:

Mercer County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

URBAN SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 3100 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Sulfur Dioxide

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

DUNN CENTER Site Name: 9610 SEVENTH STREET SW Street Address:

Not in a MSA MSA:

Dunn County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

4.0 Probe Height (m): 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

- 1101 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Sulfur Dioxide

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

HANNOVER Site Name: 1575 HIGHWAY 31 Street Address:

Not in a MSA MSA:

Oliver County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: AREA Dominant Source:

URBAN SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 1102 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM10

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

LOSTWOOD NWR Site Name: 8315 HIGHWAY 8, KENMARE Street Address:

Not in a MSA MSA:

Burke County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: POINT Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 3103 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM

- Fine

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

LOSTWOOD NWR Site Name: 8315 HIGHWAY 8, KENMARE Street Address:

Not in a MSA MSA:

Burke County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: POINT Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 3104 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM

- Fine

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Fargo

FARGO NW Site Name: 4266 40TH AVE NORTH Street Address:

Fargo

- Moorhead,ND

- MN MSA:

Cass County: FARGO

- MOORHEAD, ND

- MN UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: POINT Dominant Source:

URBAN SCALE Meas. Scale: SUBURBAN Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 3105 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM10

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Fargo

FARGO NW Site Name: 4266 40TH AVE NORTH Street Address:

Fargo

- Moorhead,ND

- MN MSA:

Cass County: FARGO

- MOORHEAD, ND

- MN UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: POINT Dominant Source:

URBAN SCALE Meas. Scale: SUBURBAN Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 3106 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM10

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Not in a city

TRNP

- NU Site Name: 229 SERVICE RD., WATFORD CITY Street Address:

Not in a MSA MSA:

McKenzie County: NOT IN AN URBAN AREA UAR:

BACKGROUND SURVEILLANCE Project Type: POINT Dominant Source:

REGIONAL SCALE Meas. Scale: RURAL Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 3107 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

PM10

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Bismarck

BISMARCK RESIDENTIAL Site Name: 1810 N 16TH STREET Street Address:

Bismarck,ND MSA:

Burleigh County: BISMARCK, ND UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: AREA Dominant Source:

URBAN SCALE Meas. Scale: SUBURBAN Location Setting:

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

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

Sample Residence Time: Y Unrestricted Air FLow?:

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

- 3108 May. 18, 2007 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

MONITOR DESCRIPTION REPORT

Nitrogen Dioxide

Parameter Measured: North Dakota

Monitor ID:

20070331 Date of Latest Collection: 20070430 Last Updated:

North Dakota Owner: Bismarck

BISMARCK RESIDENTIAL Site Name: 1810 N 16TH STREET Street Address:

Bismarck,ND MSA:

Burleigh County: BISMARCK, ND UAR:

POPULATION

- ORIENTED SURVEILLANCE Project Type: MOBILE Dominant Source:

URBAN SCALE Meas. Scale: SUBURBAN Location Setting:

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

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

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

- 1109 

### Appendix D

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