United States
Environmental Protection
Agency
Region 8
"""50 Li.,coin Street
Denver, Colorado 80295
EPA-908/2-80-002
October, 1980
Surveillance and Analysis Division,  Data Analysis Branch
 Air Quality Trends
 in  Region VIII

 1979  Data

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EPA - 908/2-80-002 U.S Envfronmental Protection Agency
AIR QUALITY TRENDS
IN REGION VIII
(1979 DATA)
Data Analysis Branch
Surveillance and Analysis Division
Denver, Colorado
September 1980

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DISCLAIMER
This report has been reviewed by the Surveillance and Analysis
Division, U.S. Environmental Protection Agency Region Viii, and approved
for publication. Mention of trade names or comeercial products does not
constitute endorsement or recommendation for use.
Document is available to the public through the National Technical
Information Service, Springfield, Virginia 22161.
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ABSTRACT
Air quality trends and status f or the calendar year 1979 were determined
for the six states in Region VIII. These states include Colorado, Montana,
North Dakota, South Dakota, Utah and Wyoming. Data resident in the SAROAD
national data bank was analyzed.
Statistical tests which detect significant differences between two
populations were utilized to identify trends. The status and severity of air
pollutants was reported as a direct measure of air quality standard and alert
level exceedences. The report includes a suninary of air quality in each
nonattainment area.
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CONTENTS
Page
Abstract
Table of Contents ill
SECTION I
Introduction . 2
Air Quality Standards g
AirQualityNoflattaiflmefltArea s
Analytical Procedures — Air Quality 13
SECTION II
StateAirQUalitySUlTlflaries • • 16
General Description 17
Colorado 19
Montana 32
NorthDakOta.. 45
SouthDakota 50
Utah 57
Wyoming 69
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APP ENDI CES
A. National Ambient Air Quality Standards
76
B. Break points for Pollution Standards Index (PSI)
C. Procedures Used to Determine Status
0. Nonattainment Area Maps
78
80
87
Denver
Denver/Boul der/Longmont
Pueblo
Larimer/Weld . . . . .
Mesa • • •
Missoula Primary TSP
Missoula Secondary TSP
Missoula CO . . .
Columbia Falls . .
Coistrip .
GreatFalls
B lllingsCO
Billings TSP
Laurel .
Butte
Anaconda
East Helena S02 . .
East Helena TSP . .
RapidCity.
Sweetwater County .
. . . . .
• . • . •
• . . . .
• . . . •
• . . . .
• . S • •
• . . • •
• S • S •
• . . . .
S • S • S
88
89
90
91
92
94
. . 95
. . . 96
97
98
99
100
101
102
103
104
105
106
107
108
• . S
• • S
• S •
• . .
• . •
S • •
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SECTION I
1

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Introduction
Air quality monitoring activities have increased substantially in Region
VIII over the past few years both in scope and frequency. These increases are
due to public demand for accurate information about harmful pollutants in the
environment and to the passage of Federal Legislation, namely, The Clean Air
Act Amendments. To fulfill the requirements of these legislative mandates
State agencies have planned and developed extensive monitoring networks which
have generated a mass of air quality data. This report presents a portrayal
of current ambient air quality status and trends in the six states comprising
EPA’s Region VIII. Trend analyses performed on the 1977, 1978, and 1979 air
quality data available in the SAROAD System indicate that 42 of the 252
counties, where sufficient data were available, experienced statistically
significant changes for at least one pollutant group. Air quality was found
to be deteriorating in 26 counties and improving in 19 counties. Table 1
summarizes these trends.
The severity analyses of 1979 air data reveals that total suspended
particulates continue to present the most wide-spread pollutant problem in the
region where 19 of the 30 counties which exceeded the primary standard also
exceeded alert levels. TSP was sampled in 118 counties. These values
represent an increase over those for 1978 when 130 counties sampled TSP and 11
of the 27 counties with violations of the primary Health Standard also
exceeded the alert level.
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During 1979 18 counties monitored for carbon monoxide. Of the 12 counties
where violations of the primary standard occurred, 7 were found which also
violated alert levels. In 1978 there were 13 counties with primary CO
violations, including 3 which also had alert violations.
No appreciable trend was observed between standards violations occurring
in 1978 and 1979 for sulphur dioxide, nitrogen dioxide or ozone.
Lead, newly designated as a criteria pollutant, was sampled in 19 counties
with only one county experiencing violations of the primary standard. The
majority of sites sampling for lead are located in rural rather than in urban
settings and it is difficult to draw any meaningful results from the lead
data, either in terms of health affects or in terms of trends in
concentrations due to vehicular emissions. Probably with the increased use of
unleaded gas in motor vehicles and with old vehicle attrition, lead pollution
will cease to present any major pollution problem.
The comparisons of single year observations of pollutant concentrations is
generally considered inadequate for accurately measuring and describing
trends. Meteorological considerations such as precipitation, solar intensity,
wind speed and direction have a major effect on year-to-year short-term
changes in pollutants and should not be neglected. However, due to the lack
of long-term monitoring data and missing periods in the data at most sites,
short-term trends must be calculated. Current trends referenced in this
report are approximated from the 1977, 1978, and 1979 data bases.
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The map in Figure 1 gives a county-by-county picture of Regional air
quality status during 1979. In constructing this map, the air quality of an
entire county is determined by that site in the county exhibiting the most
severe pollutant violations. Counties colored blue are those which sampled at
least one of the criteria pollutants for 75 percent of the total possible
sampling time and did not violate the health standard. Yellow indicates that
at least one of the sampled sites in the county violated primary air quality
standards. Red indicates that at least one of the sampled sites in the county
exceeded the alert level. Counties without current monitoring data or with
less than 75 percent of the total possible sample are colored green.
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TABLE 1
Air Quality Monitoring
Summary of
Region
Total sites
Counties with data
Counties exceeding primary standard
Counties exceeding alert level
Counties with deteriorating air
quality
Counties with improving air quality
Counties with insufficient data or
no discernible trend
Air Monitoring In
VIII in 1979
TSP S02 NO 2 CO OZONE LEAD TOTAL
227
54
49
23
22
37
412
118
39
41
18
18
19
252
30
3
0
12
5
1
51
19
0
0
7
0
0
26
12
1
4
5
4
0
26
4
3
5
4
3
0
19
1 U.S. EPA. “Guideline for Public Reporting of Daily Air Quality
Standards Index (PSI),” EPA 450/2—76—013, August 1976.
—— Pollutant
2 Instrumentation measures ozone which Is the primary constituent of oxidants.
5

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-Li
Region VIII Air Quality Status
1979
•‘ Counties meeting primary
ambient air quality
standards (at least one
criteria pollutant
sampi ed)
Counties not meeting pri-
mary anbient air quality
standards for at least
cne primary pollutant
i Counties without currect
ironitoring data or in-
sufficient data.
Figure 1

