# Annual Report

North Dakota

A mbient Monitoring

Network Plan

20 1 2ii 

# Annual Report

North Dakota

Ambient Monitoring

Network Plan

20 1 2

Jack Dalrymple

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

................................ .................... 1 5

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 2.5 Network

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

2.4.5 Speciation Network

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

2.5 Carbon Monoxide

................................ ..................... 28

2.5.1 Sources

................................ ......................... 28

2.5.2 Monitoring Network

................................ ................ 28

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

................................ ................ 3 1

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



# ................................ .................... 59

Appendix C Detailed Monitor Descriptions



# ................................ ................ 68

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 & FEM PM 2.5 Particulates

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

Table 11 Continuous PM 10

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

Table 1 2 Major CO Sources

................................ ................................ ................................ 29

Table 13 Carbon Monoxide

................................ ................................ ................................ 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 SO 2 Maximum 1

- Hour Concentrations

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

Figure 4 SO 2 Maximum 3

- Hour Concentrations

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

Figure 5 SO 2 M aximum 24

- Hour Concentratio ns

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

Figure 6 Major Oxides of Nitrogen Sources

................................ ................................ ... 17

Figure 6 A Annual Oxides of Nitrogen Emissions

................................ ............................. 17

Figure 7 NO 2 Annual Average Concentrations

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

Figure 8 Major VOC Sources

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

Figure 9 Annual 4 th H ighest Ozone Concentrations

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

Figure 1 0 Major PM 10 Sources

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

Figure 10 A Annual PM Emissions

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

Figure 11 Major CO Sources

................................ ................................ ............................. 29

Figur e 12 Major 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 1 6 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 primary categories: National Core (NCore)

and State, Local, and Tribal (SLT). Each s tate is required to have at least one NCore site. Fargo

NW has been selected as North Dakota’s required NCore site. Fargo NW is also a part of EPA’s 54

-

site Speciation Trends National Network. The NAAMS explains the purpose of these national

networks and rationale for each gaseous and particulate measurement

.

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

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

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

object ives. These objectives are as follows:

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

the network.

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

.

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

categories.

4. To determine the general/background concentration levels.

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

.

6. To determine welfare

- related impacts (such as visibility impacts and vegetation effects).

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

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

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

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

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

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

EPA, are described as follows:

Microscale

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

Middle Scale

– a reas up to several city blocks in size with dimensions ranging from about 100

meters to 0.5 km.

Neighborhood Scale

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

km.

Urban Scale

– overall, city

- wide dimensions on the order of 4 t o 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 Neighborh ood, 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 monit ored 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 r eviewing each site and associated monitors to evaluate their

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

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

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

D.

1.2 General Monitoring Needs

As can be gathered from the prior discussion, each air pollutant has certain characte ristics 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 th e 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 sou rce or class category; ( 4) long range transport; and ( 5) regional haze.

There are a total of 1 6 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, is 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 particula te (PM 2.5 )

sampler. The NPS also provides a continuous PM 2.5 analyzer, which the department 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 d epartment’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 do wnwind of two major sources. Fargo NW is population orientated

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

- Moorhead

,

MN , area. The data from this site is used as input to dispersion models to evaluate permits

- to

con struct and permits

- to

- operate for projects located in or near population centers in the eastern

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 2.5 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 n ot

normally used for NO 2 monitoring. Once a specific location is selected for a site, the 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: Appendix 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 loca tions.

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 chang es needed 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 2.5 , cont. PM 10 Manual PM 2.5 Population Exposure

&

Significant Source

2 Bismarck Residential

380150003 SO 2 , NO 2 , O 3 , MET

cont. PM 2.5 , cont. PM 10 Manual PM 2.5 Population Exposure

3 Dunn Center

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

cont. PM 2.5 , cont. PM 10 General Background

4 Fargo NW

380171004 SO 2 , NO 2 , O 3 , CO, NO

y , MET

cont. PM 2.5 , cont. PM 10 Manual PM 2.5 PM fine Speciation Population Exposure

Population Exposure

Population Exposure

Population Exposure

5 Hannover

380650002 SO 2 , NO 2 , O 3 , MET

cont. PM 2.5 , cont. PM 10 Source Impact

6 Lostwood NWR

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

cont. PM 2.5 , 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 2.5 , cont. 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.