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TABLE 2
Air Quality Pollutants and Health Effects
Pollutant
Physical Description
Health Effect at
Concentrations above
the Primary Standard
Total Suspended
Particulates (TSP)
TSP is a measurement of parti-
cles in the air (such as soot,
mist, and sprays) and includes
non-toxic materials (dust and
dirt) as well as toxic mater-
ials (lead, asbestos, sulfates).
Natural and man-made sources
contribute to TSP which affects
the respiratory system in
varying degrees depending on
particle size and chemical
composition. Particle sizes
up to 15 micron size can be
inhaled into the lungs and
particles smaller than 2.5
can become lodged deeply in the
lungs. Normally the size of
major concern is from .1 to 3
microns.
Aggravation of asthma
and chronic lung
diseases, increased
cough, chest discom-
fort, restricted
activity, aggravation
of heart and lung
disease symptoms in
the elderly, increas-
ed death rate; long
term exposure to TSP
levels from 100-300
Mg/rn 3 may cause
multiple lung func-
tion changes.
Sulfur Dioxide
(SO 2 )
SO 2 is a colorless gas with
a ‘rotten egg smell that is
detectable by most people at
concentrations greater than .3
to 1 part per million. When
combined with water it forms
sulfuric acid. When in the air
in sufficient quantity it can
combine with rain to form “acid
rain.” This is a problem
whose frequency is just being
recognized. The most common
form of SO 2 in the atmosphere,
results from combustion of coal
and gas or as a by—product in
mineral smelting operations.
SO 2 reacts readily with other
atmospheric pollutants to form
sulfates, a group of compounds
responsible for aggravation of
respiratory ailments.
Aggravation of asthma,
aggravation of heart
and lung disease
symptoms in the
elderly, increased
lung illness, increas-
ed death rate; long
term exposure to SO 2
levels from 05-lppm
may cause multiple
lung function changes
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Carbon Monoxide
(CO)
CO is a colorless, odorless,
tasteless gas--a toxic product
of combustion. The automobile
engine represents the major
single source of this pollutant
Interference with
mental and physical
activity, reduced
capacity in persons
suffering from heart
and other circulatory
disorders; decreases
visual perception and
general alertness.
Ozone and other photochemical
oxidant compounds are formed
by a complex series of
chemical reactions occurring
when hydrocarbons and nitrogen
oxides from motor vehicles or
other emission sources are
exposed to sunlight. Ozone,
the critical constituent in
oxidants, is a severe irritant
to human tissue.
Aggravation of asthma
and chronic lung
disease, irritation of
the eye and of the
respiratory tract,
decreased vision,
reduced heart and lung
capacity.
Nitrogen Dioxide
(NO 2 )
NO 2 is a reddish-brown gas
with a pungent odor. It is
corrosive and is an oxidizing
agent which reacts with
hydrocarbon in sunlight to
form photochemical oxidants
(ozone-primarily). NO 2 is
formed during high temperature
combustion (motor vehicle
engines and powerplant boilers).
Increased chronic
bronchitis, reduced
resistance to disease,
aggravation of chronic
lung disease.
Lead
(Pb)
Lead is a gray-white metal
with a high luster and low melt-
ing point. It is produced in a
much larger quantity than any
other toxic metal. The major
use of lead is as a knock
retardant (tetraethyl lead) in
gasoline. More than half the
lead in the country goes into
gasoline to produce aln ost 90%
of the total lead in the
atmosphere, a large majority of
which is in particualte form
(usually less than 2 microns).
Impairs hemoglobin
production, causes
anemia, often fatal
to infants.
Ozone
(03)
.
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Air Quality Standards
The Environmental Protection Agency has been given the authority to
establish ambient air quality standards which specify, for the principal and
most widespread classes of air pollutants, limitations necessary to protect
the public health and welfare. These pollutants currently are total suspended
particulate matter, sulfur dioxide, nitrogen dioxide, ozone, and carbon
monoxide. Standards for lead have recently been proposed.
Two types of standards were established. Primary standards are set at
levels to protect human health. Secondary standards are set at levels to
protect against other forms of damage to such things as vegetation and
materials. The numerical value for each standard is listed in Appendix A.
Air Quality Nonattainment Areas
The Clean Air Act Amendments of 1977 placed additional requirements on the
States and EPA. Section 107(d) directed each State to submit a list of the
NAAQS attainment status for all areas within the State. These designations
were to be based on air quality levels that existed at the time the Amendments
were enacted. States were required by EPA guidance to consider the most
recent four quarters of monitored ambient air quality data available. If
these data showed no standards violations, then the previous four quarters of
monitoring data were to be examined to assure that the current indication of
attainment was not the result of a single year’s data reflecting
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unrepresentative meteorological conditions. In the absence of sufficient
monitored air quality data, other evaluation methods were used, including air
quality disperson modeling. The Act specified that the designated areas could
be based on air quality control regions (AQCRs) or any subportions of these
areas. EPA advised States they could divide (AQCRs) into various
nonattainment, attainment, or unclassified portions, i.e., county, subcounty,
or other geographic areas as long as the area could be clearly defined in a
written narrative. Additionally, a different geographic area could be used in
designating the status for each pollutant. The section 107(d) designations
were meant to provide a starting point for States in their effort to correct
existing air quality problems and to implement programs under the 1977 CM
Amendments. But the designation of an area as nonattainment or attainment
must be considered only a point of departure and not a final, inflexible end
in itself. Table 2 indicates, on a State—by-State, pollutant-by-pollutant
basis, the attainment status of every area as submitted by the appropriate
State agency and approved, or as designated by the Environmental Protection
Agency. No distinctions have been made as to the severity of the violations
recorded in the areas designated by nonattainment in this table. Each area
was designated nonattainment for primary or secondary standard violations. A
“P” indicates “does not meet primary standards” and “S” indicates “does not
meet secondary standards”. 1979 status and trends f or each nonattainment area
in Region VIII are described in the appropriate state sumary.
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TABLE 3
EPA NONATTAINMENT AREAS IN REGION VIII
FEDERAL REGISTER - MARCH 3, 1978
TSP S02 N02 CO
Montana Coistrip Area P
City of Columbia Falls P
City of Missoula P
Missoula Area S
Billings Area S
Great Falls Area S
Butte Area S
East Helena Area S PS
Laurel Area P
Anaconda Area PS
City of Billings P
Yellowstone County P
Rosebud County P
So. Dak. Rapid City Area P
Utah Davis County S P
Salt Lake County P PS P P
Utah County P P
Weber County P P
City of Price P
Cedar City S PS
Tooele County PS
Uintah County P
City of Bountiful P
City of Ogden P
City of Provo P
Wyoming Trona Industrial Area P
Sweetwater County
Cob. Larimer-Weld P P
designated area
Denver Designated Area P P p
Cob. Springs 3-C P
Pueblo 3-C P
Mesa Designated Area P
El Paso County P
Ft. Collins-Greeley
P - Does not meet primary standard
S - Does not meet secondary standard
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TABLE 4
EPA NONATTAINMENT AREAS IN REGION VIII
1979
TSP SOz N02 Co Q
Cob. Denver Designated Area P P P p
Cob. Springs 3-C P p
Pueblo 3—C P
Mesa Designated Area P
Ft. Collins-Greeley S P
Montana Coistrip Area P
City of Columbia Falls P
City of Missoula P P
Missoula Area S
City of Billings S P
Great Falls Area S
Butte Area P
East Helena Area S PS
Laurel Area P
Anaconda Area PS
So. Dak. Rapid City Area P -
Utah Davis County S P
Salt Lake County P PS P
Utah County P P
Weber County P P
Cedar City PS
Tooele County PS
City of Bountiful P
City of Ogden P
City of Provo P
Salt Lake City P
Wyoming Trona Industrial Area P
P - Does not meet primary standard
S - Does not meet secondary standard
12

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Analytical Procedures - Air Quality
Status and Severity Analysis
Status and severity of air quality are determined by comparing
measurements made at monitoring stations to air pollution standards. The
indicator used to characterize air quality status in this manner was the
number of days in which measurements exceed the primary standards at the worst
site in each county. The indicator may not actually represent air quality for
the entire county, however the worst site is always selected in an area where
measured concentrations are affecting some segment of the population.
Complete procedures for determining status are documentated in Appendix C.
Another indicator is used to demonstrate the severity of the problem.
Each pollutant has been assigned an alert level, the concentration at which
the public must be notified of possible adverse health affects. These values
shown in Appendix B are significantly higher than the standards and are not
frequently encountered.
These two indicators correspond to break points in the Pollutant Standards
Index (PSI) which is becoming the nationwide index for reporting air quality
levels to the public. In the PSI the worst site pollutant concentration in
each metropolitan are is chosen, and the index is calculated from the
concentration at the site referenced to primary standards and alert levels.
PSI breakpoints are detailed by pollutant in Appendix B.
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Trend Analysis
For a long while it has been felt by many researchers in the field that
air pollutant concentration probability distributions were not known at all or
at the very best only poorly approximated. This is true f or the types of
distributional forms previously studied, namely the log normal and
distributions similar to the log normal (e.g., SB, gari na, etc). All of these
fall short in providing a usable model for the data. As a result,
nonparametric techniques, which are inherently less powerful than parametric
techniques, have been advised f or trending purposes. Recent statistical
research in the Data Analysis Branch has brought to our attention a type of
truncated normal distribution which has proven quite effective in modeling air
data. Our trending techniques have been based upon this distribution and are
totally parametric and extremely powerful. Although based upon complicated
formulae, the trending technique is intuitively appealing. Utilizing the new
distributional form, a 95 percent confidence interval is constructed for the
true concentration mean for each year under study. This mean is not the same
as a simple arithmetic mean or a geometric mean. The more proper term for the
type of mean used here is the “expected value,” with the definition of this
term being described as it ususally is in mathematics and statistics. The
“expected value” is the single best measure of the central tendency of a data
set. Each time interval is inspected for any overlap or cormionly included
parts with other intervals. If no overlap occurs, we can safely assume that
there has been a significant shift in mean concentrations, i.e., a trend is
present. The specific type of trend, whether increasing or decreasing, is
defined by the relative position of the interval along the
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concentration real number line. For example, if the 1ower bound of the 95
percent confidence interval for 1978 is greater than the upper bound of the 95
percent confidence interval for 1977, the 1978 mean value has significantly
shifted upward from the 1977 mean value.
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SECTION II
STATE AIR QUALITY SUMMARIES
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The following graphics and charts appear as a part of each state summary:
1. A map showing the location of all active air quality
monitoring sites in the state. Stations with more than 75
percent of all possible data are represented by squares.
Circles identify stations where less than 75 percent of the
data was collected.
2. A table specifying stations and pollutants used for trends
and/or status in each county. Stations with less than
three years of data are not used for trending. They are,
however, used to determine current status. Each station
used for either status or trends is required to have 75
percent of the maximum possible data.
3. A table showing the number of violation days for the years
1977, 1978, and 1979 for each pollutant at sites within
designated nonattainment areas. Both alert level and
primary level violation days are noted along with a count
of sampling days.
4. A bar chart showing total days sampled and alert and
primary violation days in 1979 by county and specific
site. Each site with a violation of criteria pollutants is
displayed.
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5. A chart showing current status and trends by county and
pollutant. If there were no data or insufficent data in
the county, arrows are not shown. Status was determined by
comparing the 1977, 1978, and 1979 data. Ozone status is
based on a three year average of 1-hour primary level
violations.
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Colorado Air Quality
The Denver metropolitan area and the Fort Collins/Greeley areas still are
the major air pollution problem areas in Colorado. Denver still has high TSP
violation rates at the 21st and Broadway site. However, TSP violations were
noted at sites in 16 other Colorado Counties. Nearly 1/2 of all instances in
which the TSP health standard was exceeded involved concentrations at or above
the alert level, not only in heavily populated Denver county, but also
throughout most of the state. Carbon monoxide violations tend to be confined
to the metropolitan areas of Denver, Colorado Springs, and Greeley. Denver
has by far the most numerous CO violations with a generally increasing trend.
Twenty-one percent of the total CO exceedences of the primary health standard
involved concentrations above the alert level. Ozone violations were limited
to the Denver Metro area. They also showed an increasing trend.
Status of Nonattainment Areas in Colorado
Larimer-Weld Designated Area - Colorado initiated a change to drop the primary
nonattainment status for TSP on November 6, 1979. The designation for TSP was
changed to a secondary standard for only Fort Collins and Greeley. In 1978
daily primary and alert level violations occurred at the Loveland, Johnstown,
Platteville, Fort Collins, Greeley and La Salle stations. Yearly geometric
mean primary violations occurred at the Loveland, Johnstown and La Salle
stations. The year 1979 still showed annual geometric mean primary violations
at the Loveland and Johnstown sites located in the Larimer-Weld County area.
19

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On November 26, 1979, the area was changed to unclassified for ozone. The
only station sampling ozone for Larimer-Weld Counties was at Greeley. This
showed one violation in 1978 and one in 1979.
El Paso County - This area was changed to unclassified for ozone on November
25, 1979. No violations were observed at the Colorado Springs station for
1976 to 1979.
Denver Designated Area — The nitrogen dioxide nonattainment area generally
represented by the Denver Metro area is shown on the map in Appendix
The carbon monoxide and ozone nonattainment areas consist of Adams, Arapahoe,
Boulder, Denver, Douglas and Jefferson Counties. Automobile emissions and
meteorological phenomenon common to the Rocky Mountains are the main causes of
NO 2 , CO and 03 pollutant problems. There were 2 stations monitoring NO 2
during 1979, 3 in 1978 and 5 in 1977. No violations were noted in 1978 and
1979.
Nine stations were used to monitor CO with no discernible trend in
violation rate f or the three year period. Of the 365 days sampled in 1979,
160 days showed primary or alert level violations. Seven ozone stations
operating in 1978 and 1979 (5 in 1977) showed no specific trend during this
period. There were 12 primary violations in 1979.
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Total suspended particulates were sampled in an area shown by the map in
Appendix . (Generally, the Denver metro area). A traditional cause of
violations is the Cherokee Power Plant while nontraditional causes include
street cleaning, winter sanding, unpaved roads, construction work, demolition
activities, unpaved alleyways and parking areas.
The number of sampling stations remained about the same, i.e., 25 in
1977, 22 in 1978 and 23 in 1979, but the sampling days increased from 91 in
1977 to 144 in 1978 and 177 in 1979. Primary to alert level violation ratios
remained about the same for 1977 and 1978 but increased substantially In
1979. Increased downtown construction appears to be one of the causes of the
increase in TSP violation levels.
Colorado Springs 3C Area - The area of El Paso County in and around Colorado
Springs comprises this area. CO problems are primarily caused by automobiles
and the meteorology and topography of the area. Two stations reported CO
samples for 365 days each of the last two years. The last three years have
shown a primary violation day increase from 0 in 1977 to 4 in 1978 and 11
violations in 1979.
Along with the semi-arid climate which promotes the potential for air
borne dust, winter sanding, grading and construction activities contribute to
TSP problems. The one station which sampled this area for an average of 78
days per year showed no primary violations during 1977, 1978 or 1979.
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Pueblo 3C Area - The map in Appendix D shows the area of nonattainment for TSP
which consists of the City of Pueblo and its irTinediate outskirts. The CF&I
Steel Company is one of the major contributors to TSP along with the standard
nontraditional sources. Two stations sampled an average of 88 days. During
1977 six primary violation days were observed. There was one violation in
1978 and two in 1979.
Mesa Designated Area — This area is in and around Grand Junction. Three
stations were sampled in 1977 and 1978 with four stations used in 1979. No
violations for TSP were noted in any of the three years which were sampled an
average of 85 days per year.
Fort Collins - Greeley Area — The City limits of Fort Collins and Greeley
constitute the limits of this area. Motor vehicles cause the vast majority of
CO emissions in these two cities with the meteorology and topography of the
area being of some consideration in pollution dispersion. The two stations
(one in Greeley and one in Fort Collins) sampled daily and showed a marked
increase in carbon monoxide primary standard violations with 10 in 1977, 6 in
1978 and 31 in 1979.
The TSP sampling donc at -t .rcc stations showed no apparent increase in
primary violation levels between 1977, 1978 and 1979 (1 to 2 to 2). The
average number of sampling days was 83 per year.
22

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Stations with greater than 75%
of maximum possible data
Stations with less than 75%
of maximum possible data
QJLORA]JO
1JNITORIN(
— —1
“I
I
SITES
ADAMS
a
ARAPAHOE
U
- - — — ____._-
/
23

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COLORADO
STATIONS USED FOR TRENDS AND/OR STATUS
County — City cr Location Station Number TSP SO2 NO2 CO O, LgAD
Adams Adams 060020001F01 X
Aurora 060140001F01 X
Brighton 060240001FO1 X
Welby 062210001F01 X X X X
Westminister 062240002F01 X
Alamosa Alamosa 060040001F01 X
Arapahoe Cherry Creek Dam 060080001F01 X
Englewood 060780001F01 X
S. Univ. Blvd 060 080002F01 X X
Archuletta Pagosa Springs 060100001F01 X
Boulder Boulder 060200001F01 X
Boulder 060200008G01 X
Boulder 060200006G05
Longmont 061460001F01 X
Clear Creek Idaho Springs 060360001FO1 X
Delta Delta 060540001F01 X
Denver Denver-Annex 060580001F01 X
Denver 21st & Bdwy 060580002F01 X X X
Denver Health Dept 060580007FO1 X
Denver Cob Blvd 060580010F01 X
Denver-Marion 060580012FO1 X
Denver-Julian 060580009FO1 X X
Douglas Castle Rock 060660001F01 X
Eagle Vail 060700001F01 X
El Paso Colorado Springs 060380004FO1 X X X X
Fremont Canon City 060300001FO1 X
Garfield Glenwood Springs 060920001F01 X
Rifle 060880001F01 X
Gunnison Crested Butte 061020001FO1 X
Crested Butte 061040002F01 X
*
Status Only
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COLORADO
STATIONS USED FOR TRENDS AND/OR STATUS
County Cjjy L tion Station Number TSP S02 N02 CO O LEAO
Jefferson Arvada 060120002F01 X X
Arvada 0601 20003F01 X
Golden 060940001F01 X
Lakewood 061260001F01 X
La Plata Durango 060680003F01 X
Red Mesa 061300083K03 X
Larimer Fort Collins 060820001F01 X X
Loveland 061480002F01 X
Las Animas Trinidad 062160002F01 X
Mesa Fruita 06152 0001F01 X
Grand Junction 060980010F01 X
Palisade 061520002F01 X
Moffat Craig 060480001F01
Montez na Mesa Verde 061530003F03 X
Towaoc 0616000041(03 X
Montrose Montrose 061620001F01 X
Otero La Junta 061220001F01 X
Pitkin Aspen 061780001F01 X
Prowers Lamar 061280001F01 X
Pueblo Pueblo Fire Stat 061820003F01 X
Pueblo Health Dept 061820007F01 X X
Rio Blanco Rangely 061860002F01 X
Routt Steamboat Springs 061920003F01 X
San Miguel Telluride 062000001F01 X
Weld Greeley 061000005F01 X X
Greeley 061000006F01 X
Johnstown 062220003F01 X
Platteville 062720005F01 X
*Status Only
25

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COLORADO
STATIONS NOT USED FOR TRENDS AND/OR STATUS - LESS THAN
75% OF MAXIMUM DAYS
County City or Location Station Number TSP Ox LEAD
Boulder Broomfield 060260001F01 X
Boulder 060200008G01 X
Denver Denver-Gates Rubber 060580003FO1 X
Denver-lOlO S. Broadway 060580003F02 X
Eagle Eagle Courthouse 060700004F01 X
El Paso Manitou Springs 061500001F01 X
Fremont Florence 060800001F01 X
Jefferson Edgewater 060720001F01 X
Rocky Flats 061140001F02 X
La Plata Ignacio 061300003K03 X
Logan Sterling 062080001F01 X
Mesa Grand Junction 060980011F01 X
Morgan Brush 060280001F01 X
Otero Rocky Ford 061900001F01 X
Weld Greeley 061000003F01 X
26

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AIR QUALITY TRENDS
BASED ON STANDARD VIOLATIONS
COLORADO
NONATTAINMENT AREAS
Total Suspended Particulates Nitrogen Dioxide Carbon Monoxide
Stations
Number Average W/Yearly Number Number
Days Violation of Percent Average of Days Violation of
Nonattainment Area Year Sampled Days Stations Obs./Sta. Violations Stations Sampled Days Stations
Denver Designated 1977 91 A4/P—17 25 86% P-2 5 365 A—18/P—145 9
Area 1978 144 A8jP26 22 72% P0 3 365 A34/P484 9
1979 177 A—27/P—52 23 91% P-O 2 365 A—34/P-160 9
Colorado Springs 3C 1977 80 P-O 1 350 P-0 2
1978 71 P—O 1 365 A-1/P—4 2
1979 82 P-O 1 365 A-i/P-il 2
Pueblo 3C 1977 90 Ai/P6 2
1978 79 P-i 2
1979 96 A—1/P—2 2
Mesa Designated Area 1977 91 P—O 3
1978 77 P-0 3
1979 86 P-0 4
Fort Collins-Greeley 1977 81 P—i 3
1978 81 P-2 3
1979 87 A-i/P-2 3
A — Alert Violation Days
P - Primary Standard Violation Days

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AIR QUALITY TRENDS
BASED ON STANDARD VIOLATIONS
COLORADO
NONATTAINMENT AREAS
Ozone
Number
Days Violation of
Nonattainment Area Year Sampled Days Stations
Denver Designated Area 1977 363 P-15 5
1978 356 A- .1/P-5 7
1979 365 P—12 7
A - Alert Violations Days
P - Primary Standard Violation Days

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NUMBER OF DAYS THAT PRIMARY STANDARD OR ALERT LEVEL WAS
EXCEEDED IN 1979
COLORADO
TOTAL SUSPENDED PARTICULATES
Days
County (City or Location) Sampled
Adams (Adams City) 80
(Brighton) 82
Alamosa (Alamosa) 83
Archuleta (Pagosa Spgs.) 80
Boulder (Longmont) 71
Clear Creek (Idaho Spgs.) 82
Denver (City Cty Bldg.) 78
(2105 Broadway) 175
Garfield (Rifle) 83
Jefferson (Arvada) 68
La Plata (Durango) 70
Larimer (Ft. Collins) 78
(Loveland) 72
Prowers (Lamar) 79
Pueblo (Health Dept.) 92
(Fire Sta.) 89
Rio Blanco (Rangely) 22
Routt (Steamboat Spgs.) 62
San Miguel (Tellόrid ”’ 70
Weld (Greeley) 83
I I
Primary level exceeded
Alert level exceeded
1 1(48 )
0
Days/Year
10
20
29