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 2.5 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 include coal

- fired steam

- powered

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

refinery, and flaring at oil/gas well sites. As a result, SO 2 is one of the Department's primary

interests in regard to vis ibility: 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 201 1 emissions are

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

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

from point sources and three sub

- categories for 1984 through 20 11

.

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 Basin Electric Power Cooperative Antelope Valley Station 3805700011

4 Otter Tail Power Company Coyote Station 3805700012

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

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 University of North Dakota UND Heating Plant 3803500003

11 American Crystal Sugar Company Hillsboro Plant 3809700019

12 North Dakota State University NDSU Heating Plant 3801700005

13 Tesoro Refining and Marketing Company Mandan Refinery 3805900003

14 American Crystal Sugar Company Drayton Plant 3806700003

15 Petro

- Hunt, LLC Little Knife Gas Plant 3800700002

16 ADM Corn Processing Walhalla Ethanol Plant 3806700004

17 Minn

- Dak Farmers Cooperative Wahpeton Plant 3807700026

18 Cargill Corn Milling Wahpeton Facility 3807700110

Figure 2 Major Sulfur Dioxide Sources8 2.1.3 Monitoring Network

The SO 2 monitoring sites are shown on Figure 2. There were no significant changes made

to the SO 2 monitoring network in 2011. There are no significant changes planned for 2013.

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

and gas development in the west and the coal

- fired steam electrical generating plants in the

west

- central part of the s tate. Tables 3 and 3A show the 20 1 1 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

process ing plants and two power plants. The two natural gas processing plants are the Figure 2A Annual Sulfur Dioxide Emissions 0 50000 100000 150000 200000 250000

1984 1986 1988 1990 1992 1994 1996 1998 2000 2002 2004 2006 2008 2010SO2(TONS) NORTH DAKOTA

POINT SOURCE

SO

2 EMISSIONS

TOTAL OIL & GAS OTHER PT. SOURCES UTITLITY BOILERS9 Lignite Gas Plant and Tioga Gas Plant. The two power plants, Shand Power Station and

Boundary Dam Power Station

, are located near Estevan, Saskatchewan, approximately 40

miles to the northwest.

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

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

not been the case. There have been possible short

- term inf luences, but no significant long

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

5 present the following for the Department

- operated sites : ( 1 ) 1

- hour maximums; ( 2 ) 3

- hour

maximums; and ( 3 ) 24

- hour maximums

. Bec ause the industry sites are sited specifically for

maximum expected concentrations (primarily as predicted by dispersion models and

secondarily in a downwind direction), the industry sites are not reviewed for particular long

term trends.

To calculate valid statistics, at least 75 percent of t he data for each averaging period must be

valid. The result of the 75 percent requirement is that each 1

- hour average must have at

least 45 valid minutes of data. The 3

- hour average must have three valid values. The 24

-

hour average must have at least 18 valid hourly averages. And, the annual average must

have 6

, 570 hours of data.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

NUM 1 ─ HOUR 99 TH % 3

– HOUR 24 ─ HOUR ARITH 3yr 1HR 24HR

LOCATION YEAR OBS 1ST 2ND 1HR 1ST 2ND 1ST 2ND MEAN Avg #>273 #>99

─────────────────────────────────────────────────────────────── ─────────────────────────────────────────────────────────── ─────────── │ │ │ │ │ │

Beulah

- North 201 1 8662 │ 28 25 │ 52 │ 17.6 17.6 │ 5. 7 5.0 │ 1. 02 │ 34 │ │ │ │ │ │ │

Bismarck Resi dential 2011 8623│ 47 28 │ 22 │ 25.6 21.3 │ 8.2 7.7 │ 0.86 │ 31 │ │ │ │ │ │ │ │ │ │ │ │

Hannover 2011 86 84 │ 12 8 118 │ 5 2 │ 96.6 63.3 │ 16.4 1 2

. 0 │ 0.75 │ 51

* The air quality standards are:

STATE Standards ─

1) 75 ppb Three year average of the annual 99 th percentile (4 th highest) of the daily maximum 1─hour average concentration in a year. 2) 500 ppb highest 3─hour average concentration not to be excee ded more than once per year.

FEDERAL Standa rds ─

1) 75 ppb Three year average of the annual 99 th percentile (4 th highest) of the daily maximum 1

- hour average concentration in a year.

2) 500 ppb highest 3

- hour average concentration not to be exceeded more than once per year.

3) 140 pp b highest 24─hour concentration not to be exceeded more than on ce per year. 4) 30 ppb annual arithmetic mean.

TABLE 3 A

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

NUM 1 ─ HOUR 99 TH % 3

– HOUR 24 ─ HO UR ARITH 3yr 1HR 24HR

LOCATION YEAR OBS 1ST 2ND 1HR 1ST 2ND 1ST 2ND MEAN Avg #>273 #>99

──────────────────────────────────────────────────────── ───────────────────────────────────────────── ──────────────────── │ │ │ │ │ │ │ │ │ │ │ │

Dunn Center 2011 6927│ 30.9 1 1.0 │ 10 .0 │ 5.7 5.6 │ 2.2 1.8 │ 0. 27 │ 13

*** │ │ │ │ │ │ │ Fargo NW 2011 8134│ 9.1 5.6 │ 5.0 │ 5.8 4.8│ 2.4 2.3 │ 0.29 │ 5 │ │ │ │ │ │ │

Lostwood NWR 2011 8607 │ 47.4 34.6 │ 30.0 │ 30.9 25.3│ 7.8 17.8 │ 0.79 │ 43 │ │ │ │ │ │ │ │ │ │ │ │

TRNP

- NU 2011 8695│ 130.3 17.5 │ 9.0 │ 53.7 13.5│ 7.6 5.5 │ 0.55 │ 10 │ ** │ │ ** │ │ │

* The a ir quality standards are:

STATE Standards ─

1) 75 ppb Three year average of the annual 99 th percentile (4 th highest) of the daily maximum 1─hour average concentration in a year. 2) 500 ppb highest 3─hour average concentration not to be excee ded more than once per year.

FEDERAL Standards ─

1) 75 ppb Three year average of the annual 99 th percentile (4 th highest) of the daily maximum 1

- hour average concentration in a year.

2) 500 ppb highest 3

- hour average concentration not to be exc eeded more than once per year.

3) 140 ppb highest 24─hour concentration not to be exceeded mor e than once per year.

4) 30 ppb annual arithmetic mean.

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

** Qualified Prescribed Burn11 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

NUM # HOURS

LOCATION YEAR OBS 1ST 2ND 3RD >600 │ │ │ │ │ │ │ │

Beulah

- North 2011 8559 │ 114 │ 68 │ 66 │ │ │ │ │ │ │ │ │

Bismar ck Residential 2011 8623 │ 71 │ 61 │ 58 │ │ │ │ │ │ │ │ │

Hannov er 2011 86 84 │ 290 │ 283 │ 191 │ │ │ │ │

* 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

NUM # HOURS

LOCATION YEAR OBS 1ST 2ND 3RD >600 │ │ │ │ │ │ │ │

Dunn C enter 2011 6927 │ 40.6 │ 23.9 │ 15.5 │

*** │ │ │ │ │ │ │ │

Fargo NW 2011 8134 │ 1 2

. 1 │ 10.5 │ 9

. 5 │ │ │ │ │ │ │ │ │

Lostwo od NWR 2011 8607 │ 118.1 │ 84.5 │ 72.3 │ │ │ │ │ │ │ │ │

TRNP

- NU 2011 8694 │ 298.6 │ 67.7 │ 20.3 │ │ ** │ ** │ │

* No Standard is currently in effect:

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

** Qualified prescribed burn

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

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

Dakota hit its peak activity. Dunn Center and TRNP

– NU show the influence from the oil field

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

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

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

has been long

- range transport from major point sources.

Dunn Center and TRNP

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

well. S ince TRNP

– NU is more centrally located in the “oil patch,” it is the st ro nger indicator. Dunn

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

the “oil patch” and the coal conversion facilities to the e ast.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 startu ps (1984 had only three months of

data and shut down Dec

. 31, 1986). Hannover was started up again Jan

. 1, 1988 ; and t he Beulah

- North site began operation in 1999 and has tracked the Hannover data.13 Figure 3 SO 2 Maximum 1

- Hour Concentrations

Figure 4 SO 2 Maximum 3

- Hour Concentrations14 Figure 5 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 is formed when NO is oxidized in the ambient air. There is no ambient air

quality standard for NO.