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NUMBER OF DAYS THAT PRIMARY STANDARD OR ALERT LEVEL WAS
EXCEEDED IN 1979
COLORADO
CARBON MONOXIDE
Days
Sampled
Days/Year
0 10
County (City or Location )
Adams (Welby) 359
Denver Cob. Blvd.) 364
2105 Broadway) 364
Julian) 259
El Paso (Cob. Spgs.) 363
Jefferson (Arvada) 365
Weld (Greeley) 352
Arapahoe (So. Univ.) 288 ____
Boulder (Boulder) 152 ______
Denver (Julian) 343 _____
Jefferson (Arvada) 353 _____
Primary level exceeded
____ Alert level exceeded
20 30
1 1
(158
( 80
C 35’
OZONE
1
1
30

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STATUS AND TRENDS IN
COLORADO
AIR QUALITY
County
TSP
S02
N02
CO Ox LEAD
County
TSP S02
N02 CO Ox LEAD
Adams
Alamosa
45
•
c:)
1J
I pti>
Larimer
Las Animas
E3
•
Arapahoe
Archuleta
,f J,,

j’ ?l.JJ,
Logan
Mesa
Boulder
.
Moffat
Clear Creek
Montezuma
‘j’jt’
Delta
Montrose
Denver
Douglas
Ir
I
J
4 3 h
4 J .
Morgan
Otero
c::
Eagle
•
Pitkln
El Paso
13
Prowers
Fremont
Pueblo
Garfield
Rio Blanco
!
Gunnison
a
Routt
Jefferson
La Plata
San Migoel
Weld
!
it3rc
0
a/ Status Based on Annual Mean
No evidence standard exceeded
Exceeds p fmary standard
Exceeds alert level
Improvement
No apparent trend or insufficient data to
determine trend
Deterioration
Only
31

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Montana Air Quality
There have been few pollution problems in Montana that have shown either
an improvement or deterioration. Two of the major improvements have occurred
in the city of Missoula and the Anaconda area. Carbon monoxide violations in
Missoula dropped drastically during the trend period. Missoula, located in a
valley, is particularly susceptible to pollution because of it’s topography.
Sulfur dioxide violations in the Anaconda area decreased substantially
although there were 3 alert and 18 primary SO 2 violations in 1979. Lead
violations for all 3 quarters of the 3 quarters sampled were observed in
Helena.
Status of Nonattainment Areas in Montana
Rosebud County - This area was changed from nonattainment to unclassified for
ozone. No ozone sampling was done in Montana during 1976, 1978 or 1979.
Rosebud showed no ozone violations for 290 sampling days in 1977.
Colstrip Area - The Rosebud County area is a square approximately 11 miles on
a side centered at Colstrip, Montana. This area had been designated
nonattairiment for TSP for both 24 hour and annual primary standards. Five
sampling sites in the area had no primary violations and only two secondary
violations during the 32 days of sampling in 1979. The Ashland site, (the
only site sampled in prior years) showed no violation in 1976, 1977 and 1978.
32

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City of Columbia Falls — The city limits of Columbia Falls constitute this TSP
nonattainment area located in Flathead County. This area was designated
nonattainment for the primary standard. Fugitive dust from Highway 40 and
Nucleus Avenue is the major TSP contributor. These streets will be rebuilt
and maintained by the city to alleviate this problem. Even though no daily
violations were observed for the 27 samples taken in 1977, there were 5
violations observed in 1978 and in 1979. The total of samples taken was 55 in
1978 and 8 in 1979.
City of Missoula - The city limits of Missoula make up the area which is a
primary standard nonattainment area f or TSP and CO. A broader area around
Missoula has a secondary standard nonattainment designation. The TSP problem
can be attributed primarily to dust from unpaved roads. A primary standard
violation rate of 7 days in 1977, 16 days in 1978 and 10 days in 1979 was
observed during the trend period.
Carbon monoxide due primarily to motor vehicles and the air stagnation
producing topography of this area (a valley) cause the continuing CO alert and
primary standard violation occurrences. Most of the data for 1977 and 1978
was accumulated from the station at Brooks and South Avenue. This station
location was moved for part of 1978 and 1979 to a location at Bancroft and
Kent. The number of daily violations diminished but there was still one alert
and 9 primary violation days for the 136 days sampled at the Bancroft and Kent
site.
33

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Billings Area - The area bounded by 6th Avenue N on the north, 2nd Avenue S on
the south, 25th Street on the east and 33rd Street on the west comprise the
nonattainment area designated because of secondary TSP violations.
Reentrained dust from paved roads is a major problem. A planned pilot
sweeping and flushing program will be started to alleviate the TSP problem.
Five stations showed a total of three primary standard violation days in
1979. However, the Central Park site had 36 secondary violation days of the
299 days sampled. No primary violations were noted in 1977 or 1978.
Great Falls Area - This area is bounded by 2nd Avenue N on the north, 2nd
Avenue S on the south, 10th Street on the east and the Missouri River on the
south. It is designated nonattainment for secondary violations of TSP.
Windblown particulate matter from street sanding is a major problem. No
primary violations were noted in 1978 and 1979 for four stations that sampled
93 and 126 days respectively.
Great Falls has recently been made a primary level violation
nonattainment area for carbon monoxide. One station was used for sampling CO
and this showed four primary level violations out of 94 sampling days in
1979. The years 1977 and 1978 also showed 4 and 10 primary level violations
respectively.
34

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Butte Area - The northeast section of Butte is currently designated
nonattainment for primary TSP violations. Fugitive dust emission violations
caused by the open pit mine owned by Anaconda Copper Company and unpaved roads
increased dramatically in 1979. Five primary violations days were noted out
of 240 days sampled at six stations in 1979. Only two primary standard
violations were noted in 1977 and no violations occurred in 1978. These
stations were sampled for 44 days in 1977 and 181 days in 1978.
East Helena Area — The designation of nonattainment for primary level SO 2
violations covers an area of .67km radius around the ASARCO smelter. A 1400
foot square area in the northeast corner of the SO 2 area has been designated
a nonattainment TSP area because of secondary standard violations. The ASARCO
lead smelter causes the majority of the TSP emission problems. No TSP
sampling sites are located in this area but two sampling sites are located in
Helena. These sites showed no primary level violations in 1977 thru 1979 but
do show a total of seven secondary violations for the 59 days sampled in 1979.
A station is set up in Montana City four miles SSE of the ASARCO plant to
monitor SO 2 . No violations of the primary standard were shown at this site
for 1977 thru 1979 even though there were 290, 183 and 133 days of sampling
respectively. Eighty percent of the emissions are from 400 foot stacks, while
the remaining 20 percent of the emissions are from 110 foot stacks and subject
to down wash. Taller stacks (375 feet) have been suggested as a replacement
to the 110 foot stacks to solve down wash problems.
35

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Laurel Area — An area of 2 km radius around the Cenex Refinery is the area
designated nonattainment for primary SO 2 standard violations. The one site
used for monitoring showed 10 primary violation days in both 1978 and 1979
down from 33 in 1977. The number of days sampled has decreased over the trend
period.
Anaconda Area — A 6 mile square area centered at the Anaconda Copper smelter
constitutes the nonattainment area designated because of SO 2 violations.
Violations occur because of excessive emissions from the main stack In the
elevated terrain southwest of the plant. Excessive fugitive emissions also
occur close to the smelter. Only one site currently has data in the EPA data
system for 1979, and shows 18 primary violation days for 335 days sampled by
comparison 1978 showed 136 primary violation days at the 10 sampling sites
City of Billings - The area bounded by 6th Avenue N on the north, the
Burlington Northern tracks on the south, U.S. 87 on the east and Division
Street on the west has been designated as nonattainment for carbon monoxide
violations. Motor vehicle emissions cause almost all the CO problems. No
data was collected in 1979 at any site in Billings. Only one station was used
for 1977 and 1978. This showed three daily violations of 276 samples taken in
1977 and no violations for 82 samples taken In 1978. Three major
intersections need modifications to help alleviate this problem area.
Billings was changed from nonattainment to unclassified for ozone. No
ozone data was collected in 1978 or 1979.
36

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MONITORING SITES
Stations with 75% or more of
maximum possible data
Stations with less than 75%
of maximum possible data
ffPI A
37

-------
MONTANA
STATIONS USED FOR TRENDS AND/OR STATUS
County City or Location Station Number TSP S02 CO L fl
Big Horn N.E. of Decker 270060009F03 X
Cascade Great Falls 270660015F01
Great Falls 270660009G01 X
Great Falls 270660026F01 X
Daniels Scobey 270340001F03 X
Scobey 270340003F03 X
Scobey 270340003F03 X
Dawson Lindsay 270360004F03 X
Deer Lodge Anaconda-Lincoln 270020007F01 X X
Highway Jct 270400004F02 X X
Mill Cr Crossing 270400012F02 X
Flathead Columbia Falls 270270005F01 X
Columbia Falls 270480029F02 X
Gallatin Kalispell 270800014F01 X
Bozeman 270120001F01 X
Jefferson Montana City 270760904F02 X
Microwave 270760903F02 X
Lake Ronan 270820011F05 X
Lewis & Clark Helena 270720001F0]. X
Helena 270860002F02 X X
Helena 270720001F07 X
Lincoln Libby 270900010F01 X
Missoula Missoula-Lions Pk 271100019F01 X X X
Missoula 271100020G01 X
Missoula 271100001G01 X X
Missoula 271100015G02 X
Missoula 271100016GO2 X
Rosebud BN Site 271360027F02 X
*Status Only
38