2.2.1 Point Sources

The major 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 6 shows the approximate locations of these facilities (the numbers correspond to the

site and source tables). The larger NO

x point sources in North Dakota are associated with

coal

- fired steam

- powered electrical generating plants in t he west

- central portio n of the s tate

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

of the s tate. Figure 6 A 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 automobile 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 Regio n 8 administrator permission. Figure 6 A 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 Mo nitoring Network

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

x analyzers. Table 6 shows the 20 1 1

NO 2 data summaries. The measured NO 2 valu es are quite low. From Figure 6 it can be

seen that NO/NO 2 /NO

x analyzer s, 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 Ottertail Power Company Coyote Station 3805700012

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

3 Basin Electric Power Cooperative Antelope Valley Station 3805700011

4 Great River Energy Coal Creek Station 3805500017

5 Basin Electric Power Cooperative Leland Olds Station 3805700001

6 Dakota Gasification Company Great Plains Synfuels Facility 3805700013

7 Great River Energy Stanton Station 3805700004

8 Montana Dakota Utilities Company RM Heskett Station 3805900001

9 Hess Corporation Tioga Gas Plant 3810500004

10 American Crystal Sugar Company Hillsboro Plant 3809700019

11 Tesoro Refining and Marketing Company Mandan Refinery 3805900003

12 American Crystal Sugar Company Drayton Plant 3806700003

13 Minn

- Dak Farmers Cooperative Wahpeton Plant 3807700026

14 University of North Dakota UND Heating Plant 3803500003

15 ONEOK Rockies Midstream, L.L.C Fort Buford Compressor Station 3805300028

16 Red Trail Energy, L.L.C. Richardton Ethanol Plant 3808900058

17 North Dakota State University NDSU Heating Plant 3801700005

18 Cavalier AFS Cav a lier AFS Power Plant 3806700005

19 Alliance Pipeline, L.P. Wimbledon Compressor Station 3800300013

20 Alliance Pipeline, L.P. Towner Compressor Station 3804900006

21 Northern Border Pipeline Company Compressor Station #8 3805100001

22 Northern Border Pipeline Company Compressor Station #6 380590000717 Figure 6A Annual Oxides of Nitrogen Emissions Figure 6 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

NUM 1 ─ HOUR 98TH ARITH 3yr

LOCATION YEAR OBS 1ST 2ND PCTL MEAN Avg

─────────────────────────────────────────────────────────────────────────────────────────────────────────────────────────────── │ │ │ │ │ │ │ │

Beulah

- North 2011 8354 │ 36 30 │ 2 2 │ 2. 30 │ 25 │ │ │ │ │ │ │ │

Bismarck Residen tial 2011 8213 │ 53 48 │ 37 │ 4.8 5 │ 38 │ │ │ │ │ │ │ │

Dunn Cent er 2011 6912 │ 12 1 0 │ 1 0 │ 1. 38 │ 1 1 *** │ │ │ │ │ │ │ │

Fargo NW 2011 8085 │ 55 45 │ 40 │ 4.45 │ 42 │ │ │ │ │ │ │ │

Hannover 2011 8292 │ 21 18 │ 13 │ 1.29 │ 17 │ │ │ │ │ │ │ │

Lostwood NWR 2011 8597 │ 22 20 │ 14 │ 1.78 │ 17 │ │ │ │ │ │ │ │

TRNP

- NU 2011 8042 │ 2 2 9 1 8 │ 10 │ 1.1 2 │ 9

**

* The air quality standards are:

STATE Standards ─

1) 100 ppb Three year average of the annual 98 th percentile (8 th highest) of the daily maximum 1

- hour average concentration in a year.

2) 53 ppb annual arithmetic mean.

FEDERAL Standards ─

1) 100 ppb Three year average of the annual 98 th percentile (8 th Highest) of the daily maximum 1

- hour average concentration in a year.

2) 53 ppb annual arithmetic mean.

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

** Qualified prescribed burn

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. Figure 7 show s the annual average concentrations for the

d epartment

- operated sites for 1980

- 20 1 1

.

There were no significant changes made to the NO

x network in 2011. There are no changes

planned for 2012 or 2013.19 Figure 7 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

nitrogen (NO

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

x are emitted directly into the

atmosphere. Since solar radiat ion 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 for North

Dakota as May 1 through September 30.