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MONTANA
STATIONS USED FOR TRENDS AND/OR STATUS
County City or Location Station Number TSP S02 CO LEAD
Silverbow Butte 270160005F01 X
Fisher Butte 271360002F03 X
lierney 2714800]5F02 X
Butte 270160020F01
Butte 270160017F01 X
Butte 270160018F01 X
Butte 270160019F0]. X
Yellowstone Billings 270080059F01 X
Billings 270080007G01 X
Billings 270080008G01 X
Billings 270080009G01 X
Laurel 270840001G02 X X
Laurel 270840009F0]. X
Laurel 270840009F05 X
*Status Only
39

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MONTANA
STATIONS NOT USED FOR TRENDS AND/OR STATUS - LESS THAN
75% OF MAXIMUM DAYS
County City or Location Station Number TSP
Big Horn Decker-Warren Ranch 270060009F03 X
Lake Poison 270820010F05 X
McCone Fort Peck 270980001F03 X
Yellowstone Billings 270080006F05 X
40

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AIR QUALITY TRENDS
BASED ON STANDARD VIOLATIONS
MONTANA
NONATTAINMENT AREAS
Total Suspended Particulates Carbon Monoxide
— Number Number
Days Violation of Days Violation of
Nonattainment Area Year Sampled Days Stations Sampled Days Stations
Coistrip Area 1977 27 P-O 1
1978 13 P-U 1
1979 32 p-U 5
City of Columbia 1977 27 P—3 1
Falls 1978 55 A—3/P-5 2
1979 60 A—2/P—8 1
City of Missoula 1977 365 P-7 8 290 A—12/P—133
1978 360 A—6/P-16 9 150 A—21/P-66 2
1979 365 A-1/P-1O 6 136 A-1/P-9
Missoula Area 1977 365 P—7 8
1978 360 A-6/P-16 9
1979 365 A-1/P—1O 6
Billings Area 1977 60 P-O 4
1978 138 p-U 7
1979 303 P—3 5
Great Falls Area 1977 99 A—i/P—i 2 161 P-4
1978 93 P—0 4 57 P-lU
1979 126 P-U 4 94 P-4
Butte Area 1977 44 P—2 5
1978 131 P-O 8
1979 240 P—5 6
A - Alert Violation Days
P - Primary Standard Violation Days

-------
AIR QUALITY TRENDS
BASED ON STANDARD VIOLATIONS
MONTANA
NONATTAINMENT AREAS
Total Suspended Particulates Sulfur Dioxide Carbon Monoxide
Number Number Number
Days Violation of Days Violation of Days Violation of
Nonattainment Area Year Sampled Days Stations Sampled Days Stations Sampled Days Stations
East Helena Area 1977 49 p-a 2 290 P0 1
1978 68 p-a 3 183 p-a i
1979 59 P-a 2 133 P-O 1
Laurel Area 1977 191 P—33 2
1978 75 A-2/P-14 2
1979 172 P-1O 2
Anaconda Area 1977 365 A8/P28 1
1978 363 A-48/P-136 10
1979 335 A-3/P—18 1
City of Billings 1977 226 P—3
1978 82 p-a
1979 0 —- 0
A - Alert Violation Days
P - Primary Standard Violation Days

-------
NUMBER OF DAYS THAT PRIMARY STANDARD OR ALERT LEVEL WAS
EXCEEDED IN 1979
MONTANA
TOTAL SUSPENDED PARTICULATES
Days/Year
Days
Sampled 0 10
County (City or Location )
Flathead (Coltinbia Falls)
(Kal Ispell)
Lake (Ronan)
Lincoln (Libby)
Missoula (Lions Park)
(Rose Park)
Silver Bow (Butte)
Deer Lodge Highway Jct.)
Anaconda)
Mill Cr. Cross)
Yellowstone (Laurel)
Cascade (Great Falls)
Missoula (Lions Park)
60
47
50
57
352
209
239 _______
SULFUR
175
322
186
157
CARBON MONOXIDE
82
132
I
U
I
-J
DIOXIDE
S I
I
20 30
LEAD - VIOLATIONS-QUARTERLY AVERAGE
Lewis & Clark (Helena)
Quarters
Sampled
3
F I
Primary level exceeded
Alert level exceeded
I
43

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STATUS AND TRENDS IN AIR QUALITY
MONTANA
County
Big Horn
Cascade
Daniels
Dawson
Deer Lodge
Flathead
Gallatin
Jefferson
TSP S02
CO LEAD
TSP S02 CO LEAD
.
.E
County
Lake
Lewis and Clark
Lincoln
McCone
Mi ssoul a
Rosebud
Silver Bow
Yellowstone
Flo evidence standard exceeded
Exceeds primary standard
Exceeds alert level
Improvement
No apparent trend or insufficient data
to determine trend
Deterioration
0
44

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North Dakota Air Quality
Total suspended particulates were sampled in 13 counties with no primary
ambient air quality standard violations in 1979. Only one station sampled
NO 2 and Ozone (Stanton). This site also showed no violations for these
pollutants. There are no designated non-attainment areas in the state.
45

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NORTH D fA
MONITORING SITES
Stations with 75% or more of
maximum possible data
Stations with less than 75%
of maximum possible data
46

-------
NORTH DAKOTA
STATIONS USED FOR TRENDS AND/OR STATUS
County City or Location Station Number TSP NO 2 O,
Barnes Valley City 351240001F0]. X
Billings Medora 350080001F03 X
Bowman Bowman 350160001F01 X
Burleigh Bismarck 350100001F01 X
Cass Fargo 350400001F01 X
Dunn Mandaree 350340001F03 X
Grand Forks Grand Forks 350480001F01 X
Grant Glen Ullin 350520001F03 X
Morton Mandan 35074000].FO1 X
Oliver Stanton 350860001F03 X X
Richiand Wahpeton 351260001F0].
Stark Dickinson 350300001F01 X
Ward Mi not 350780001F01 X
Lake Darling 351300001F03 X
*Status Only
47

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NORTH DAKOTA
STATIONS NOT USED FOR TRENDS AND/OR STATUS - LESS THAN
75% OF MAXIMUM DAYS
County City or Location Station Number TSP
Cass Fargo 350220001F03 X
McKenzie Roosevelt Nati Park 35O700002F03 X
Mercer Beulah 350760001F01 X
Ramsey Devils Lake 35O260001FO1 X
Stutsman Jamestown 35O580001FO1 X
Williams Williston 351360001FO1 X
48

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STATUS AND TRENDS IN AIR QUALITY
NORTH DAKOTA
County
Barnes
Billings
Bowman
Burleigh
Cass
Dunn
Grand Forks
Grant
McKenzi e
McLean
TSP
Ox
t102 Ox
00
No evidence standard exceeded
Exceeds primary standard
Exceeds alert level
Improv nent
No apparent trend or insufficient data
to determine trend
Deterioration
TSP
County
Mercer
Morton
Ramsey
Richard
Oliver
Stark
Stutsman
Ward
Williams
0
49

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South Dakota Air Quality
Total suspended particulate (TSP) is the only air pollutant monitored in
South Dakota. Seven stations located in the Rapid City area showed 2 alert
level and 3 primary level violation days. This is a deterioration from the
1977 and 1978 levels.
Status of Nonattainment Areas In South Dakota
Rapid City Area - The nonattainment area designated for TSP primary violations
is a 10 mile (north—south) by 11 mile (east-west) rectangular area centered at
Rapid City. Most of the violations have been caused by fugitive emissions
from quarry operations. Requirements have been adopted for fugitive dust
emission controls which should result in attainment by 1982. Seven stations
measured three primary and two alert level violation days for 62 days sampled
in 1979. This Is higher than in the past. There were three primary violation
days in 1977 and one in 1978.
50

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SOUTH DAIUIA
MONITORING SITES
Stations with 75% or more of
maximum possible data
Stations with less than 75%
of maximum possible data
51
0

-------
SOUTH DAKOTA
STATIONS USED FOR TRENDS AND/OR STATUS
County City or Location Station Number TSP
Beadle Huron 430820001F01 X
Fall River Hot Springs 430780001F03 X
Grant N.E. Big Stone Plant 430640002F02
S.E. Big Stone Plant 430640001F02
Hughes Pierre 431340001F01 X
Minnehaha Sioux Falls 431480004F01 X
Pennington Rapid City 431380001F01 X
Rapid City 431380007F01 X
Rapid City 431380002F01 X
Rapid City 431380005F01 X
Rapid City 431380006F01 X
Perkins LelTunon 431320001F03 X
Yankton Yankton 431800001F03 X
*
Status Only
52

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SOUTH DAKOTA
STATIONS NOT USED FOR TRENDS AND/OR STATUS - LESS THAN
75% OF MAXIMUM DAYS
County City or Location Station Number TSP
Brookings Brookings 430]40001F01 X
Codington Watertown 431760001F01 X
Pennington Rapid City 431380009F01 X
53

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AIR QUALITY TRENDS
BASED ON STANDARD VIOLATIONS
SOUTH DAKOTA
NONATTAINMENT AREAS
Total Suspended Particulates
Number
Days Violation of
Nonattainment Area Year Sampled Days Stations
Rapid City Area 1977 53 P—3 4
1978 56 P-i 4
1979 62 A—2/P—3 7
A - Alert Violation Days
P — Primary Standard Violation Days
54

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NUMBER OF DAYS THAT PRIMARY STANDARD OR ALERT LEVEL WAS
EXCEEDED IN 1979
SOUTH DAKOTA
TOTAL SUSPENDED PARTICULATES
Days/Year
Days
County (City or Location) Sampled 10 20
Pennington (Rapid City) 55
i i Primary level exceeded
Alert level exceeded
55

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STATUS AND TRENDS IN AIR QUALITY
SOUTH DAKOTA
County TSP
Beadle
Brooki ngs
Codington
Custer
Fall River
Grant
Hughes
Minnehaha
Pennington
Perkins
Yankton
No evidence standard exceeded
Exceeds primary standard
Exceeds alert level
Improvement
No apparent trend or insufficient data
to determine trend
Det rIoration
56

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Utah Air Quality
Total suspended particulate violations occurred in 1979 at approximately
the same frequency as in 1978 for the counties of Salt Lake, Weber and Utah.
Even though the TSP emitted by Kennecott Copper has diminished, U.S. Steel in
Orem continues to be the major contributor to TSP pollution in the Wasatch
Front Counties. Most of the cities in the Wasatch Front Counties (Davis, Salt
Lake, Utah and Weber) still have violations for ozone and carbon monoxide. In
most areas no trend was noted for 0 and CO pollution. Both industrial and
motor vehicle pollution prevail in this area.
Status of Nonattainment Areas in Utah
Changes in nonattainment status - The City of Price in Carbon County was
changed from a nonattainment area with primary violation status in TSP to an
unclassified area. No samples were taken in 1979 but 1978 data showed that
the site had not exceeded the primary standard. The nonattainment status of
Cedar City in Iron County was changed to unclassified designation. No ozone
data from Uintah County was found in the EPA data system for 1977, 1978, or
1979.
A nonattainment designation for total suspended particulates has been
given to four Utah Counties, Davis, Salt Lake, Utah and Weber Counties.
Fugitive dust from unpaved roads and industrial emission sources are the main
causes of TSP problems.
57

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Davis County City of Bountiful Areas - The only TSP data taken for 1978 and
1979 was at the Bountiful site. Davis County was designated nonattainment for
secondary TSP violations. The years 1978 and 1979 showed no primary level TSP
violation but each year showed 6 and 18 secondary level violation days
respectively for 333 and 334 days sampled. In 1977 one alert level and two
primary level violations were noted. Davis County is also a nonattainment
area for ozone because of primary level violations. Refineries in the area
and motor vehicle emissions are the main causes. The meteorology and
topography of the area inhibit dispersion. Mountains are on both sides of
this area. The inspection and maintenance program should help reduce both the
ozone and carbon monoxide problems in the county. The ozone violation day
level has remained relatively constant in the last three years. There have
been primary violations of 8, 8 and 10 in 1977 thru 1979 respectively. The
City of Bountiful was designated nonattainment for primary level carbon
monoxide violations. Again motor vehicles appear to be the primary cause of
the CO violations. The three year average of primary violation days is
currently slightly less than 4 per year for 1977 thru 1979. This is in
comparison with 20 and 23 violation days in 1975 and 1976 at the same site.
Salt Lake County - Salt Lake City Areas - The TSP primary and alert level
violations that occurred in Salt Lake County were caused by the previously
mentioned corruiici regional sources with additional pollution caused by the
smelters at the Kennecott Copper Company The number of primary violations
have remained the same for 1978 and 1979 (9 violation days each year). This
is down considerably from 33 violation days in 1977.
58

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Ambient air quality violation of the sulfur dioxide standard have
diminished considerably since the construction of the stack at the Kennecott
Copper Company smelter near Magna. This was the main cause of the SO 2
violations in Salt Lake County. The primary violation days have decreased in
the last four years. They were 120, 30, 17 and four days for 1976 thru 1979
respectively.
Salt Lake County ozone problems caused primarily by motor vehicles should
be reduced with the implementation of the inspection and maintenance program.
The Salt Lake Health Department monitoring site showed three and four primary
level violations exceedences in 1978 and 1979.
Carbon monoxide violation days for the City of Salt Lake still remain
high. They have declined from 54 violation days in 1976 to 16 in 1979.
However, there were still two alert level days in 1979.
Utah County - Provo Areas - One of the main causes of TSP violations in this
area is the U.S. Steel plant west of Orem. Of the three TSP measuring sites
located in Utah County, only two primary daily TSP violations were noted.
However, all three sites showed violations of the primary annual geometric
mean level violations for TSP.
59

-------
The CO site at Provo showed four primary violations in 1979 versus 51, 23
and 7 in 1976, 1977 and 1978 respectively. There has been only one primary
ozone violation day In three years at the Provo site under the revised ozone
standard. The State of Utah will soon be redesignating Utah County to an
unclassified area.
Weber County - Ogden Areas - The station at Ogden is the only station used to
monitor TSP for Weber County. Primary level daily violations have remained
approximately the same for 1977 thru 1979 with three primary and one alert
level violation day being noted in 1979. The annual geometric mean has been
at the primary violation level for the last four years 1976—1979.
There have been no ozone violations noted for Weber County at the Ogden
site for 1977 thru 1979 using the revised ozone standards. The State of Utah
will be redesignating these areas to unclassified. Motor vehicle emissions
still are a major problem in Ogden. Primary daily ozone violations numbered
12 and 14 in 1978 and 1979. This is down from 75 and 36 ozone violation days
in 1976 and 1977.
Cedar City Area - Cedar City in Iron County was designated a nonattainment
area for SO 2 . The cause was a building burning high sulfur oil for
heating. No primary violations occurred in 1979 because of a change to low
sulfur fuel in that building. The state implementation plan for this city was
approved by EPA.
60

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Tooele County Area — The East Tooele monitoring site showed no primary level
TSP violations in 1978 or 1979. The original cause of violations was the
emissions from the copper smelter owned by Kennecott Copper Company. The
design change taken by Kennecott has caused this decrease in primary
violations.
61

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lrrM
MONITORING SITES
U
Stations with 75% or more of
maximum possible data
Stations with less than 75%
of maximum possible data
62
0

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UTAH
STATIONS USED FOR TRENDS AND/OR STATUS
County City or Location Station Number TSP S02 N02 CO Ox LEAD
Davis Bountiful 460060001F01 X X X X X
En’ery Castledale 460280004F02 X X
Green River 460280005F02 X
Huntington Canyon 460280001K03 X
Huntington #2 4602800031(03 X
Garfield Escalante 460300002K03 x
Henri eville 460300003K03 x
Grand Moab 460580002F01
Iron Cedar City 460160002F01 X
Kane Glen Canyon 4604000031(03 X
Salt Lake Airport (SLC) 460920004F02 X
Health Dept (SLC) 460920001F01 X X X X X
Magna 460520001F02 X X
San Juan Navajo Mt 46O96OO0 .KO3 X
Olsato 460960002K03 X
Tooele East Tooele 461160001F01 X X
Uintah East Vernal 461200001F01 X X X
Utah Lindon 461120001F01 X
Pleasant Grove 460760001F01 X
Provo 460800001F01 X X X X
Washington Bloomii gton 461280001K03 X
George 4612800021(03 X
Weber Ogden 460680001F01 X X X X
*Status Only
63

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UTAH
STATIONS NOT USED FOR TRENDS AND/OR STATUS - LESS THAN
75% OF MAXIMUM DAYS
County City or Location Station Number LEAD
San Juan Aneth 460960003K03 X
64

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AIR QUALITY TRENDS
BASED ON STANDARD VIOLATIONS
UTAH
NONATTAINMENT AREAS
Total Suspended Particulates Sulfur Dioxide Ozone
Number Number Number
Days Violation of Days Violation of Days Violation of
Nonattainment Area Year Sampled Days Stations Sampled Days Stations Sampled Days Stations
Davis County 1977 334 P—2 1 364 P-8 1
1978 333 P—O 1 364 A—1/P-8 1
1979 334 P—O 1 358 P-lU 1
Salt Lake County 1977 365 A-3/P-33 8 361 A-4/P-119 1 355 P-O 1
1978 363 A—4/P-9 4 261 A—2/P—151 3 179 P—3 1
1979 364 A-2/P-9 3 263 P-4 2 362 P-4 1
Utah County 1977 365 A—4/P—19 6 365 P—O 2
1978 356 P—O 3 352 P—i 2
1979 356 P—2 2 363 P—O 1
Weber County 1977 350 A—1/P—3 2 203 P—U 1
1978 301 P—i 2 72 P—O 1
1979 350 A—i/P—3 1 341 p—U 1
Cedar City 1977 272 P-li 1
1978 334 P-7 2
1979 334 P—O 1
Tooele County 1977 306 P—7 1
1978 305 p-U 1
1979 231 P—U 1
A - Alert Violation Days
P — Primary Standard Violation Days
U,

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AIR QUALITY TRENDS
BASED ON STANDARD VIOLATIONS
UTAH
NONATTAI NMENT AREAS
Carbon Monoxide
Number
Days Violation of
Nonattainment Atea Year Sampled Days Stations
City of Bountiful 1977 228 P—7 1
1978 334 P-O 1
1979 334 P-4 1
City of Ogden 1977 341 A-3/P-36 1
1978 349 P—12 1
1979 337 P—14 1
City of Provo 1977 365 P-23 1
1978 277 P—7 1
1979 212 P-4 1
Salt Lake City 1977 359 A-3/P-40 1
1978 352 P—18 1
1979 364 A—3/P—18 1
A - Alert Violation Days
P - Primary Standard Violation Days
0•i
o I

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NUMBER OF DAYS THAT PRIMARY STANDARD OR ALERT LEVEL WAS
EXCEEDED IN 1979
Salt Lake (Magna)
UTAH
TOTAL SUSPENDED PARTICULATES
SULFUR DIOXIDE
328
II
CARBON MONOXIDE
Davis (Bountiful)
Salt Lake (Salt Lake Health Department)
Utah (Provo)
Weber (Ogden)
Davis (Bountiful)
Salt Lake (Health Department)
OZONE
342
364
214
337
Primary level exceeded
Alert level exceeded
County (City or Location)
Days
Sampled
Salt Lake Magna)
Airport)
Health Department)
Weber (Ogden)
Utah (Provo)
0
Days/Year
10
20
346
294
249
350
337
D
— I
1
348
362
1
[ I
67

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STATUS AND TRENDS IN AIR QUALITY
UTAH
Counti
ia
Davis
Emery
C>
c
0
c
0
I
Garfield
Grand
Iron
c ’
Salt Lake
jja
1Db
•
San Juan
Tooele
UI ntah
Utah
!
Wastl ngton
Weber
*
No evidence standard exceeded
Exceeds primary standard
Exceeds alert level
Improvement
No apparent trend or insufficient data
to determine trend
Deterioration
0
68