2.3.1 Point Sources

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

emissi on inventories reported to the d epartment are listed in Table 7 . Figure 8 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 locat ions 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 r equire monitoring, 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 eight continuous ozone analyzers in oper ation. The

department has set up an Ozone monitoring station in Williston

. The site contain s an ozone

monitor as well as a meteorological equipment set consisting of wind speed, wind direction,

ambient temperature , and particulate monitors . This site is to asce rtain the impacts of oil

development on the ozone levels in the state as they pertain to the national ambient air

quality standards. See Figure 8 for locat ions. Table 8 presents the 20 1 1 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 Minnkota Power Cooperative, Inc. Milton R. Young Station 3806500001

4 ADM Processing Velva Facility 3804900005

5 Northern Sun (Division of ADM) Enderlin Facility 3807300001

6 Great River Energy Coal Creek Station 3805500017

7 Basin Electric Power Cooperative Leland Olds Station 3805700001

8 American Crystal Sugar Company Hillsboro Plant 3809700019

9 Trinity Containers, L.L.C. Trinity Containers, L.L.C. 3801700122

10 Minn

- Dak Farmers Cooperative Wahpeton Plant 3807700026

11 Cargill Corn Milling Wahpeton Facility 3 807700110

12 Tharaldson Ethanol Plant I, LLC Tharaldson Ethanol Plant I, LLC 3801700134

Figure 8 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

VAL 1 ─ HOUR 8 ─ HOUR 3yr 1 HR 8HR

LOCATION YEAR DAYS 1ST 2ND 1ST 2ND 3RD 4TH Avg #>120 #>75

─────────────────────────────────────────────────────────────── ────────────────────────────────────────────────────── │ │ │ Beulah North 2011 153 │ 66 6 4 │ 6 2 6 2 59 59 │ 5 8 │ │ │

Bismar ck Residential 2011 1 47 │ 63 63 │ 62 60 58 56 │ 57 │ │ │

Dunn C enter 2011 152 │ 60 6 0 │ 58 57 5 4 5 4 │ 5 5 │ │ │ │ │ │ Fargo NW 2011 129 │ 66 64 │ 61 60 58 57 │ 59 │ │ │ │ │ │ Hannover 2011 140 │ 78 6 5 │ 6 2 6 2 6 0 58 │ 5 8 │ │ │

Lostwood NWR 2011 1 49 │ 68 65 │ 65 62 61 60 │ 60 │ │ │

TRNP

- NU 2011 144 │ 327 65 │ 62 62 6 0 59 │ 58 │ * * │ │

* The air quality standards for ozone are:

STATE

– 75ppb Three year average of the annual 4 th highest daily maximum 8

- hour concentrations.

FEDERAL Standards

- 75 ppb Three year average of the annual 4 th highest daily maximum 8

- hour concentrations.

** Qualified prescribed burn

2.3.4 Network Analysis

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

(see Figure 8 ). Beulah and Hannover are within 45 miles of five of the 1 2 major VOC sources in

the s tate. Lostwood NWR and TRNP

- NU are located in Cl ass 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 influence s, one would expect to see a diversity of ozone concentrati ons. On the

contrary, Figure 9 shows a significant similarity among the 4 th maximu m 8

- hour annual

concentrations . Since 1980, only four 8

- hour averages have been higher than 70 ppb. Another,

even stronger, indication of a uniform ozone distribution is the 8

- hour concentrations: for all sites,

the difference among the 4 th highest average is 6 ppb (see Table 8).23 Figure 9 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 2.5 . The

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

and are designated as PM 10 . The PM 2.5 particulates have an aerodynamic diameter less than

or equal to a n ominal 2.5 microns. The EPA has defined a new PM subgroup of p articles

called “coarse fraction,” or PM

coarse . This subgroup is made up of PM 10

– PM 2.5 . Specific

health effects have been identified for both the PM

co a rse and PM 2.5 groups

.