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Wyoming Air Quality
The only air pollution monitoring in Wyoming is for total suspended
particulates. The nonattainment area for TSP in the Trona industrial area
showed no primary level violations. Rock Springs, located 28 miles ENE of
this area, did show 2 primary level violations f or TSP. No other TSP primary
violations were noted in Wyoming since there were only 8 secondary level TSP
violations in all of Wyoming for 1979.
Status of Nonattainment Areas in Wyoming
Trona Industrial Area — A nonattainment area for primary TSP violations was
designated for an area 10 miles by 10 miles square centered approximately 28
miles WSW of Rock Springs. No primary level violations were shown for 1977
thru 1979 at the Granger station. An average of 56 days were sampled during
each of these three years.
69

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Stations with 75% or more of
maximum possible data
70
Stations with less than 75%
of maximum possible data
MONITORING SITES

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WYOMING
STATIONS USED FOR TRENDS AND/OR STATUS
County City or Location Station Number TSP
Big Horn Lovell 520040001F01 X
Campbell Gillette 520280002F01 X
Crook Devils Tower 520200002F03 X
Fremont Riverton 520600001F01 X
Goshen Lingle 520300003F03 X
Johnson Southwest of Buffalo 520360001F03 X
Laramie Cheyenne 520140001F01 X
Platte Wheatland 520830001.FO1 X
Sheridan Sheridan 520660002F03 X
Sublette Boulder 520680001F03 X
Sweetwater Rock Springs 520620001F01 X
Rock Springs 520620003F01 X
Granger 520680001F03 X
Teton Kelly 520720001F03 X
*Status Only
71

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WYOMING
STATIONS NOT USED FOR STATUS AND/OR TRENDS - LESS THAN
75% OF MAXIMUM DAYS
County City or Location Station Number TSP
Albany Laramie 520400005F03 X
Converse Douglas 520220002FO3 X
Fremont Lander 520380001F01 X
Natrona Casper 520120001F01 X
Sweetwater Rock Springs 520620001F01 X
Uinta Evanston 52O240001F01 X
72

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AIR QUALITY TRENDS
BASED ON STANDARD VIOLATIONS
WYOMING
NONATTAINMENT AREAS
Total Suspended Particulates —
Number
Days Violation of
Nonattainment Area Year Sampled Days Stations
Trona Industrial 1977 58 P-O 1
Area 1978 55 P-O 1
1979 55 p-a 1
A - Alert Violation Days
P - Primary Standard Violation Days
73

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NUMBER OF DAYS THAT PRIMARY STANDARD OR ALERT LEVEL WAS
EXCEEDED IN 1979
WYOMING
TOTAL SUSPENDED PARTICULATES
Days/Year
Days
County (City or Location) Sampled 10 20
Sweetwater (Rock Springs) 38
i i Primary, level exceeded
Alert level exceeded
74

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STATUS AND TRENDS IN AIR QUALITY
WYOMING
Counti
Albany
Big Horn
Campbell
Converse
Crook
Fremont
Goshen
Johnson
TSP
TSP
County
Laramle
Natrona
Platte
Sheridan
Sublette
Sweetwater
Teton
Ulnta
No evidence standard exceeded
Exceeds primary standard
Exceeds alert level
Improvement
No apparent trend or insufficient data
to determine trend
Deterioration
75

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APPENDIX A
National Nnbient Air Quality Standards
76

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NATIONAL AMBIENT AIR QUALITY STANDARDS
Maximum
permissible
Pollutant Time period/standard concentration
Suspended particulate matter Annual, secondary 60 .zg/m 3
(Total suspended particulates) Annual, primarya 75 tg/m
(TSP) 24-hour, secondaryb 150 g/m3C
24—hour, primary 260 jg/m3C
Sulfur dioxide Annual, primary 80 .ig/m 3
(SO 2 ) 24—hour, primary 365 iig/m3C
3-hr, secondary 1300 i. g/m3C
Carbon monoxide 1-hr, primary 40 mg/m3C
(CO) 8-hr, primary 10 mg/m3C
Oxidants/ozone 1—hr, primary 235
(O + O or 03)
Nitrogen dioxide Annual, primary 100 j g/m 3
(N02)
Lead Quarterly, primary 1.5 g/m 3
aprimary: ‘toprotect public health.
bSecondary: to protect public welfare.
cThese values are not to be exceeded more than once per year.
77

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APPENDIX B
Breakpoints For Pollutant
Standards Index
(Includes Alert Level For Each Pollutant)
78

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Breakpoints for PSI (4,) in Metric Units
PSI TSP SO 2 CO 03 N02
Value g/m 3 ig/m 3 TSPxSO2 mg/rn 3 1 g/m 3 ig/m 3
Breakpoints (4,) 24-hr. 24-hr. ( ig/m 3 ) 2 8 hours 1-hr. 1-hr.
50% of primary short- 50 75 80a b 5.0 118 b
term NAAQS
Primary short-term NAAQS 100 260 365 b 10.0 235 b
Alert Level 200 375 800 65x10 3 17.0 400 1130
‘° Warning Level 300 625 1600 261x10 3 34.0 800 2260
Emergency Level 400 875 2100 393x10 3 46.0 1000 3000
Significant Harm Level 500 1000 2620 490x10 3 57.5 1200 3750
aAnnual primary NAAQS.
bNo index value reported at concentration levels below those specified by the Alert level
criteria.

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APPENDIX C
Procedures Used To Determine Status
80

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PROCEDURES USED TO DETERMINE STATUS
TOTAL SUSPENDED PARTICULATES
County Status
1. Select worst site In each county based on
o Number of days per year greater than 260 ig/m 3
o Data available in 1979 (must have greater than 75%
of maximum possible data)
o Population exposure of site. Should be representa-
tive of populated area
2. For the selected site the number of days with a value
greater than 260 iig/m 3 for 1979
3. For same site, number of days with at least one value
greater than 375 g/m 3
Nonattainment Area Status
1. Select all the sites in each nonattainment area based on
o Any sites with a daily value of greater than 260 .ig/m 3
in the county
o Any sites with a daily value of greater than 375 .ig/m 3
in the county
o Compare violation days at all sites to total days
sampled at all sites for the year
81

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NITROGEN DIOXIDE
County Status
1. Select worst site In each county based on
o Highest annual average
o Data available in 1979
2. Determine whether annual average is greater than 100 ig/m 3
o Actual data are used
o Years without valid annual average are disregarded
Nonattainment Area Status
1. Select all the sites in each nonattainment area based on
o Any site with an average of greater than 100 ig/m 3
2. Compare the sites with yearly average values of 100 zg/m 3
to the total number of sites sampled for the year.
82

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SULFUR DIOXIDE
County Status
1. Select site in each county based on
o Population exposure. Must be in area where people
are present
o Representativeness within county
o Number of days for 1979 greater than 24-hour
average of 365 g/m 3
o Data available in 1979
2. For the selected site, number of days in 1979 greater than
primary 24-hour standard for the year
o Actual data used
o Continuous data preferred over noncontinuous
3. For same site count number of days per year with at least
one value greater than 730 3.Lg/m 3
o Actual data used
Nonattainment Area Status
1. Select all the sites in each nonattainment area based on
o Any sites with a 24—hour concentration of greater than
365 ig/m 3 in the county
o Any sites with a 24-hour concentration of greater than
730 . g/m 3 in the county
2. Compare violation days at all sites to the total days sampled
at all sites for the year
83

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OZONE
County Status
1. Select worst site in county based on
o Number of days greater than 235 pg/rn 3
o Data available for at least one year (1977—1979)
during the months April through September
2. For selected site, count the number of days per year
1977-1979, with at least one hourly value greater than
235 pg/rn 3
o For periods with no data, estimate by examining data
from nearby sites and for the same site during same
period of other years
o Data are insufficient if unavailable during the peak
ozone season (April-September)
3. For same site, count number of days with at least one value
greater than 400 pg/rn 3
o Actual number is always used
Nonattainment Area Status
1. Select all the sites in each nonattainment area based on
o Any sites with a day having a 1-hour concentration
of greater than 235 pg/rn 3
o Any sites with a day having 1—hour concentration of
greater than 400 pg/rn 3
2. Compare violation days at all sites to total days sampled
at all sites for the year
84

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CARBON MONOXIDE
County Status
1. Select worst site in each county based on
o Number of days greater than 10 mg/rn 3 8-hour average
o Data available for 1979
2. For selected site, count the number of days In 1979 wIth
at least one 8-hour average greater than 10 mg/rn 3
o For periods with no data estimate by examining data
for same site for same period of other years and by
looking at data for other nearby sites.
3. For same site count number of days with at least one value
greater than 17 mg/rn 3
o Actual number always used
Nonattainment Area Status
1. Select all the sites in each nonattainment area based on
o Any sites with a day having an 8-hour concentration
of greater than 10 mg/rn 3
o Any sites with a day having an 8-hour concentration
of greater than 17 mg/rn 3
2. Compare violation days at all sites to total days sampled
at all sites for the year
85

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LEAD
County Status
1. Select the worst site in each county based on
o Quarterly average periods greater than 1.5 iig/m 3
o Data available in 1979
2. For selected site, count number of quarters in 1973
with quarterly value of greater than 1.5 g/m
Nonattainment Area Status
1. Select all the sites in each nonattainment area based on
o Any sites with a quarterly average greater than
1.5 ig/m 3
2. Compare violation quarters at all sites to total quarters
sampled at all sites for the year
86

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APPENDIX D
Nonattainment Area Maps
87

-------
TOrr L... sT1 pENDED PARTICULATES
AND CARBON MONOXIDE
non—attainment area

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THREE C. YEAR 2000. PLANN G AREA MAP
89
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DENVER
DENVER! BOULDER! LONGMONT (DBL) AREA

-------
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•1 . Pueblo Nonattainment Area
- . URBAN NSPOI’ATI(
V. - __ __ - - - • r PLANNING BOUNDARY

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LAR IMER/ WELD
OF COLORADO :‘T Z T or: PUBLiC HEALTH
4210 EAST 11TH AVENUE. DENVER, COLORADO 80220 . PHONE 388-6111
R. L. CLEERE, M.O.. M.P.M..-OIRICTOR
NOTICE
In compliance zith the provisions of the “Air Pollution Control Act”,
Section S (1) (C), Session La rs of Colorado, Second Regular Session 1966,
NOTICE is hereby given epartnent of Public Health has desi ted the
follo ;in le a1ly described area inJ a and W 1 Cou i , State of
Colorado, in :hich the a:tbient air standards set forth in Section 4.of the
above cited Act are not being met, and in thich the enission stan s sat
forth in Section 5 and the penalties prescribed in SectIon 15 of said Act,
as amended by Sonate Bill. No. 380, 46th General Asscmbly (1967), shall be
in effect as provided therein, to wIt:
Coencing at the Northuest corner of SectIon 6, Township 9
North, Range 70 t!est; thence East a1on the section lines
approxthately 18 niles to the Northeast corner of Section 1,
Township 9 orth, Range 68 !est; thence South along the sattion
lines appro:d..’ately 6 niles to the Southeast corner of Section
36, Township 9 North, Range 65 West; thence East along the section
lines appro i ataly 24 miles to the Northeast corner of Section 1,
Township S North, Range 64 West; thence South along the section
lines apprcxi. ate1y 48 nilas to the Southeast corner of Section 36,
Township 1 orth, Range 64 West; thence West along the section
lines approximately 30 miles to the South :est corner of Secticn 31,
Township 1 north, Range 68 West; thence North along the section
lines approximately 13 miles to the Norchuest corner of Se :ion 6,
Township 3 orch, Range 63 West; thence West along the section
lines approximately 12 miles to the Southwest corner of Section 31,
Township 4 North, Range 70 West; thence North a ong the section
lines approximately 36 miles to the point of beginning;

Roy, Lη,Cl crc, L.D., M.P.a. Gcor c J,jD :,ir 5 1 , D.D.S.
Dircηtor Chairu otV /
Colorad3 S atc D. p.:irtmcnt of Air PollucLon Variance
Public Uc lr.i Board
91
Datcd 1 ttC(Zt 4, 19G7

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MESA
I/sea C’ COLO A O : ::t ;; - 0:: PU L!C (-!rZALT;1
4210 EAST 11TH AVEA’UE . DENVE!?, COLOPADO O22O . P/lONE 38e.s6or
R. L CL . Cnc M.d).. Af .P /f.. Dl ECTOi7
NOTICE
In compliance with thc provisions of Scction 8 (1) (c) of tho
“Air Pollution Control Act” (Ch. 45, Pg. 210, Colorado Session La :s
1966) NOTICE is hereby given that the Division of Ad iinistratjon of
the Colorado State D2partmenc of Public Health has enlarged the area
comprising the air pollution basin in Nesa County to incltde additional
territory an has c1esi natecj the following Legally described area of
}!csa County, Colorado in which the ambient air standards set forth in
Section 4 of the above cited Act are not being ract, and in wtich the
emission standards sct forth in Section 5 of said Act, shall be in
effect as provided therein, to wit:
Cor uencin at the Northeast Corner of Section 34.Towr ship
10 South, Range 98 west; thence South along the section
line approximately I mile to the Southeast Corner of Section
34, Township 1.0 South, Range 98 West; thence East alon; the
section line approximately 400 feat to the Northeast Co cr
of Section 2, Township 11 South, Range 98 West; thence
South along the section lines approximately 2.4 miles to
the Southeast Corna: of Section 11, Township 11 South,
Range 98 1cst; thence West along the section line a pro.:i-
mately 2000 feet to a point where such line intersects the
Eastern boun’Iary of Section 1, Township I South, Range 2
East; thence South along the section lines approxi at ly 6
miles and 3800 fcct to th uθhcast Corner of Sc ctjon I,
Township 2 South, Rar;c 2 East; thence !cst along the
Scction linc approxirilately 11 miles to the Southwest
Corner f Section 5, To znshLp 2 South, Range 1 East;
thence North along the sCction line appro:imaccly 1 mile
to the North cct Corncr of Scccion 5, Township 2 South,
R&nge 1. East; rhcnc Wesr. along the section lines approxi-
mately 5 and /4 mi1c to thc. point where said line
intcrsccts thc rast boundary of the Coloralo National
Honumc’nt Park; thence fl a ‘orth ’csterly direction along
the boundary line of sai’J I’ark to the Northt: st Corner of
SectIon 31, Tot:n:hip I North, 1 an e 2 lest; thence North
-92

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along thc section line approxim.2tely 1 milc to the Southwest
Corner of Scction 19) Tocmship 1 ? orth, R tnge 2 Jest; thcnce
West along the section linc approximately 1 mile to the
Southucst Coincr of Section 24, .To n hip 1 North, Range 3
Vest; thence North along the section line approx atcly 1
mile to the Sotithtzest Corner of Section 13, Township 1
North, Range 3 1cst; thence Uest along the section lines
approxit ate 1y 2 miles to the Southwest Corner of Section 15,
Tounship 1 North, RanCC 3 Ucsc; thence North along thc
section lines approximately 3 miles to the Nortlit;cst Cor cr
of Section 3, To znship I north, Range 3 West; thence East
along the section lines approx mate1y 11 n.iles to the
Northeast Corner of Section 5, To .-nship 1 North, Range 1
West; thence South along the section lines approximately
2 miles to the Northeast Corner of Section 17, Township
1 North, Range 1 West; thence East along the section
line appro :imataIy 1 mile to the Northeast Corner of Section
16, Township 1 North, Range 1. Was ; thence South along
the section line approximately I mile to the Southeast
Corner of Section 16, To nship I. North, Range 1 West;
thence East along the Section lines appro,:imatci.y 15
miles to the point of beginning, all in Mesa County,
Colorado.
_ / __ __
Roy L.(/learc, Z1.D., U.P.H. George D 1 c, D.D.S.
Director Chairman
Colorado State Deparcmcnt of Air Pollution Vaciancc
Public health Board
Dated 3une 9, 1966
93

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MISSOULA PRIMARY TSP
NON—ATTAINMENT AREA
Missoula City Limits
‘‘PAQCR 144
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Sections
- Sections
35, 36
1, 2, 12,
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lJe.
MISSOULA Co NON-ATTAINMENT ATREA
a City Limits
AQCR 144
96

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FLATHEAD COUNTY
MONTANA
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COLUMBIA FALLS
TSP NON-ATTAINMENT AREA
CITY LIMITS OF COLUMBIA FALLS
AQCR 144
lΰ I
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to
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51*15 .5 VUT
500 • 1 (5
lP00

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COLSTRIP
TSP NON-ATTAINMENT AREA
AQCR 143
A
N
Boundaries - VTM coordinates as indicated.
98

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North Boundary
East Boundary
South Boundary
West Boundary
99
2nd Ave. N.
10th Street
2nd Ave. S.
Missouri River
AQCR 141

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F
I 1 *ILNU*U MA1
POST OF?ICE
COURT HOUSE
ELEMENTARY
HIGH SCHOOL
HOSPITAL
ELEVATION
a
+
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BILLINGS Co NON-ATTAINMENT AREP
North Boundary 6th Aye, N.
East Boundary US 87/312
South Boundary SN Tracks
West Boundary Division SI
AQCR 140
CITY PLAT
BILLIN(
100 YELLOW TONE CO
MONTAN?
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2nd Ave. So.
33rd .$treet/Di vision
AQCR 140
CITY PLAT
BILLIN(
YELLOWSTONE CC
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;
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SO 2 NON-ATTAINMENT AREA
2.0 km Radium Around
Cenex Refinery (Point A)
102 AQCR 140

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4. N N N N C ‘L N N1!
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ANACONDA SMELTER - POINT A
AQCR 142
104
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EAST HELENA
S02 NON-ATTAINMENT AREA
0.67 Km Radius.Around Smelter
AQCR 142
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AQCR 142
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Approximate Over fl
Boundary of Non—
attainment Areas
Trona Industrial
Nonattainment Area
SWEETWATER COUNTY

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TECHNICAL REPORT DATA
(Please read Instructions on the reverse before completing)
2

3 RECIPIENT’S ACCESSION NO
REGION VIII (1979 Data)
Protection Agency
5 REPORT DATE
September 1980
6. PERFORMING ORGANIZATION CODE
A. Entzminger, Stephen C. Bell
8 PERFORMING ORGANIZATION REPORT NO
NAME AND ADDRESS
Protection Agency
Analysis Division
10 PROGRAM ELEMENT NO
11 CONTRACT/GRANTNO
AND ADDRESS
13 TYPE OF REPORT AND PERIOD COVERED
Final
14 SPONSORING AGENCY CODE
and status for the calendar year 1979 were determined
Region VIII. These states include Colorado, Montana,
Dakota, Utah and Wyoming. Data resident in the SAROAD
analyzed.
which detect significant differences between two
utilized to identify trends. The status and severity of air
as a direct measure of air quality standard and alert
The report includes a summary of air quality in each
KEY WORDS AND DOCUMENT ANALYSIS
b IDENTIFIERS/OPEN ENDED TERMS
C. COSATI E ’IeId/GrOUp
Colorado SAROAD
Montana
North Dakota
South Dakota
Utah
Wyoming —
19 SECURITY CLASS (This Report)
Unclassified
21 NO OF PAGES
109
20 SECURITY CLASS (This page)
Unclassified
22 PRICE
EPA Form 2220—1 (Rev. 4—77)
PREVIOUS EDITION IS OBSOLETE
109

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