2.4.1 Sources

The major PM 10 point sources (>100 TPY) are listed in T able 9 . Figure 1 0 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. F igure 10 A shows the contribution of poi nt

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 Monitorin g Network

The Department operated seven continuous PM 10 analyzers, three manual PM 2.5 samplers

,

seven FEM continuous PM 2.5 analyzers, and one speciation sampler. Table 10 show s the

manual FRM and continuous FEM PM 2.5 data summaries. Table 11 shows the continuous

PM 10 particulate data summary

.25 TABLE 9

Major PM 10 Sources

(> 100 TPY)

# COMPANY SOURCE Facility ID

1 Great River Energy Coal Creek Station 3805500017

2 Basin Electric Power Cooperative Leland Olds Station 3805700001

3 American Crystal Sugar Company Hillsboro Plant 3809700019

4 American Crystal Sugar Company Drayton Plant 3806700003

5 Montana Dakota Utilities Company RM Heskett Station 3805900001

6 Great River Energy Stanton Station 3805700004

7 Basin Electric Power Cooperative Antelope Valley Station 3805700011

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

9 Otter Tail Power Company Coyote Station 3805700012

10 Dakota Gasification Company Great Plains Synfuels Facility 3805700013

11 Red Trail Energy, L.L.C. Richardton Ethanol Plant 38089000 58

12 Tesoro Refining and Marketing Company Mandan Refinery 3805900003

Figure 10 Major PM 10 Sources26 TABLE 10

COMPARISON OF AIR QUALITY DATA WITH

THE NORTH DAKOTA AMBIENT AIR QUALITY STANDARDS *

POLLUTANT : FRM and FEM PM 2.5 Particulates (μ g/m 3 )

M A X I M A

VAL 24

– HOUR 24

- HR 24

- HR WTD Annual

LOCATION YEAR DAYS MIN 1ST 2ND 3RD 98th% 3yr Avg MEAN 3yr Avg #>35 AM>15

─────────────────────────────────────────────────── ─────────────────────────────────────────────────────────────── ───────────── │ │ │ │ │

Beulah

- North 201 1 59 │ 11 .0 10.9 10.8 │ 10.9 │ (NA) │ 5.08 │ (NA) │ │ │ │ │ │ │ │ │ │

Beulah

- North (BAMM) 201 1 353 │ 21.6 18.3 18.1 │ 15.3 │ 15 .0 │ 6.88 │ 6.3 │ │ │ │ │

Bismarck Residential 201 1 116 │ 12.3 12.2 12.2 │ 12.2 │ (NA) │ 5.67 │ (NA) │ │ │ │ │

Bismarck Residential (BAMM) 201 1 291 │ 22.5 22.5 19.2 │ 1 5 .0 │ 1 6 .0 │ 6.80 │ 6.9 │ │ │ │ │ │ │ │ │ │

Dunn Center (BAMM) 201 1 96 │ 17.1 13.9 13.8 │ 13.9 │ 14 .0 │ 6.39 │ 6.4

*** │ │ │ │ │

Fargo NW 201 1 1 10 │ 23.5 21.6 21.3 │ 21.3 │ (NA) │ 7.73 │ (NA) │ │ │ │ │

Fargo NW (BAMM) 201 1 337 │ 22.5 20.2 18.9 │ 18.0 │ 21.0 │ 7.11 │ 8. 1 │ │ │ │ │

Hannover (BAMM) 201 1 43 │ 16.8 9.1 8.9 │ 16.8 │ 17.0 │ 3.91 │ 3.9

*** │ │ │ │ │

Lostwood NWR (BAMM) 201 1 354 │ 2.04 19.5 19.5 │ 13.7 │ 1 5 .0 │ 7.38 │ 7.7 │ │ │ │ │

TRNP

- NU (BAMM) 201 1 345 │ 29.3 23.1 18.6 │ 17

. 0 │ 1 8 .0 │ 8. 80 │ 8. 7 │ │ │ │ │

* The ambient air quality standards are:

FEDERAL Standards

- 1) 24

- hour: 3

- year average of 98th per centiles not to exceed 3 5 μ g/m 3

. 2) Annual: 3

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

. *** Less than 80% of the possible samples (data) were collected. Figure 10A Annual PM Emissions27 Table 11

COMPARISON OF AIR QUALITY DATA WITH

THE NORTH DAKOTA AMBIENT AIR QUALITY STANDARDS *

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

M A X I M A

NUM 24 ─ HOUR 24HR

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

────────────────────────────────────────────────────────────── ─────────────────────────────────────────────────────────────── │ │

Beulah

- North 201 1 8550 │ 53 .0 46 .0 43 .0 3 7 .0│ 10.7 │ │

Bismarck Residential 201 1 8545 │ 74 .0 62 .0 55 .0 4 8 .0│ 14.1 │ │

Dunn Center 201 1 6811 │ 96 .0 74 .0 61 .0 57 .0│ 13.9 ***│ │

Fargo NW 201 1 8020 │ 98 .0 89 .0 85 .0 8 1 .0│ 17.7 │ │

Hannover 201 1 963 │ 14 .0 14 .0 13 .0 11 .0│ 7.4

*** │ │

Lostwood NWR 201 1 8567 │ 63 .0 52 .0 48 .0 45 .0│ 11.0 │ │

TR NP

- NU 201 1 8490 │ 35 .0 30 .0 25 .0 25 .0│ 7.9 │

* The STATE and FEDERAL air quality standards are:

1) 150 μ g/m 3 maximum averaged over a 24

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

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

2.4.3 PM 10 Network Analysis

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

primary purpose for the continuous PM 10 analyzers is to be used with the continuous

PM 2.5 analyzers to determine the PM

coarse fraction. The data also is compared to both the

data and federal ambient air quality standards.

2.4.4 PM2.5 Network

The manual PM 2.5 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. FEM Continuous PM 2.5 analyzers have been

installed at all sites in the network

.

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.28 2.5 Carbon Monoxide

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

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

sufficient population with the corresponding traffic congestion and

geographical/meteorological conditions to create significant CO emission problems.

However, there are sev eral stationary sources in the s tate that emit more than 100 TPY of

CO.

2.5.1 Sources

The major stationary CO sources (>100 TPY) are listed in Table 1 2 . Figure 1 1 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 are considerably

lower.

2.5.2 Monitoring Network

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

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

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

Mall was drafted for the Fargo

- Moorhead Council of Governments for use in its traffic

planning program. T he department opera t es a Trace Level CO analyzer at the Fargo NW

site in order to comply with the NCore requirements.29 Figure 11 Major CO Sources TABLE 1 2

Major CO Sources

(> 100 TPY)

# COMPANY SOURCE Facility ID

1 Dakota Gasification Company Great Plains Synfuels Facility 3805700013

2 Great River Energy Coal Creek Station 3805500017

3 American Crystal Sugar Company Hillsboro Plant 3809700019

4 Montana Dakota Utilities Company RM Heskett Station 3805900001

5 Basin Electric Power Cooperative Antelope Valley Station 3805700011

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

7 Otter Tail Power Company Coyote Station 3805700012

8 Basin Electric Power Cooperative Leland Olds Station 3805700001

9 Tesoro Refining and Marketing Company Mandan Refinery 3805900003

10 Minn

- Dak Farmers Cooperative Wahpeton Plant 3807700026

11 American Crystal Sugar Company Drayton Plant 3806700003

12 ONEOK Rockies Midstream, L.L.C. Fort Buford Compressor Station 3805300028

13 Cargill, Inc. Cargill Oilseeds Processing 380 1700066

14 Cargill Corn Milling Wahpeton Facility 3 807700110

15 Great River Energy Stanton Station 3805700004

16 Hess Corporation Tioga Gas Plant 3810500004

17 University of North Dakota UND Heating Plant 380350000330 TABLE 1 3

COMPARISON OF AIR QUALITY DATA WITH

THE NORTH DAKOTA AMBIENT AIR QUALITY STANDARDS *

POLLUTANT : **CARBON MONOXIDE** (PPB)

M A X I M A

NUM 1

- HOUR 8

- HOUR 1HR 8HR

LOCATION YEAR OBS 1ST 2ND 1ST 2ND #>35000 #>9000 │ │ │

Fargo NW 20 11 8137 │ 682 .0 674 .0 │ 4 00 .0 4 00.0 │

* The STATE and FEDERAL air quality standards are:

1) The maximum allowable 1

- hour concentration is 35000 ppb not to be exceeded more than once per year.

2) The maximum allowable 8

- hour concentration is 9000 pp b not to be exceeded more than once per year.31 2.6 Lead

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

concentrations and no significant lead sources. This determination, coupled with the fe deral

requirement for a NAMS network only in urbanized areas, re sulted in terminating the 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 Federal 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. Flares and treater stacks associated with oil/gas wells, oil storage

tanks, compressor stations, pipeline risers, and natural gas processing plan ts are potential

H 2 S emission sources.

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 1 5 and Figure 1 2 shows the approximate

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

2.8.2 Monitoring Netwo rk

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

.32 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 LM Wind Power Blades Grand Forks Facility 3803500067

Figure 12 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 were as follows: 3

- year average 1

- hour 99 th percentile

–

70 ppb ; 3

- hour

– 104.6 ppb ; 24

- hour

– 29.3 ppb ; annual 1

. 56 ppb.

There is no SO 2 5

- minute standard currently in effect. The maximum 5

- minute average

was 358 ppb.

3.2 Nitrogen Dioxide (NO 2 )

Neither the s tate nor f ederal standards were exceeded at any of the monitoring sit es. The

maximum conc entrations were as follows: Three year average of the 98 th percentile 1

-

hour average concentrations

– 40 ppb; annual

– 4

. 85 ppb.

3.3 Ozone (O 3 )

Neither the state nor f ederal standard was exceeded during the year. The maximum

fourth

- highest 8

- hour concentration was 60 ppb

.34 3.4 Inhalable Particulates

Neither the state nor f ederal PM 10 standards were exceeded during the y ear. The

maximum concentration was : 24

- hour

– 98 .0 μg/m 3

.

The f ederal PM 2.5 standards were not exceeded during the year. The maximum

concentrations are as follows: 24

- hour

– 2 9

. 3 μg/m 3 ; annual

– 8

. 7 μg/m 3

.

3.5 Carbon Monoxide (CO)

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

maximum concentrations are as follows: 1

- hour

– 682 ppb; 8

- hour

– 4 00 ppb

.

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

consider ed: 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 b e 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 site 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 2.5 monitoring site s for North Dakota

Gas/Particulate parameters:

Parameter Sampling &

Analysis Method Operating

Schedule Monitoring

Objective Spatial

Scale

Sulfur Dioxide Instrumental Pulsed Florescent Continuous Population Exposure Urban

Nitrogen Dioxide Instrumental Chemiluminescence Continuous Population Exposure Urban

Ozone Instrumental Ultra Violet Continuous Population Exposure Urban

Ammonia Instrumental Chemiluminescence Continuous General Background Regional

PM 2.5 24

- hour Gravimetric 1/6 Population Exposure Urban

PM 2.5 FEM PM 2.5 BAMM 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.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 s ite 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

pressure) an d 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 paramete rs:

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 2.5 24

- hour Gravimetric 1/6 Population Exposure Urban

PM 2.5 FEM PM 2.5 BAMM 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.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

dioxide, and PM 2.5 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 2.5 PM 2.5 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 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 site is required to have

trace level analyzers for sulfur dioxide, carbon monoxide, and NO Y (total reactive nitrogen) operational

by January 1, 2011. The trace level analyzers are installed.

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

Carbon Monoxide Gas Filter Correlation Continuous Population Exposure Urban

NO

y Instrumental Chemiluminescence Continuous Population Exposure Urban

Ozone Instrumental Ultra Violet Continuous Population Exposure Urban

PM 2.5 24

- hour Gravimetric 1/3 Population Exposure Urban

PM 2.5 FEM PM 2.5 BAMM 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.47 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 county area. The data collected here is used to supplement ambient data collected

at Beulah

– North and TRNP

– NU.

Gas/Particulate parameters:

Parameter Sampling &

Analysis Method Operating

Schedule Monitoring

Objective Spatial

Scale

Sulfur Dioxide Instrumental Pulsed Florescent Continuous Source Oriented Urban

Nitrogen Dioxide Instrumental Chemiluminescence Continuous Source Oriented Urban

Ozone Instrumental Ultra Violet Continuous Source Oriented Urban

PM 2.5 PM 2.5 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 we stern

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

Schedule Monitoring

Objective Spatial

Scale

Sulfur Dioxide Instrumental Pulsed Florescent Continuous Regional Transport Regional

Nitrogen Dioxide Instrumental Chemiluminescence Continuous Regional Transport Regional

Ozone Instrumental Ultra Violet Continuous Regional Transport Regional

PM 2.5 FEM PM 2.5 BAMM 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: This 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 use d 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 2.5 FEM PM 2.5 BAMM 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

- 39 2 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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